JP2014156821A - Exhaust emission control system - Google Patents

Exhaust emission control system Download PDF

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JP2014156821A
JP2014156821A JP2013028082A JP2013028082A JP2014156821A JP 2014156821 A JP2014156821 A JP 2014156821A JP 2013028082 A JP2013028082 A JP 2013028082A JP 2013028082 A JP2013028082 A JP 2013028082A JP 2014156821 A JP2014156821 A JP 2014156821A
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reducing agent
exhaust gas
storage tank
liquid
catalyst layer
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JP2014156821A5 (en
JP6140470B2 (en
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Susumu Hizuya
進 日数谷
Naoe Hino
なおえ 日野
Seigo Yamamoto
誠吾 山本
Ami Nishi
亜美 西
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Hitachi Zosen Corp
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Hitachi Zosen Corp
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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 ; Methods of operation or control of catalytic converters
    • F01N3/2066—Selective catalytic reduction [SCR]
    • 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
    • F01N2240/00—Combination 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
    • F01N2240/02—Combination 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
    • 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
    • F01N2610/00—Adding substances to exhaust gases
    • F01N2610/02—Adding substances to exhaust gases the substance being ammonia or urea
    • 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
    • F01N2610/00—Adding substances to exhaust gases
    • F01N2610/10—Adding substances to exhaust gases the substance being heated, e.g. by heating tank or supply line of the added substance
    • 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
    • F01N2610/00—Adding substances to exhaust gases
    • F01N2610/14—Arrangements for the supply of substances, e.g. conduits
    • F01N2610/1406—Storage means for substances, e.g. tanks or reservoirs
    • 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
    • F01N2900/00—Details of electrical control or of the monitoring of the exhaust gas treating apparatus
    • F01N2900/06—Parameters used for exhaust control or diagnosing
    • F01N2900/18—Parameters used for exhaust control or diagnosing said parameters being related to the system for adding a substance into the exhaust
    • F01N2900/1806—Properties of reducing agent or dosing system
    • F01N2900/1808—Pressure
    • 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
    • F01N2900/00—Details of electrical control or of the monitoring of the exhaust gas treating apparatus
    • F01N2900/06—Parameters used for exhaust control or diagnosing
    • F01N2900/18—Parameters used for exhaust control or diagnosing said parameters being related to the system for adding a substance into the exhaust
    • F01N2900/1806—Properties of reducing agent or dosing system
    • F01N2900/1811—Temperature
    • Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02T—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO TRANSPORTATION
    • Y02T10/00—Road transport of goods or passengers
    • Y02T10/10—Internal combustion engine [ICE] based vehicles
    • Y02T10/12—Improving ICE efficiencies

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Health & Medical Sciences (AREA)
  • Toxicology (AREA)
  • Combustion & Propulsion (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Exhaust Gas After Treatment (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide an exhaust emission control system that can remove nitrogen oxide (NOx) in exhaust gas by adding a liquid reducer such as alcohol and hydrocarbon even when the exhaust gas has a temperature in a relatively low temperature region of around 200-400°C like exhaust gas of an internal combustion engine such as a marine diesel engine and that can prevent decline in the exhaust gas temperature.SOLUTION: In an exhaust emission control system, reducer supply means 3 and a NOx removal catalyst layer 4 are disposed in this order from the upstream side in an exhaust passage 2 of an internal combustion engine. A reducer is added to exhaust gas on the catalyst layer upstream side by the reducer supply means to reduce nitrogen oxide in the exhaust gas, so as to purify the exhaust gas. The exhaust emission control system comprises a liquid reducer storage tank 5 and compressed air supply means 6. Compressed air is supplied from the compressed air supply means to the reducer vaporized within the liquid reducer storage tank 5, so as to form vaporized reducer entrained air. The vaporized reducer entrained air is supplied to the reducer supply means.

Description

本発明は、例えば船舶用ディーゼルエンジン等の内燃機関などの排ガスの浄化システム、さらに詳しくは、内燃機関などの排ガスに、アルコール、炭化水素などの液体還元剤を添加して、排ガス中の窒素酸化物（ＮＯｘ）を除去する排ガス浄化システムに関するものである。   The present invention relates to a system for purifying exhaust gas such as an internal combustion engine such as a marine diesel engine. More specifically, a liquid reducing agent such as alcohol or hydrocarbon is added to exhaust gas such as an internal combustion engine to oxidize nitrogen in the exhaust gas. The present invention relates to an exhaust gas purification system for removing substances (NOx).

一般に、船舶用ディーゼルエンジン等の内燃機関などの排ガス中の窒素酸化物の除去方法としては、例えば下記の特許文献１に記載のように、排ガスにアンモニア系還元剤を添加し、脱硝触媒に接触させる方法が知られており、そしてこの場合、アンモニア系還元剤の添加方法は、脱硝触媒層の上流側の排気通路に、アンモニア系還元剤を液体の状態でスプレー等により噴霧し、脱硝触媒層に到達する前にアンモニア系還元剤を気化させる方法が採用されている。   In general, as a method for removing nitrogen oxides in exhaust gas from an internal combustion engine such as a marine diesel engine, an ammonia reducing agent is added to the exhaust gas and contacted with a denitration catalyst as described in Patent Document 1 below, for example. In this case, the ammonia reducing agent is added to the exhaust passage upstream of the denitration catalyst layer by spraying the ammonia reducing agent in a liquid state by spraying or the like. A method of vaporizing the ammonia-based reducing agent before reaching the point is adopted.

一方、例えば下記の特許文献２に記載のように、船舶用ディーゼルエンジン等の内燃機関などの排ガス温度が３００〜４００℃程度の比較的低温域での排ガスの浄化方法として、排ガス中に、アンモニア系還元剤以外のアルコール、炭化水素などの還元剤を添加して、排ガス中の窒素酸化物を除去する方法についても、検討が進められている。   On the other hand, as described in, for example, Patent Document 2 below, as a method of purifying exhaust gas in a relatively low temperature range where the exhaust gas temperature of an internal combustion engine such as a marine diesel engine is about 300 to 400 ° C., ammonia is contained in the exhaust gas. Studies are also underway on methods of removing nitrogen oxides in exhaust gas by adding reducing agents such as alcohols and hydrocarbons other than system reducing agents.

特開２００１−１７３４３１号公報JP 2001-173431 A 特開２００４-２６１７５４号公報JP 2004-261754 A

しかしながら、上記特許文献２に記載の従来の排ガス浄化システムでは、脱硝触媒層の上流側の排気通路に、アルコール系還元剤を液体の状態でスプレー等により噴霧し、脱硝触媒層に到達する前にアルコール系還元剤を気化させているため、還元剤の気化熱により排ガス温度が低下し、触媒層における触媒の脱硝性能が低下するという問題があった。そして、これに対処するためには、例えば脱硝触媒の使用量を増加するなどの対策が必要であるという問題があった。特に、船舶用ディーゼルエンジン等の内燃機関などでは、排ガス温度が２００〜４００℃程度とさらに低温域であるため、還元剤の気化熱により排ガス温度がさらに低くなると、十分な脱硝性能が得られず、実用化が難しいというのが現状であった。   However, in the conventional exhaust gas purification system described in Patent Document 2, an alcohol-based reducing agent is sprayed in a liquid state to the exhaust passage on the upstream side of the denitration catalyst layer in a liquid state before reaching the denitration catalyst layer. Since the alcohol-based reducing agent is vaporized, there has been a problem that the exhaust gas temperature is lowered by the heat of vaporization of the reducing agent, and the denitration performance of the catalyst in the catalyst layer is lowered. And in order to cope with this, there existed a problem that measures, such as increasing the usage-amount of a denitration catalyst, were required, for example. In particular, in an internal combustion engine such as a marine diesel engine, the exhaust gas temperature is about 200 to 400 ° C., which is a lower temperature range. The current situation is that it is difficult to put into practical use.

本発明の目的は、上記の従来技術の問題を解決し、例えば船舶用ディーゼルエンジン等の内燃機関の排ガスのように、排ガス温度が２００〜４００℃程度の比較的低温域の排ガスであっても、アルコール、炭化水素などの液体還元剤を用いて、しかも排ガス温度を低下させることなく、高い脱硝性能を維持することができて、実用性に優れている、排ガス浄化システムを提供することにある。   The object of the present invention is to solve the above-mentioned problems of the prior art, for example, even in a relatively low temperature exhaust gas having an exhaust gas temperature of about 200 to 400 ° C., such as an exhaust gas of an internal combustion engine such as a marine diesel engine. An object of the present invention is to provide an exhaust gas purification system that can maintain high denitration performance using a liquid reducing agent such as alcohol and hydrocarbon, without lowering the exhaust gas temperature, and is excellent in practicality. .

本発明者らは、上記の点に鑑み鋭意研究を重ねた結果、液体還元剤貯留槽内で気化した還元剤に対して圧縮空気を供給し、これにより形成された気化還元剤同伴空気を内燃機関の脱硝触媒層上流側の排気通路に供給することにより、排ガスに添加する際に、事前に気化した還元剤を供給することができて、従来の液体還元剤の気化熱による排ガス温度の低下を抑制し、高い脱硝性能を維持することができて、実用性に優れた排ガス浄化システムを構築できることを見出し、本発明を完成するに至ったものである。   As a result of intensive studies in view of the above points, the present inventors have supplied compressed air to the reducing agent vaporized in the liquid reducing agent storage tank, and the vaporized reducing agent-entrained air formed thereby is internal combustion. By supplying it to the exhaust passage upstream of the denitration catalyst layer of the engine, it is possible to supply a pre-vaporized reducing agent when adding to the exhaust gas, and the exhaust gas temperature is reduced by the heat of vaporization of the conventional liquid reducing agent. It has been found that an exhaust gas purification system that can suppress the above and maintain high denitration performance and is excellent in practicality can be constructed, and the present invention has been completed.

