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JP3711490B2 - Method and apparatus for oxidizing SO2 in exhaust gas using HO2 radical as OH generating reactive species in radical chain reaction of SO2 oxidation - Google Patents
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JP3711490B2 - Method and apparatus for oxidizing SO2 in exhaust gas using HO2 radical as OH generating reactive species in radical chain reaction of SO2 oxidation - Google Patents

Method and apparatus for oxidizing SO2 in exhaust gas using HO2 radical as OH generating reactive species in radical chain reaction of SO2 oxidation Download PDF

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Publication number
JP3711490B2
JP3711490B2 JP2001166676A JP2001166676A JP3711490B2 JP 3711490 B2 JP3711490 B2 JP 3711490B2 JP 2001166676 A JP2001166676 A JP 2001166676A JP 2001166676 A JP2001166676 A JP 2001166676A JP 3711490 B2 JP3711490 B2 JP 3711490B2
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Prior art keywords
exhaust gas
radical
radicals
chain reaction
flow tube
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JP2002361034A (en
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光男 越
正毅 定方
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Japan Science and Technology Agency
National Institute of Japan Science and Technology Agency
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Japan Science and Technology Agency
National Institute of Japan Science and Technology Agency
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Description

【0001】
【発明の属する技術分野】
本発明は、SOの酸化のラジカル連鎖反応におけるOH生成反応を維持するHOラジカルを安定的に制御して生成し得るSOを含む排気ガスの処理方法および該排気ガスの処理方法を実施する設置に関する。
【0002】
【従来の技術】
大気中に排出されるSO、特にSOは酸性雨の発生原因として問題とされてきたが、ヨーロッパや北アメリカでは、大規模な火力発電所から排出されるSOやNOは酸性雨をもたらし、森林や湖沼の生態系への影響がさらに深刻なものとした。また、その問題は一国では解決できない国境を越えた問題となり、更に、経済のグローバル化と共に、この問題は先進国だけでなく発展途上国においてもこれら排ガスの発生源となり、その発生源の対策も経済成長との関連で複雑な問題を引き起こしている。
【0003】
SOなどの排ガスの発生の問題の解決には、燃料の低硫黄化処理のように燃料そのもののSOの発生原因を抑制することにより行う方法と、燃焼排ガスからSOなどを化学的プロセスなどにより除去する方法などがあり、それぞれの技術分野において検討が進められてきた。特に後者の技術手段の開発は、あらかじめSO発生化合物を除去しにくい、石炭を燃料とする場合に重要である。このような問題の解決方法、特に水源に乏しい燃焼設備でSOなどの処理には乾式法が有力であり、このような技術を志向するものとして次の1,2などの技術が提案されている。1,石灰−石膏反応を利用した方法、すなわち、アルカリ土類系の脱硫剤を燃焼炉中または煙道中に吹き込む方法であり、水を使用しない方法であり設備の管理が容易であるという利点がある。2,また、乾式方法として、活性炭吸着法があり、この方法の原理は活性炭によるSOの吸着、SOへの酸化および排ガス中のHOとの反応によるHSO化し、これを回収する方法であるが、コストがかかるという問題がある。電子ビーム法という、排ガス中のO、HOの一部を解離させてO、OH、HOラジカルやイオンを発生させ、SOやNOを酸化して硫酸および硝酸ミスとを生成させ、該反応器にNHを吹き込みアンモニウム塩のエアゾルとし、コットレルなどの電気的集じん器(EP)により捕集するものである。また、パルスコロナ誘起プラズマ化学プロセス(PPCP法)という乾式法もラジカルイオンを発生させ電気集じん器を用いるという点では、ラジカルイオンの発生手段を電子ビーム法から前記手段に変えた類似技術と言える。
【0004】
しかし、前記方法は、多くの化学材料を使用する、設備と管理にコストが多くかかるなどの不都合があり、発展途上国でのSO処理技術としては実用化し難いものである。ただ、前記2,の後半で挙げたラジカルイオンを用いる方法は、使用する薬剤を極めて少ないものとする可能性がある点で魅力的である。
【0005】
【発明が解決しようとする課題】
本願発明の課題は、薬剤の使用を減少させ、かつ反応効率の良いSO処理方法および処理装置を提供することである。このような中で、本発明者らは、ラジカルの反応性に着目した、SOの酸化に関与するラジカルを安定的、かつ制御して供給できる、SOのラジカル連鎖酸化反応系を形成できる方法および装置を鋭意検討する中で、SOの酸化に関与するラジカルOHを高効率で発生できるシステムを構築できることを発見し、前記本発明の課題を解決することができた。
【0006】
【課題を解決するための手段】
本発明の第1は、(1)内側表面温度が327±50℃維持された少なくとも内側表面がホウ珪酸ガラスにより形成されたフロー管または少なくとも表面がホウ珪酸ガラスにより形成されかつ該ガラス表面の温度が327±50℃に維持された部材を配設したフロー管にSOまたはSOおよびNOを含む被処理排気ガス、およびSOのラジカル酸化連鎖反応のトリガーとなるOHラジカルを生成するまたはHNO を導入してHOラジカルの生成反応を含む連鎖反応によりSOを酸化処理することを特徴とするSOを含む排気ガス処理方法である。好ましくは、(2)フロー管へOHラジカルを生成させるH またはHNO の導入部に、更に貴金属を主成分とする触媒又は紫外線照射手段が配設されたH またはHNO の導入手段が設けられていることを特徴とする請求項1に記載のSOを含む排気ガス処理方法、より好ましくは、(3)排ガスが石炭燃焼により生成するものであることを特徴とする前記(1)または(2)に記載のSOを含む排気ガス処理方法であり、一層好ましくは、(4)該SOを含む排気ガス処理フロー管に該酸化連鎖反応におけるHOラジカルの生成を監視し制御する手段が設置されていることを特徴とする前記各SOを含む排気ガス処理方法であり、更に、好ましくは、(5)HOラジカルの生成の監視手段にNd:YAGレーザの2倍の高調波を用いることを特徴とする前記各SOを含む排気ガス処理方法である。
【0007】
本発明の第2は、フロー管の内面温度を327±50℃に維持する加熱手段を備えた少なくとも内面がホウ珪酸ガラスにより形成されたフロー管または少なくとも表面がホウ珪酸ガラスにより形成されかつ該ガラス表面の温度を327±50℃に維持する手段が設けられた部材を配設したフロー管、該フロー管にSOを含む排気ガスを導入する該ガスの予熱装置が設けられていてもよい排ガス導入部、該フロー管