また、本発明者らは、液体還元剤貯留槽からの還元剤を熱交換器において加熱して気化させ、この気化還元剤を内燃機関の脱硝触媒層上流側の排気通路に供給することにより、排ガスに添加する際に、事前に気化した還元剤を供給することができて、従来の液体還元剤の気化熱による排ガス温度の低下を抑制し、高い脱硝性能を維持することができて、実用性に優れた排ガス浄化システムを構築できることを見出し、本発明を完成するに至ったものである。   Further, the present inventors heated the reductant from the liquid reductant storage tank in a heat exchanger to vaporize it, and by supplying this vaporized reductant to the exhaust passage upstream of the denitration catalyst layer of the internal combustion engine, When added to exhaust gas, it is possible to supply a pre-vaporized reducing agent, suppress the decrease in exhaust gas temperature due to the heat of vaporization of conventional liquid reducing agents, maintain high denitration performance, and practical The present inventors have found that an exhaust gas purification system excellent in performance can be constructed, and have completed the present invention.

上記の目的を達成するために、請求項１の発明は、内燃機関の排気通路に、上流側から順に還元剤供給手段と脱硝触媒層が配置され、前記還元剤供給手段より還元剤が前記触媒層上流側の排ガスに添加され、排ガス中の窒素酸化物が還元されて、排ガスが浄化される排ガス浄化システムにおいて、
液体還元剤貯留槽と、圧縮空気供給手段とを備えており、前記液体還元剤貯留槽内で気化した還元剤に対して前記圧縮空気供給手段から圧縮空気が供給されて、気化還元剤同伴空気が形成され、この気化還元剤同伴空気が前記還元剤供給手段に供給されることを特徴としている。 In order to achieve the above object, according to the first aspect of the present invention, a reducing agent supply means and a denitration catalyst layer are arranged in order from the upstream side in an exhaust passage of an internal combustion engine, and the reducing agent is supplied from the reducing agent supply means to the catalyst. In the exhaust gas purification system that is added to the exhaust gas upstream of the bed and the nitrogen oxides in the exhaust gas are reduced to purify the exhaust gas,
A liquid reducing agent storage tank and compressed air supply means are provided, and compressed air is supplied from the compressed air supply means to the reducing agent vaporized in the liquid reducing agent storage tank, and vaporized reducing agent-entrained air The vaporized reducing agent entrained air is supplied to the reducing agent supply means.

請求項２の発明は、請求項１に記載の排ガス浄化システムであって、前記圧縮空気供給手段から液体還元剤貯留槽内に供給する圧縮空気の流量および貯留槽内液体還元剤温度を制御することにより、排ガスに添加する気化還元剤量を制御することを特徴としている。   The invention according to claim 2 is the exhaust gas purification system according to claim 1, wherein the flow rate of compressed air supplied from the compressed air supply means into the liquid reducing agent storage tank and the liquid reducing agent temperature in the storage tank are controlled. Thus, the amount of the vaporization reducing agent added to the exhaust gas is controlled.

請求項３の発明は、請求項１または２に記載の排ガス浄化システムであって、さらに液体還元剤保管槽を備えており、前記液体還元剤貯留槽には液面計が設置され、この液面計からの貯留槽内還元剤液上面のレベル検知信号に基づいて、前記液体還元剤保管槽から液体還元剤貯留槽に供給される還元剤の供給量が制御されることを特徴としている。   The invention of claim 3 is the exhaust gas purification system according to claim 1 or 2, further comprising a liquid reducing agent storage tank, and a liquid level gauge is installed in the liquid reducing agent storage tank. The supply amount of the reducing agent supplied from the liquid reducing agent storage tank to the liquid reducing agent storage tank is controlled based on the level detection signal on the upper surface of the reducing agent liquid in the storage tank from the surface meter.

請求項４の発明は、請求項１〜３のうちのいずれか一項に記載の排ガス浄化システムであって、前記液体還元剤貯留槽に加熱手段が備えられ、この加熱手段によって貯留槽内の液体還元剤の温度が調整されることを特徴としている。   Invention of Claim 4 is an exhaust gas purification system as described in any one of Claims 1-3, Comprising: A heating means is provided in the said liquid reducing agent storage tank, By this heating means, in a storage tank It is characterized in that the temperature of the liquid reducing agent is adjusted.

請求項５の発明は、請求項４に記載の排ガス浄化システムであって、脱硝触媒層の下流側の排気通路に循環熱媒体加熱用熱交換器が設置され、該熱交換器と前記加熱手段とは熱媒体循環管によって接続されており、該熱交換器において触媒層から排出された浄化排ガスの排熱で、液体還元剤貯留槽の加熱手段からの循環熱媒体が加温されることを特徴としている。   A fifth aspect of the present invention is the exhaust gas purification system according to the fourth aspect, wherein a heat exchanger for circulating heat medium heating is installed in the exhaust passage downstream of the denitration catalyst layer, and the heat exchanger and the heating means Is connected by a heat medium circulation pipe, and the circulating heat medium from the heating means of the liquid reducing agent storage tank is heated by the exhaust heat of the purified exhaust gas discharged from the catalyst layer in the heat exchanger. It is a feature.

請求項６の発明は、内燃機関の排気通路に、上流側から順に還元剤供給手段と脱硝触媒層が配置され、前記還元剤供給手段より還元剤が前記触媒層上流側の排ガスに添加され、排ガス中の窒素酸化物が還元されて、排ガスが浄化される排ガス浄化システムにおいて、
液体還元剤貯留槽と、還元剤気化用熱交換器とを備えており、液体還元剤貯留槽から導出された還元剤が熱交換器において加熱されて気化せしめられ、この気化還元剤が、前記還元剤供給手段に供給されることを特徴としている。 In the invention of claim 6, the reducing agent supply means and the denitration catalyst layer are arranged in order from the upstream side in the exhaust passage of the internal combustion engine, and the reducing agent is added to the exhaust gas upstream of the catalyst layer from the reducing agent supply means, In the exhaust gas purification system in which the nitrogen oxides in the exhaust gas are reduced and the exhaust gas is purified,
The reductant storage tank and a heat exchanger for vaporizing the reducing agent are provided, and the reductant derived from the liquid reductant storage tank is heated and vaporized in the heat exchanger. It is characterized by being supplied to a reducing agent supply means.

請求項７の発明は、請求項６に記載の排ガス浄化システムであって、還元剤気化用熱交換器が、脱硝触媒層の下流側の排気通路に設置され、該熱交換器において触媒層から排出された浄化排ガスの排熱で液体還元剤が加熱されて気化せしめられることを特徴としている。   The invention according to claim 7 is the exhaust gas purification system according to claim 6, wherein the heat exchanger for vaporizing the reducing agent is installed in an exhaust passage downstream of the denitration catalyst layer, and the heat exchanger uses the catalyst layer from the catalyst layer. The liquid reducing agent is heated and vaporized by the exhaust heat of the exhausted purified exhaust gas.

請求項８の発明は、請求項１〜７のうちのいずれか一項に記載の排ガス浄化システムであって、液体還元剤が、アルコール、エーテル、ケトン類、および炭化水素よりなる群の中から選ばれた少なくとも１つの有機化合物であることを特徴としている。   The invention of claim 8 is the exhaust gas purification system according to any one of claims 1 to 7, wherein the liquid reducing agent is selected from the group consisting of alcohols, ethers, ketones, and hydrocarbons. It is characterized by being at least one selected organic compound.

本発明によれば、例えば船舶用ディーゼルエンジン等の内燃機関の排ガスのように、排ガス温度が２００〜４００℃程度の比較的低温域の排ガスであっても、アルコール、炭化水素などの液体還元剤を用いて、しかも排ガスに添加する際に、事前に気化した還元剤を供給することができて、従来の液体還元剤の気化熱による排ガス温度の低下を抑制し、高い脱硝性能を維持することができるうえに、気化還元剤の添加量の制御が容易であり、実用性に優れているという効果を奏する。   According to the present invention, liquid reducing agents such as alcohols and hydrocarbons can be used even in a relatively low temperature exhaust gas having an exhaust gas temperature of about 200 to 400 ° C., such as an exhaust gas from an internal combustion engine such as a marine diesel engine. In addition, when added to the exhaust gas, it is possible to supply a pre-vaporized reducing agent, suppress the decrease in exhaust gas temperature due to the heat of vaporization of the conventional liquid reducing agent, and maintain high denitration performance In addition, the addition amount of the vaporization reducing agent can be easily controlled, and the practicality is excellent.

本発明の第１発明による排ガス浄化システムの第１実施形態を示すフローシートである。It is a flow sheet which shows 1st Embodiment of the exhaust gas purification system by 1st invention of this invention. 本発明の第１発明による排ガス浄化システムの第２実施形態を示すフローシートである。It is a flow sheet which shows 2nd Embodiment of the exhaust gas purification system by 1st invention of this invention. 本発明の第２発明による排ガス浄化システムの第１実施形態を示すフローシートである。It is a flow sheet which shows 1st Embodiment of the exhaust gas purification system by 2nd invention of this invention. 従来の排ガス浄化システムを示すフローシートである。It is a flow sheet which shows the conventional exhaust gas purification system.

つぎに、本発明の実施の形態を、図面を参照して説明するが、本発明はこれらに限定されるものではない。   Next, embodiments of the present invention will be described with reference to the drawings, but the present invention is not limited thereto.

図１は、本発明の第１発明による排ガス浄化システムの第１実施形態を示すフローシートである。   FIG. 1 is a flow sheet showing a first embodiment of an exhaust gas purification system according to the first invention of the present invention.

同図を参照すると、本発明の第１発明は、例えば船舶用ディーゼルエンジン等の内燃機関などの排ガス源１からの排気通路２に、上流側から順に還元剤供給用管（還元剤供給手段）３と脱硝触媒層４が配置され、前記還元剤供給用管３より還元剤が前記触媒層４に添加され、排ガス中の窒素酸化物が還元されて、排ガスが浄化される排ガス浄化システムであって、液体還元剤を貯留させるための液体還元剤貯留槽５と、コンプレッサー（圧縮空気供給手段）６とを備えており、前記液体還元剤貯留槽５内で気化した還元剤に対して前記コンプレッサー６から圧縮空気が供給（パージ）されて、気化還元剤同伴空気が形成され、この気化還元剤同伴空気が前記還元剤供給管３に供給されることを特徴としている。   Referring to FIG. 1, a first invention of the present invention is a reducing agent supply pipe (reducing agent supply means) in order from an upstream side to an exhaust passage 2 from an exhaust gas source 1 such as an internal combustion engine such as a marine diesel engine. 3 and a denitration catalyst layer 4 are disposed, a reducing agent is added to the catalyst layer 4 from the reducing agent supply pipe 3, and nitrogen oxides in the exhaust gas are reduced, whereby the exhaust gas is purified. The liquid reducing agent storage tank 5 for storing the liquid reducing agent and a compressor (compressed air supply means) 6 are provided, and the compressor is used for the reducing agent vaporized in the liquid reducing agent storage tank 5. Compressed air is supplied (purged) from 6 to form vaporized reducing agent-entrained air, and this vaporized reducing agent-entrained air is supplied to the reducing agent supply pipe 3.

この実施形態においては、液体還元剤貯留槽５上部の空間内に、コンプレッサー６から導管７を経て圧縮空気を供給（パージ）することで、気化還元剤同伴空気を形成し、この気化還元剤同伴空気を前記還元剤供給管３より排気通路２内に供給する。   In this embodiment, by supplying (purging) compressed air from the compressor 6 through the conduit 7 into the space above the liquid reducing agent storage tank 5, vaporized reducing agent accompanying air is formed, and this vaporized reducing agent accompanying air is formed. Air is supplied into the exhaust passage 2 from the reducing agent supply pipe 3.

ここで、液体還元剤として用いることができる化合物としては、メタノール、エタノール、プロパノール等のアルコール類、ジエチルエーテル等のエーテル類、メチルエチルケトン等のケトン類、および軽油、灯油、ガソリン等の炭化水素よりなる群の中から選ばれた少なくとも１つの低分子量の有機化合物であることが好ましい。   Here, the compounds that can be used as the liquid reducing agent include alcohols such as methanol, ethanol, and propanol, ethers such as diethyl ether, ketones such as methyl ethyl ketone, and hydrocarbons such as light oil, kerosene, and gasoline. It is preferably at least one low molecular weight organic compound selected from the group.

また、例えば船舶用ディーゼルエンジン等の内燃機関の排ガスなどの浄化処理にあたり、上記液体還元剤を用いた脱硝触媒システムにおける脱硝触媒としては、有効成分がゼオライトである脱硝触媒を使用するのが好ましい。   Further, for example, in the purification treatment of exhaust gas from an internal combustion engine such as a marine diesel engine, it is preferable to use a denitration catalyst whose active ingredient is zeolite as the denitration catalyst in the denitration catalyst system using the liquid reducing agent.

そして、本発明の第１発明において、気化還元剤同伴空気中の気化還元剤濃度を一定にするために、液体還元剤貯留槽５の温度を一定に保つことが好ましい。   In the first invention of the present invention, it is preferable to keep the temperature of the liquid reducing agent storage tank 5 constant in order to make the concentration of the vaporizing and reducing agent in the air accompanying the vaporizing and reducing agent constant.

この実施形態においては、液体還元剤貯留槽５の周壁にジャケット式加熱器（加熱手段）８が設けられ、この加熱器８によって貯留槽５内の液体還元剤の温度が調整される。そしてこの場合、脱硝触媒層４の下流側の排気通路２に循環熱媒体加熱用熱交換器９が設置され、該熱交換器９と上記加熱器８とは熱媒体循環管１０によって接続されており、熱媒体循環管１０の途上に介在させられたポンプ１１の作動によって、貯留槽５のジャケット式加熱器８から加熱用循環熱媒体が熱交換器９に送り込まれ、この熱交換器９おいて循環熱媒体が、触媒層４から排出された浄化排ガスの排熱で加温された後、液体還元剤貯留槽５のジャケット式加熱器８に返送されて、貯留槽５の温度が一定に保持されることが好ましい。   In this embodiment, a jacket type heater (heating means) 8 is provided on the peripheral wall of the liquid reducing agent storage tank 5, and the temperature of the liquid reducing agent in the storage tank 5 is adjusted by the heater 8. In this case, a circulating heat medium heating heat exchanger 9 is installed in the exhaust passage 2 downstream of the denitration catalyst layer 4, and the heat exchanger 9 and the heater 8 are connected by a heat medium circulation pipe 10. By the operation of the pump 11 interposed in the middle of the heat medium circulation pipe 10, the circulating heat medium for heating is sent from the jacket type heater 8 of the storage tank 5 to the heat exchanger 9, and this heat exchanger 9 The circulating heat medium is heated by the exhaust heat of the purified exhaust gas discharged from the catalyst layer 4 and then returned to the jacket heater 8 of the liquid reducing agent storage tank 5 so that the temperature of the storage tank 5 is constant. It is preferred that it be retained.

ここで、液体還元剤として、例えばエタノール（沸点７８．３７℃）を使用した場合、液体還元剤貯留槽５の液体還元剤の温度を、４０℃以上、６０℃以下に保持することが好ましい。このとき、例えば脱硝触媒層４の下流側の排気通路２に設置された熱交換器９において、触媒層４から排出された浄化排ガスの排熱で循環熱媒体を、例えば５０℃に加温した後、熱媒体循環管１０によって貯留槽５のジャケット式加熱器８に返送し、貯留槽５の温度を５０℃に保持することが好ましい。   Here, when, for example, ethanol (boiling point 78.37 ° C.) is used as the liquid reducing agent, the temperature of the liquid reducing agent in the liquid reducing agent storage tank 5 is preferably maintained at 40 ° C. or higher and 60 ° C. or lower. At this time, for example, in the heat exchanger 9 installed in the exhaust passage 2 on the downstream side of the denitration catalyst layer 4, the circulating heat medium is heated to, for example, 50 ° C. with the exhaust heat of the purified exhaust gas discharged from the catalyst layer 4. Then, it is preferable to return to the jacket type heater 8 of the storage tank 5 by the heat medium circulation pipe 10 and keep the temperature of the storage tank 5 at 50 ° C.

上記のように、脱硝触媒層４の下流側の排気通路２に循環熱媒体加熱用熱交換器９が設置されて、脱硝触媒層４から排出された浄化排ガスの排熱を利用して、液体還元剤貯留槽５の温度が一定に保持されている。ここで、循環熱媒体としては、通常、水を使用するが、その他、ペンタン、イソペンタン、ブタン、プロパン等の低分子炭化水素、およびフロン（Ｒ１３４ａ、Ｒ２４５ｆａ）等を用いることができる。循環熱媒体は、回収する排熱の温度分布に応じて最適なものが選定される。   As described above, the circulating heat medium heating heat exchanger 9 is installed in the exhaust passage 2 on the downstream side of the denitration catalyst layer 4, and the exhaust heat of the purified exhaust gas discharged from the denitration catalyst layer 4 is used to generate liquid. The temperature of the reducing agent storage tank 5 is kept constant. Here, water is usually used as the circulating heat medium, but other low molecular hydrocarbons such as pentane, isopentane, butane, and propane, and Freon (R134a, R245fa) can also be used. An optimum circulating heat medium is selected according to the temperature distribution of the exhaust heat to be recovered.

本発明の第１発明の排ガス浄化システムにおいて、コンプレッサー６から導管７を経て液体還元剤貯留槽５の上部空間内に供給する圧縮空気の流量および貯留槽内液体還元剤温度を制御することにより、排ガスに添加する気化還元剤量を制御することが好ましい。   In the exhaust gas purification system of the first invention of the present invention, by controlling the flow rate of compressed air supplied from the compressor 6 via the conduit 7 into the upper space of the liquid reducing agent storage tank 5 and the liquid reducing agent temperature in the storage tank, It is preferable to control the amount of the vaporizing and reducing agent added to the exhaust gas.

上記のように、貯留槽５内の液体還元剤の温度を所定温度（例えば５０℃）に保持することにより、貯留槽５の上部空間内の気化還元剤の蒸気圧は一定に保持され、貯留槽５の上部空間内の気化還元剤の濃度が一定となる。従って、貯留槽５の上部空間内に供給する圧縮空気の流量および貯留槽内液体還元剤温度を制御することにより、圧縮空気に同伴される気化還元剤の量も制御され、この気化還元剤同伴空気を還元剤供給管３から排気通路２内の排ガスに添加することにより、排ガスへの気化還元剤の添加量を制御することが可能となる。   As described above, by keeping the temperature of the liquid reducing agent in the storage tank 5 at a predetermined temperature (for example, 50 ° C.), the vapor pressure of the vaporizing reducing agent in the upper space of the storage tank 5 is kept constant, and stored. The concentration of the vaporization reducing agent in the upper space of the tank 5 is constant. Therefore, by controlling the flow rate of the compressed air supplied into the upper space of the storage tank 5 and the liquid reducing agent temperature in the storage tank, the amount of the vaporizing and reducing agent accompanying the compressed air is also controlled. By adding air from the reducing agent supply pipe 3 to the exhaust gas in the exhaust passage 2, it is possible to control the amount of the vaporized reducing agent added to the exhaust gas.

また、気化還元剤同伴空気中の気化還元剤濃度を一定にするために、液体還元剤貯留槽５内の液体還元剤の貯留量を一定に保つことが好ましい。   Further, in order to make the concentration of the vapor reducing agent in the vapor reducing agent accompanying air constant, it is preferable to keep the amount of the liquid reducing agent stored in the liquid reducing agent storage tank 5 constant.

すなわち、本発明の第１発明の排ガス浄化システムにおいて、さらに液体還元剤保管槽１２を備えており、前記液体還元剤貯留槽５には液面計（レベルスイッチ）（図示略）が設置され、この液面計からの貯留槽５内の液体還元剤の上面（液面）のレベル検知信号に基づいて、還元剤液面レベルが貯留下限値を下回った際に、液体還元剤保管槽１２からポンプ１４の作動により導管１３を経て液体還元剤を補充し、還元剤液面レベルが貯留上限値を上回った際に、ポンプ１４の作動を止めて、液体還元剤の補充を停止することにより、液体還元剤貯留槽５に供給される還元剤の供給量を制御することが好ましい。   That is, the exhaust gas purification system of the first invention of the present invention further includes a liquid reducing agent storage tank 12, and a liquid level gauge (not shown) is installed in the liquid reducing agent storage tank 5. Based on the level detection signal of the upper surface (liquid level) of the liquid reducing agent in the storage tank 5 from the liquid level gauge, when the reducing agent liquid level falls below the storage lower limit value, the liquid reducing agent storage tank 12 When the liquid reducing agent is replenished via the conduit 13 by the operation of the pump 14 and the reductant liquid level exceeds the storage upper limit value, the operation of the pump 14 is stopped and the replenishment of the liquid reducing agent is stopped. It is preferable to control the supply amount of the reducing agent supplied to the liquid reducing agent storage tank 5.

本発明の第１発明によれば、例えば船舶用ディーゼルエンジン等の内燃機関の排ガスのように、排ガス温度が２００〜４００℃程度の比較的低温域の排ガスであっても、アルコール、炭化水素などの液体還元剤を用いて、しかも排ガスに添加する際に、事前に気化した還元剤を供給することができるため、液体還元剤の気化熱による排ガス温度の低下を抑制し、高い脱硝性能を維持することができる。そのうえ、液体還元剤貯留槽５の上部空間内に供給する圧縮空気の流量および貯留槽内液体還元剤温度を制御することにより、圧縮空気に同伴される気化還元剤の量を制御することができ、この気化還元剤同伴空気を還元剤供給管３から排気通路２内の排ガスに添加することにより、排ガスへの気化還元剤の添加量の制御が容易であり、実用性に優れているものである。   According to the first invention of the present invention, alcohol, hydrocarbons, etc., even if the exhaust gas temperature is a relatively low temperature exhaust gas having a temperature of about 200 to 400 ° C., such as exhaust gas from an internal combustion engine such as a marine diesel engine. In addition, it is possible to supply a pre-vaporized reducing agent when it is added to the exhaust gas, thus suppressing a decrease in exhaust gas temperature due to the heat of vaporization of the liquid reducing agent and maintaining high denitration performance. can do. In addition, by controlling the flow rate of the compressed air supplied into the upper space of the liquid reducing agent storage tank 5 and the temperature of the liquid reducing agent in the storage tank, the amount of vaporization reducing agent accompanying the compressed air can be controlled. By adding this vaporized reducing agent-entrained air from the reducing agent supply pipe 3 to the exhaust gas in the exhaust passage 2, it is easy to control the amount of the vaporized reducing agent added to the exhaust gas and has excellent practicality. is there.

図２は、本発明の第１発明による排ガス浄化システムの第２実施形態を示すフローシートである。   FIG. 2 is a flow sheet showing a second embodiment of the exhaust gas purification system according to the first invention of the present invention.

ここで、上記第１発明の第１実施形態の場合と異なる点は、液体還元剤貯留槽５に内部加熱器（加熱手段）１５が設けられ、この内部加熱器１５によって貯留槽５内の液体還元剤の温度が調整される点にある。そしてこの場合、脱硝触媒層４の下流側の排気通路２に循環熱媒体加熱用熱交換器９が設置され、該熱交換器９と上記内部加熱器１５とは熱媒体循環管１０によって接続されており、熱媒体循環管１０の途上に介在させられたポンプ１１の作動によって、貯留槽５の内部加熱器１５から加熱用循環熱媒体が熱交換器９に送り込まれ、この熱交換器９おいて循環熱媒体が、触媒層４から排出された浄化排ガスの排熱で加温された後、液体還元剤貯留槽５の内部加熱器１５に返送されて、貯留槽５の温度が一定に保持されることが好ましい。このとき、例えば液体還元剤としてエタノールを使用した場合、例えば脱硝触媒層４の下流側の排気通路２に設置された熱交換器９において、触媒層４から排出された浄化排ガスの排熱で循環熱媒体を、例えば５０℃に加温した後、熱媒体循環管１０によって貯留槽５の内部加熱器１５に返送し、貯留槽５の温度を５０℃に保持することが好ましい。   Here, the difference from the case of the first embodiment of the first invention is that an internal heater (heating means) 15 is provided in the liquid reducing agent storage tank 5, and the liquid in the storage tank 5 is provided by the internal heater 15. The temperature of the reducing agent is adjusted. In this case, a circulating heat medium heating heat exchanger 9 is installed in the exhaust passage 2 downstream of the denitration catalyst layer 4, and the heat exchanger 9 and the internal heater 15 are connected by the heat medium circulation pipe 10. By the operation of the pump 11 interposed in the middle of the heat medium circulation pipe 10, the circulating heat medium for heating is sent from the internal heater 15 of the storage tank 5 to the heat exchanger 9, and this heat exchanger 9 The circulating heat medium is heated by the exhaust heat of the purified exhaust gas discharged from the catalyst layer 4 and then returned to the internal heater 15 of the liquid reducing agent storage tank 5 to keep the temperature of the storage tank 5 constant. It is preferred that At this time, for example, when ethanol is used as the liquid reducing agent, for example, in the heat exchanger 9 installed in the exhaust passage 2 on the downstream side of the denitration catalyst layer 4, it is circulated by the exhaust heat of the purified exhaust gas discharged from the catalyst layer 4. After heating the heat medium to, for example, 50 ° C., it is preferable to return the heat medium to the internal heater 15 of the storage tank 5 by the heat medium circulation pipe 10 and keep the temperature of the storage tank 5 at 50 ° C.

なお、第１発明の第２実施形態の排ガス浄化システムにおいて、コンプレッサー６から導管７を経て液体還元剤貯留槽５の上部空間内に供給する圧縮空気の流量および貯留槽内液体還元剤温度を制御することにより、排ガスに添加する気化還元剤量を制御したり、気化還元剤同伴空気中の気化還元剤濃度を一定にするために、液体還元剤貯留槽５に液面計（レベルスイッチ）（図示略）を設置して、貯留槽５中の液体還元剤の貯留レベルを一定に保持するなど点は、上記第１発明の第１実施形態の場合と同様である。   In the exhaust gas purification system according to the second embodiment of the first invention, the flow rate of compressed air supplied from the compressor 6 to the upper space of the liquid reducing agent storage tank 5 through the conduit 7 and the liquid reducing agent temperature in the storage tank are controlled. Therefore, in order to control the amount of the vaporizing / reducing agent added to the exhaust gas, or to keep the vaporizing / reducing agent concentration in the air accompanying the vaporizing / reducing agent constant, a liquid level gauge (level switch) ( (Not shown) is installed and the storage level of the liquid reducing agent in the storage tank 5 is kept constant, as in the case of the first embodiment of the first invention.

この第１発明の第２実施形態において、その他の点は、上記第１発明の第１実施形態の場合と同様であるので、図２において、上記図１と同一のものには、同一の符号を付した。   In the second embodiment of the first invention, the other points are the same as in the case of the first embodiment of the first invention. Therefore, in FIG. 2, the same components as those in FIG. Was attached.

図３は、本発明の第２発明による排ガス浄化システムの第１実施形態を示すフローシートである。   FIG. 3 is a flow sheet showing the first embodiment of the exhaust gas purification system according to the second invention of the present invention.

同図を参照すると、本発明の第２の発明は、例えば船舶用ディーゼルエンジン等の内燃機関などの排ガス源１からの排気通路２に、上流側から順に還元剤供給用管（還元剤供給手段）３と脱硝触媒層４が配置され、前記還元剤供給用管３より還元剤が前記触媒層４に添加され、排ガス中の窒素酸化物が還元されて、排ガスが浄化される排ガス浄化システムであって、液体還元剤を貯留させるための液体還元剤貯留槽５と、還元剤気化用熱交換器１６とを備えており、液体還元剤貯留槽５からポンプ１８の作動により導管１７を経て導出された還元剤が熱交換器１６において加熱されて気化せしめられ、この気化還元剤が、前記還元剤供給管３に供給されることを特徴としている。   Referring to the figure, a second invention of the present invention is a reducing agent supply pipe (reducing agent supply means) in order from the upstream side to an exhaust passage 2 from an exhaust gas source 1 such as an internal combustion engine such as a marine diesel engine. ) 3 and a denitration catalyst layer 4 are disposed, a reducing agent is added to the catalyst layer 4 from the reducing agent supply pipe 3, and nitrogen oxides in the exhaust gas are reduced, whereby the exhaust gas is purified. The liquid reducing agent storage tank 5 for storing the liquid reducing agent and the heat exchanger 16 for vaporizing the reducing agent are provided. The liquid reducing agent storage tank 5 is led out through the conduit 17 by the operation of the pump 18. The reduced reducing agent heated in the heat exchanger 16 is vaporized, and the vaporized reducing agent is supplied to the reducing agent supply pipe 3.

この第２発明の排ガス浄化システムにおいて、還元剤気化用熱交換器１６が、脱硝触媒層４の下流側の排気通路２に設置され、該熱交換器１６において触媒層４から排出された浄化排ガスの排熱で液体還元剤が加熱されて気化せしめられることが好ましい。   In the exhaust gas purification system of the second invention, the reducing agent vaporization heat exchanger 16 is installed in the exhaust passage 2 on the downstream side of the denitration catalyst layer 4, and the purified exhaust gas discharged from the catalyst layer 4 in the heat exchanger 16. It is preferable that the liquid reducing agent is heated and vaporized by the exhaust heat.

本発明の第２本発明の排ガス浄化システムにおいて、液体還元剤として用いることができる化合物は、上記第１発明の場合と同様に、アルコール類、エーテル類、ケトン類、および炭化水素よりなる群の中から選ばれた少なくとも１つの低分子量の有機化合物である。   In the exhaust gas purification system of the second invention of the present invention, the compound that can be used as the liquid reducing agent is the group consisting of alcohols, ethers, ketones, and hydrocarbons, as in the first invention. It is at least one organic compound having a low molecular weight selected from among them.

ここで、液体還元剤として、例えばエタノール（沸点７８．３７℃）を使用した場合、脱硝触媒層４の下流側の排気通路２に設置された熱交換器１６において触媒層４から排出された浄化排ガスの排熱でエタノールよりなる還元剤が沸点以上に加熱されて気化せしめられ、この気化還元剤が、還元剤供給管３より排気通路２内に供給されるものである。   Here, when, for example, ethanol (boiling point 78.37 ° C.) is used as the liquid reducing agent, the purification exhausted from the catalyst layer 4 in the heat exchanger 16 installed in the exhaust passage 2 on the downstream side of the denitration catalyst layer 4. The reducing agent made of ethanol is heated to the boiling point or higher by the exhaust heat of the exhaust gas and vaporized, and this vaporized reducing agent is supplied into the exhaust passage 2 from the reducing agent supply pipe 3.

本発明の第２発明の排ガス浄化システムにおいては、液体還元剤貯留槽５からポンプ１８の作動により導出される液体還元剤の導出量を制御することにより、排ガスに添加する気化還元剤量を制御することが好ましい。   In the exhaust gas purification system of the second invention of the present invention, the amount of vaporized reducing agent added to the exhaust gas is controlled by controlling the amount of liquid reducing agent derived from the liquid reducing agent storage tank 5 by the operation of the pump 18. It is preferable to do.

本発明の第２発明の排ガス浄化システムにおいて、さらに液体還元剤保管槽１２を備えており、液体還元剤保管槽１２からポンプ１４の作動により導管１３を経て液体還元剤を液体還元剤貯留槽５に補充するようになされている。ここで、液体還元剤貯留槽５内の液体還元剤の貯留量を保持するには、例えば液体還元剤貯留槽５からポンプ１８の作動により導管１７を経て気化用熱交換器１６に導出される還元剤の導出量に対応して、液体還元剤保管槽１２からポンプ１４の作動により同量の液体還元剤を液体還元剤貯留槽５に補充するように、両ポンプ１４，１８の導出量を制御することが好ましい。   In the exhaust gas purification system of the second invention of the present invention, a liquid reducing agent storage tank 12 is further provided, and the liquid reducing agent is stored in the liquid reducing agent storage tank 5 via the conduit 13 by the operation of the pump 14 from the liquid reducing agent storage tank 12. It is made to replenish. Here, in order to hold the storage amount of the liquid reducing agent in the liquid reducing agent storage tank 5, for example, the liquid reducing agent storage tank 5 is led to the vaporization heat exchanger 16 through the conduit 17 by the operation of the pump 18. Corresponding to the derived amount of reducing agent, the derived amounts of both pumps 14 and 18 are set so that the same amount of liquid reducing agent is replenished to the liquid reducing agent storage tank 5 by the operation of the pump 14 from the liquid reducing agent storage tank 12. It is preferable to control.

本発明の第２発明の排ガス浄化システムによれば、例えば船舶用ディーゼルエンジン等の内燃機関の排ガスのように、排ガス温度が２００〜４００℃程度の比較的低温域の排ガスであっても、アルコール、炭化水素などの液体還元剤を用いて、しかも排ガスに添加する際に、事前に気化した還元剤を供給することができるため、液体還元剤の気化熱による排ガス温度の低下を抑制し、高い脱硝性能を維持することができる。そのうえ、液体還元剤貯留槽５からポンプ１８の作動により導出される液体還元剤の導出量を制御することにより、排ガスへの気化還元剤の添加量の制御が容易であり、実用性に優れているものである。   According to the exhaust gas purification system of the second aspect of the present invention, even if the exhaust gas temperature is an exhaust gas in a relatively low temperature range of about 200 to 400 ° C., such as exhaust gas of an internal combustion engine such as a marine diesel engine, alcohol In addition, when a liquid reducing agent such as hydrocarbon is used and added to the exhaust gas, a reducing agent vaporized in advance can be supplied, so that a reduction in the exhaust gas temperature due to the heat of vaporization of the liquid reducing agent is suppressed and high. Denitration performance can be maintained. In addition, by controlling the amount of the liquid reducing agent derived from the liquid reducing agent storage tank 5 by the operation of the pump 18, it is easy to control the amount of the vaporizing reducing agent added to the exhaust gas, and the practicality is excellent. It is what.

つぎに、本発明の実施例を比較例と共に説明するが、本発明は、これらの実施例に限定されるものではない。   Next, examples of the present invention will be described together with comparative examples, but the present invention is not limited to these examples.

（実施例１）
本発明の第１発明の第１実施形態のフローシートを示す図１に基づいて本発明の排ガス浄化システムを実施した。 Example 1
The exhaust gas purification system of the present invention was implemented based on FIG. 1 showing the flow sheet of the first embodiment of the first invention of the present invention.

同図を参照すると、本発明の排ガス浄化システムにおいて、例えば船舶用ディーゼルエンジン等の内燃機関などの排ガス源１からの排気通路２に、上流側から順に還元剤供給用管（還元剤供給手段）３と脱硝触媒層４が配置され、さらに排ガス浄化システムには、液体還元剤を貯留させるための液体還元剤貯留槽５と、コンプレッサー（圧縮空気供給手段）６とを備えている。   Referring to the figure, in the exhaust gas purification system of the present invention, for example, a reducing agent supply pipe (reducing agent supply means) is sequentially supplied from an upstream side to an exhaust passage 2 from an exhaust gas source 1 such as an internal combustion engine such as a marine diesel engine. 3 and a denitration catalyst layer 4 are disposed, and the exhaust gas purification system further includes a liquid reducing agent storage tank 5 for storing the liquid reducing agent and a compressor (compressed air supply means) 6.

ここで、排ガスとしては、酸素（Ｏ２）を１３．８〔ｖｏｌ％−ｄｒｙ〕、水（Ｈ２Ｏ）を５．０〔ｖｏｌ％−ｗｅｔ〕、窒素酸化物（ＮＯｘ）を１０００〔ｐｐｍｖｄ〕、硫黄酸化物（ＳＯｘ）を６００〔ｐｐｍｖｄ〕、それぞれ含有する合成ガスを使用し、２５０〔℃〕の温度で排気通路２に供給した。 Here, as the exhaust gas, oxygen (O 2) 13.8 [vol% -dry], water (H 2 O) 5.0 [vol% -wet], nitrogen oxides (NOx) 1000 [ppmvd The synthesis gas containing 600 [ppmvd] of sulfur oxide (SOx) was used and supplied to the exhaust passage 2 at a temperature of 250 [° C.].

脱硝触媒層４には、コバルトをイオン交換したゼオライトが担持されたコルゲート・ハニカム構造型脱硝触媒を充填した。   The denitration catalyst layer 4 was filled with a corrugated honeycomb structure type denitration catalyst on which zeolite ion-exchanged cobalt was supported.

また、液体還元剤としてエタノール（ＣＨ３ＣＨ２ＯＨ：沸点７８．３７℃、５０００〔ｐｐｍｖｄ〕）を使用した。そして、脱硝触媒層４の下流側の排気通路２に設置された循環水加熱用熱交換器９において、触媒層４から排出された浄化排ガスの排熱で循環水を、例えば５０℃に加温した後、温水循環管１０によって液体エタノール貯留槽５のジャケット式加熱器８に返送し、貯留槽５の温度を５０℃に保持した。 Further, ethanol (CH 3 CH 2 OH: boiling point 78.37 ° C., 5000 [ppmvd]) was used as a liquid reducing agent. Then, in the circulating water heating heat exchanger 9 installed in the exhaust passage 2 downstream of the denitration catalyst layer 4, the circulating water is heated to, for example, 50 ° C. with the exhaust heat of the purified exhaust gas discharged from the catalyst layer 4. After that, it was returned to the jacket type heater 8 of the liquid ethanol storage tank 5 by the hot water circulation pipe 10, and the temperature of the storage tank 5 was kept at 50 ° C.

そして、液体エタノール貯留槽５上部の空間内に、コンプレッサー６から導管７を経て圧縮空気を供給（パージ）することで、気化エタノール同伴空気を形成し、この気化エタノール同伴空気を前記還元剤供給管３より排気通路２内に供給し、排ガスおよび還元剤としての気化エタノールを触媒層４の脱硝触媒に接触させて、脱硝反応による排ガスの浄化を実施した。このとき、脱硝触媒層４における面積速度を５．０（ｍ／ｈ）とし、反応温度を２５０℃とした。   Then, by supplying (purging) compressed air from the compressor 6 through the conduit 7 into the space above the liquid ethanol storage tank 5, vaporized ethanol-entrained air is formed, and this vaporized ethanol-entrained air is supplied to the reducing agent supply pipe. 3 was supplied into the exhaust passage 2 and exhaust gas and vaporized ethanol as a reducing agent were brought into contact with the denitration catalyst of the catalyst layer 4 to purify the exhaust gas by denitration reaction. At this time, the area velocity in the denitration catalyst layer 4 was 5.0 (m / h), and the reaction temperature was 250 ° C.

ここで、面積速度は、ハニカム型脱硝触媒のガス接触面積あたりの処理ガス量であり、次式で表される。   Here, the area velocity is a processing gas amount per gas contact area of the honeycomb type denitration catalyst, and is represented by the following equation.

面積速度＝処理ガス量（Ｎｍ３／ｈ）／ガス接触面積（ｍ２）
なお、貯留槽５内の液体エタノールの温度を５０℃に保持することにより、貯留槽５の上部空間内の気化還元剤の蒸気圧は一定に保持され、貯留槽５の上部空間内の気化還元剤の濃度が一定となった。このため、貯留槽５の上部空間内に供給する圧縮空気の流量および貯留槽内液体還元剤温度を制御することにより、圧縮空気に同伴される気化還元剤の量も制御され、この気化還元剤同伴空気を還元剤供給管３から排気通路２内の排ガスに添加することにより、排ガスへの気化還元剤の添加量を制御することができた。 Area velocity = treatment gas amount (Nm 3 / h) / gas contact area (m 2 )
In addition, by keeping the temperature of the liquid ethanol in the storage tank 5 at 50 ° C., the vapor pressure of the vaporization reducing agent in the upper space of the storage tank 5 is kept constant, and the vaporization reduction in the upper space of the storage tank 5 is performed. The concentration of the agent became constant. For this reason, by controlling the flow rate of the compressed air supplied into the upper space of the storage tank 5 and the liquid reducing agent temperature in the storage tank, the amount of the vaporizing reducing agent accompanying the compressed air is also controlled. By adding accompanying air to the exhaust gas in the exhaust passage 2 from the reducing agent supply pipe 3, the amount of the vaporized reducing agent added to the exhaust gas could be controlled.

また、気化エタノール同伴空気を前記還元剤供給管３より排気通路２内に供給する際の気化エタノール同伴空気の温度は、約５０℃であるが、排ガスに添加する際に、事前に気化したエタノールよりなる還元剤を供給することができるため、液体エタノールの気化熱による排ガス温度の低下を抑制することができ、脱硝触媒層４の入口の排ガス温度は、約２５０℃と変わらず、これによって、触媒層４の触媒による高い脱硝性能を維持することができた。   Further, the temperature of the vaporized ethanol-entrained air when the vaporized ethanol-entrained air is supplied from the reducing agent supply pipe 3 into the exhaust passage 2 is about 50 ° C., but the ethanol vaporized in advance is added to the exhaust gas. Therefore, the reduction of the exhaust gas temperature due to the heat of vaporization of liquid ethanol can be suppressed, and the exhaust gas temperature at the inlet of the denitration catalyst layer 4 remains about 250 ° C. High denitration performance by the catalyst of the catalyst layer 4 could be maintained.

下記の表１に、排ガス源１から排気通路２に導入した排ガスの温度と、還元剤供給管３より気化エタノール同伴空気を排気通路２内に供給した後の脱硝触媒層入口の排ガス温度を示した。   Table 1 below shows the temperature of the exhaust gas introduced from the exhaust gas source 1 into the exhaust passage 2 and the exhaust gas temperature at the inlet of the denitration catalyst layer after the vaporized ethanol-entrained air is supplied from the reducing agent supply pipe 3 into the exhaust passage 2. It was.

なお、この実施例においては、図示は省略したが、気化エタノール同伴空気中の気化エタノール濃度を一定にするために、貯留槽５内の液体エタノールの貯留量を一定に保持するようにした。このため、排ガス浄化システムにさらに液体エタノール保管槽１２を備え、前記液体エタノール貯留槽５には液面計（レベルスイッチ）を設置して、この液面計からの貯留槽５内の液体エタノールの上面（液面）のレベル検知信号に基づき、エタノール液面レベルが貯留下限値を下回った際に、液体エタノール保管槽１２からポンプ１４の作動により導管１３を経て液体エタノールを補充し、エタノール液面レベルが貯留上限値を上回った際に、ポンプ１４の作動を止めて、液体エタノールの補充を停止することにより、液体エタノール貯留槽５に供給されるエタノールの供給量を制御するようにした。   In this embodiment, although not shown, in order to keep the vaporized ethanol concentration in the vaporized ethanol accompanying air constant, the amount of liquid ethanol stored in the storage tank 5 is kept constant. For this reason, the exhaust gas purification system is further provided with a liquid ethanol storage tank 12, and a liquid level gauge (level switch) is installed in the liquid ethanol storage tank 5, so that the liquid ethanol in the storage tank 5 from the liquid level gauge Based on the level detection signal of the upper surface (liquid level), when the ethanol liquid level falls below the storage lower limit value, liquid ethanol is replenished from the liquid ethanol storage tank 12 through the conduit 13 by the operation of the pump 14, and the ethanol liquid level When the level exceeded the upper storage limit, the pump 14 was stopped and the supply of liquid ethanol was stopped, thereby controlling the amount of ethanol supplied to the liquid ethanol storage tank 5.

（実施例２）
上記第１実施例の場合と同様にして、本発明の排ガス浄化システムを実施するが、第１実施例の場合と異なる点は、本発明の第１発明の第２実施形態のフローシートを示す図２に基づいて排ガス浄化システムを実施した点にある。すなわち、液体還元剤貯留槽５の内部に加熱器（加熱手段）１５が設けられ、この内部加熱器１５によって貯留槽５内の液体還元剤の温度を調整した。具体的には、液体還元剤としてエタノールを使用し、脱硝触媒層４の下流側の排気通路２に設置された熱交換器９において、触媒層４から排出された浄化排ガスの排熱で循環水を、５０℃に加温した後、温水循環管１０によって貯留槽５の内部加熱器１５に返送し、貯留槽５の温度を５０℃に保持した。 (Example 2)
The exhaust gas purification system of the present invention is implemented in the same manner as in the case of the first example, but the difference from the case of the first example is the flow sheet of the second embodiment of the first invention of the present invention. The exhaust gas purification system is implemented based on FIG. That is, a heater (heating means) 15 was provided inside the liquid reducing agent storage tank 5, and the temperature of the liquid reducing agent in the storage tank 5 was adjusted by the internal heater 15. Specifically, ethanol is used as the liquid reducing agent, and in the heat exchanger 9 installed in the exhaust passage 2 on the downstream side of the denitration catalyst layer 4, the circulating water is discharged by the exhaust heat of the purified exhaust gas discharged from the catalyst layer 4. Was heated to 50 ° C. and then returned to the internal heater 15 of the storage tank 5 by the hot water circulation pipe 10 to keep the temperature of the storage tank 5 at 50 ° C.

この第２実施例において、その他の点は、上記第１実施例の場合と同様であり、下記の表１に、排ガス源１から排気通路２に導入した排ガスの温度と、還元剤供給管３より気化エタノール同伴空気を排気通路２内に供給した後の脱硝触媒層入口の排ガス温度をあわせて示した。   In the second embodiment, the other points are the same as in the case of the first embodiment. Table 1 below shows the temperature of the exhaust gas introduced from the exhaust gas source 1 into the exhaust passage 2 and the reducing agent supply pipe 3. The exhaust gas temperature at the inlet of the denitration catalyst layer after supplying vaporized ethanol-entrained air into the exhaust passage 2 is also shown.

（実施例３）
上記第１実施例の場合と同様にして、本発明の排ガス浄化システムを実施するが、第１実施例の場合と異なる点は、本発明の第２発明の第１実施形態のフローシートを示す図３に基づいて排ガス浄化システムを実施した点にある。 (Example 3)
The exhaust gas purification system of the present invention is implemented in the same manner as in the case of the first example, but the difference from the case of the first example is the flow sheet of the first embodiment of the second invention of the present invention. The exhaust gas purification system is implemented based on FIG.

同図を参照すると、本発明の排ガス浄化システムにおいて、排ガス源１からの排気通路２に、上流側から順に還元剤供給用管（還元剤供給手段）３と脱硝触媒層４が配置され、さらに排ガス浄化システムには、液体還元剤を貯留させるための液体還元剤貯留槽５と、還元剤気化用熱交換器１６とを備えており、液体還元剤貯留槽５からポンプ１８の作動により導管１７を経て導出された還元剤が熱交換器１６において加熱されて気化せしめられ、この気化還元剤が、前記還元剤供給管３に供給される。この第３実施例において、還元剤気化用熱交換器１６が、脱硝触媒層４の下流側の排気通路２に設置され、該熱交換器１６において触媒層４から排出された浄化排ガスの排熱で液体還元剤が加熱されて気化せしめられる。上記実施例１の場合と同様に、液体還元剤としてエタノール（沸点７８．３７℃）を使用しており、脱硝触媒層４の下流側の排気通路２に設置された熱交換器１６において触媒層４から排出された浄化排ガスの排熱でエタノールよりなる液体還元剤を１２０℃に加熱して気化させ、この気化還元剤を、還元剤供給管３より排気通路２内に供給した。   Referring to the figure, in the exhaust gas purification system of the present invention, a reducing agent supply pipe (reducing agent supply means) 3 and a denitration catalyst layer 4 are disposed in the exhaust passage 2 from the exhaust gas source 1 in order from the upstream side. The exhaust gas purification system includes a liquid reducing agent storage tank 5 for storing a liquid reducing agent and a heat exchanger 16 for reducing agent vaporization, and a conduit 17 is operated from the liquid reducing agent storage tank 5 by operating a pump 18. The reducing agent derived through the above is heated and vaporized in the heat exchanger 16, and this vaporized reducing agent is supplied to the reducing agent supply pipe 3. In this third embodiment, a reducing agent vaporizing heat exchanger 16 is installed in the exhaust passage 2 downstream of the denitration catalyst layer 4, and the exhaust heat of the purified exhaust gas discharged from the catalyst layer 4 in the heat exchanger 16. The liquid reducing agent is heated and vaporized. As in the case of Example 1 above, ethanol (boiling point 78.37 ° C.) is used as the liquid reducing agent, and the catalyst layer is installed in the heat exchanger 16 installed in the exhaust passage 2 downstream of the denitration catalyst layer 4. The liquid reducing agent made of ethanol was heated to 120 ° C. by the exhaust heat of the purified exhaust gas discharged from 4 and vaporized, and this vaporized reducing agent was supplied into the exhaust passage 2 from the reducing agent supply pipe 3.

ここで、気化エタノールを還元剤供給管３より排気通路２内に供給する際の気化エタノールの温度は、約１２０℃であるが、排ガスに添加する際に、事前に気化したエタノールよりなる還元剤を供給することができるため、液体エタノールの気化熱による排ガス温度の低下を抑制することができ、脱硝触媒層４の入口の排ガス温度は、約２５０℃と変わらず、これによって、高い脱硝性能を維持することができた。   Here, the temperature of vaporized ethanol when the vaporized ethanol is supplied from the reducing agent supply pipe 3 into the exhaust passage 2 is about 120 ° C., but when added to the exhaust gas, the reducing agent is made of ethanol vaporized in advance. Therefore, the decrease in exhaust gas temperature due to the heat of vaporization of liquid ethanol can be suppressed, and the exhaust gas temperature at the inlet of the denitration catalyst layer 4 does not change from about 250 ° C., thereby achieving high denitration performance. Could be maintained.

下記の表１に、排ガス源１から排気通路２に導入した排ガスの温度と、還元剤供給管３より気化エタノールを排気通路２内に供給した後の脱硝触媒層入口の排ガス温度をあわせて示した。   Table 1 below shows the temperature of the exhaust gas introduced from the exhaust gas source 1 into the exhaust passage 2 and the exhaust gas temperature at the denitration catalyst layer inlet after the vaporized ethanol is supplied into the exhaust passage 2 from the reducing agent supply pipe 3. It was.

なお、液体エタノール貯留槽５からポンプ１８の作動により導管１７を経て気化用熱交換器１６に導出される液体エタノールの導出量に対応して、液体エタノール保管槽１２からポンプ１４の作動により同量の液体エタノールを貯留槽５に補充するように、両ポンプ１４，１８の導出量を制御することにより、液体エタノール貯留槽５内の液体エタノールの貯留量を保持した。   Incidentally, the same amount is obtained from the liquid ethanol storage tank 12 by the operation of the pump 14 corresponding to the amount of liquid ethanol derived from the liquid ethanol storage tank 5 through the conduit 17 to the vaporizing heat exchanger 16 by the operation of the pump 18. The amount of liquid ethanol stored in the liquid ethanol storage tank 5 was maintained by controlling the amount of the pumps 14 and 18 to be replenished to the storage tank 5.

（比較例１）
比較のために、従来の排ガス浄化システムのフローシートを示す図４に基づいて排ガス浄化システムを実施した。 (Comparative Example 1)
For comparison, an exhaust gas purification system was implemented based on FIG. 4 showing a flow sheet of a conventional exhaust gas purification system.

同図を参照すると、従来の排ガス浄化システムにおいて、排ガス源２１からの排気通路２２に、上流側から順に還元剤供給用管（還元剤供給手段）２３と脱硝触媒層２４が配置され、さらに排ガス浄化システムには、液体還元剤を貯留させるための液体還元剤貯留槽２５を備えており、液体還元剤貯留槽２５からポンプ２６の作動により導出された還元剤を、供給管２３から排気通路２２内に直接導入して、排ガス中で気化させた。液体還元剤としては、上記実施例１の場合と同様に、エタノール（沸点７８．３７℃）を使用した。   Referring to the figure, in a conventional exhaust gas purification system, a reducing agent supply pipe (reducing agent supply means) 23 and a denitration catalyst layer 24 are arranged in the exhaust passage 22 from the exhaust gas source 21 in order from the upstream side. The purification system includes a liquid reducing agent storage tank 25 for storing the liquid reducing agent, and the reducing agent derived from the liquid reducing agent storage tank 25 by the operation of the pump 26 is supplied from the supply pipe 23 to the exhaust passage 22. It was directly introduced into the interior and vaporized in the exhaust gas. As the liquid reducing agent, ethanol (boiling point 78.37 ° C.) was used as in the case of Example 1 above.

その結果、液体エタノールの気化熱による排ガス温度の低下が生じて、脱硝触媒層２４の入口の排ガス温度は、２４３℃に低下した。これによって、脱硝触媒層２４の脱硝反応の温度が低下するため、触媒層２４の脱硝性能は低下したものと考えられる。   As a result, the exhaust gas temperature decreased due to the heat of vaporization of liquid ethanol, and the exhaust gas temperature at the inlet of the denitration catalyst layer 24 decreased to 243 ° C. As a result, the temperature of the denitration reaction of the denitration catalyst layer 24 is lowered, and it is considered that the denitration performance of the catalyst layer 24 is lowered.

下記の表１に、排ガス源２１から排気通路２２に導入した排ガスの温度と、還元剤供給管２３より液体エタノールを排気通路２内に直接供給した後の脱硝触媒層２４入口の排ガス温度をあわせて示した。   Table 1 below shows the temperature of the exhaust gas introduced from the exhaust gas source 21 into the exhaust passage 22 and the exhaust gas temperature at the inlet of the denitration catalyst layer 24 after liquid ethanol is directly supplied into the exhaust passage 2 from the reducing agent supply pipe 23. Showed.

なお、この比較例１の排ガス浄化システムにおいて、さらに液体還元剤保管槽２７を備えており、液体還元剤保管槽２７からポンプ２９の作動により導管２８を経て液体エタノールを液体エタノール貯留槽２５に補充するようにした。

Figure 2014156821
The exhaust gas purification system of Comparative Example 1 further includes a liquid reducing agent storage tank 27, and liquid ethanol is replenished to the liquid ethanol storage tank 25 from the liquid reducing agent storage tank 27 through the conduit 28 by the operation of the pump 29. I tried to do it.
Figure 2014156821

上記表１に記載の結果から明らかなように、本発明の実施例１〜３の排ガス浄化システムによれば、排ガス温度が２５０℃程度の比較的低温域の排ガスであっても、エタノールよりなる液体還元剤を用いて、しかも排ガスに添加する際に、事前に気化した還元剤を供給することができるため、液体還元剤の気化熱による排ガス温度の低下を抑制し、脱硝触媒層４入口の温度を低下させることなく、還元剤であるエタノールを添加することができ、脱硝触媒層４での高い脱硝性能を維持することができた。そのうえ、排ガスへの気化還元剤の添加量の制御が容易であり、実用性に優れていることが確認できた。   As is clear from the results shown in Table 1 above, according to the exhaust gas purification systems of Examples 1 to 3 of the present invention, even the exhaust gas at a relatively low temperature range of about 250 ° C. is made of ethanol. When the liquid reducing agent is used and added to the exhaust gas, the reducing agent vaporized in advance can be supplied. Therefore, the reduction of the exhaust gas temperature due to the heat of vaporization of the liquid reducing agent is suppressed, and the inlet of the denitration catalyst layer 4 is suppressed. Without reducing the temperature, ethanol as a reducing agent could be added, and high denitration performance in the denitration catalyst layer 4 could be maintained. In addition, it was easy to control the amount of vaporization reducing agent added to the exhaust gas, and it was confirmed that it was excellent in practicality.

これに対し、比較例１によれば、脱硝触媒層２４の上流側の排気通路２２に、エタノールよりなる還元剤を液体の状態で直接導入し、導入から脱硝触媒層２４に到達するまでの間にエタノールよりなる還元剤を気化させているため、還元剤の気化熱により排ガスの温度低下生じ、脱硝触媒層４における触媒の脱硝性能が低下するという問題が生じた。   On the other hand, according to Comparative Example 1, a reducing agent made of ethanol is directly introduced into the exhaust passage 22 upstream of the denitration catalyst layer 24 in a liquid state, and the period from the introduction to the denitration catalyst layer 24 is reached. Since the reducing agent made of ethanol is vaporized, the temperature of the exhaust gas is lowered due to the heat of vaporization of the reducing agent, resulting in a problem that the denitration performance of the catalyst in the denitration catalyst layer 4 is lowered.

１：内燃機関などの排ガス源
２：排気通路
３：還元剤供給用管（還元剤供給手段）
４：脱硝触媒層
５：液体還元剤貯留槽
６：コンプレッサー（圧縮空気供給手段）
７：導管
８：ジャケット式加熱器（加熱手段）
９：循環水加熱用熱交換器（循環熱媒体加熱用熱交換器）
１０：温水循環管（熱媒体循環管）
１１：ポンプ
１２：液体還元剤保管槽
１３：導管
１４：ポンプ
１５：内部加熱器（加熱手段）
１６：還元剤気化用熱交換器
１７：導管
１８：ポンプ 1: exhaust gas source such as an internal combustion engine 2: exhaust passage 3: reducing agent supply pipe (reducing agent supply means)
4: Denitration catalyst layer 5: Liquid reducing agent storage tank 6: Compressor (compressed air supply means)
7: Conduit 8: Jacket type heater (heating means)
9: Heat exchanger for circulating water heating (heat exchanger for circulating heat medium heating)
10: Hot water circulation pipe (heat medium circulation pipe)
11: Pump 12: Liquid reducing agent storage tank 13: Conduit 14: Pump 15: Internal heater (heating means)
16: Heat exchanger for reducing agent vaporization 17: Conduit 18: Pump

Claims (8)

内燃機関の排気通路に、上流側から順に還元剤供給手段と脱硝触媒層が配置され、前記還元剤供給手段より還元剤が前記触媒層上流側の排ガスに添加され、排ガス中の窒素酸化物が還元されて、排ガスが浄化される排ガス浄化システムにおいて、
液体還元剤貯留槽と、圧縮空気供給手段とを備えており、前記液体還元剤貯留槽内で気化した還元剤に対して前記圧縮空気供給手段から圧縮空気が供給されて、気化還元剤同伴空気が形成され、この気化還元剤同伴空気が前記還元剤供給手段に供給されることを特徴とする、排ガス浄化システム。 A reducing agent supply means and a denitration catalyst layer are arranged in this order from the upstream side in the exhaust passage of the internal combustion engine, the reducing agent is added to the exhaust gas upstream of the catalyst layer from the reducing agent supply means, and nitrogen oxides in the exhaust gas are In the exhaust gas purification system, where the exhaust gas is reduced and purified,
A liquid reducing agent storage tank and compressed air supply means are provided, and compressed air is supplied from the compressed air supply means to the reducing agent vaporized in the liquid reducing agent storage tank, and vaporized reducing agent-entrained air The exhaust gas purification system is characterized in that the vaporized reducing agent-entrained air is supplied to the reducing agent supply means. 前記圧縮空気供給手段から液体還元剤貯留槽内に供給する圧縮空気の流量および貯留槽内液体還元剤温度を制御することにより、排ガスに添加する気化還元剤量を制御することを特徴とする、請求項１に記載の排ガス浄化システム。   By controlling the flow rate of compressed air supplied from the compressed air supply means into the liquid reducing agent storage tank and the liquid reducing agent temperature in the storage tank, the amount of vaporization reducing agent added to the exhaust gas is controlled. The exhaust gas purification system according to claim 1. さらに液体還元剤保管槽を備えており、前記液体還元剤貯留槽には液面計が設置され、この液面計からの貯留槽内還元剤液上面のレベル検知信号に基づいて、前記液体還元剤保管槽から液体還元剤貯留槽に供給される還元剤の供給量が制御されることを特徴とする、請求項１または２に記載の排ガス浄化システム。   Further, a liquid reducing agent storage tank is provided, and a liquid level gauge is installed in the liquid reducing agent storage tank, and the liquid reducing agent is stored on the basis of a level detection signal on the upper surface of the reducing agent liquid in the storage tank from the liquid level gauge. The exhaust gas purification system according to claim 1 or 2, wherein a supply amount of the reducing agent supplied from the agent storage tank to the liquid reducing agent storage tank is controlled. 前記液体還元剤貯留槽に加熱手段が備えられ、この加熱手段によって貯留槽内の液体還元剤の温度が調整されることを特徴とする、請求項１〜３のうちのいずれか一項に記載の排ガス浄化システム。   The said liquid reducing agent storage tank is equipped with a heating means, The temperature of the liquid reducing agent in a storage tank is adjusted with this heating means, It is any one of Claims 1-3 characterized by the above-mentioned. Exhaust gas purification system. 脱硝触媒層の下流側の排気通路に循環熱媒体加熱用熱交換器が設置され、該熱交換器と前記加熱手段とは熱媒体循環管によって接続されており、該熱交換器において触媒層から排出された浄化排ガスの排熱で、液体還元剤貯留槽の加熱手段からの循環熱媒体が加温されることを特徴とする、請求項４に記載の排ガス浄化システム。   A heat exchanger for heating the circulating heat medium is installed in the exhaust passage on the downstream side of the denitration catalyst layer, and the heat exchanger and the heating means are connected by a heat medium circulation pipe, and from the catalyst layer in the heat exchanger The exhaust gas purification system according to claim 4, wherein the circulating heat medium from the heating means of the liquid reducing agent storage tank is heated by the exhaust heat of the exhausted purified exhaust gas. 内燃機関の排気通路に、上流側から順に還元剤供給手段と脱硝触媒層が配置され、前記還元剤供給手段より還元剤が前記触媒層上流側の排ガスに添加され、排ガス中の窒素酸化物が還元されて、排ガスが浄化される排ガス浄化システムにおいて、
液体還元剤貯留槽と、還元剤気化用熱交換器とを備えており、液体還元剤貯留槽から導出された還元剤が熱交換器において加熱されて気化せしめられ、この気化還元剤が、前記還元剤供給手段に供給されることを特徴とする、排ガス浄化システム。 A reducing agent supply means and a denitration catalyst layer are arranged in this order from the upstream side in the exhaust passage of the internal combustion engine, the reducing agent is added to the exhaust gas upstream of the catalyst layer from the reducing agent supply means, and nitrogen oxides in the exhaust gas are In the exhaust gas purification system, where the exhaust gas is reduced and purified,
The reductant storage tank and a heat exchanger for vaporizing the reducing agent are provided, and the reductant derived from the liquid reductant storage tank is heated and vaporized in the heat exchanger. An exhaust gas purification system which is supplied to a reducing agent supply means. 還元剤気化用熱交換器が、脱硝触媒層の下流側の排気通路に設置され、該熱交換器において触媒層から排出された浄化排ガスの排熱で液体還元剤が加熱されて気化せしめられることを特徴とする、請求項６に記載の排ガス浄化システム。   A heat exchanger for reducing agent vaporization is installed in the exhaust passage downstream of the denitration catalyst layer, and the liquid reducing agent is heated and vaporized by the exhaust heat of the purified exhaust gas discharged from the catalyst layer in the heat exchanger. The exhaust gas purification system according to claim 6, wherein: 液体還元剤が、アルコール、エーテル、ケトン類、および炭化水素よりなる群の中から選ばれた少なくとも１つの有機化合物であることを特徴とする、請求項１〜７のうちのいずれか一項に記載の排ガス浄化システム。   The liquid reducing agent is at least one organic compound selected from the group consisting of alcohols, ethers, ketones, and hydrocarbons, according to any one of claims 1 to 7, The exhaust gas purification system described.
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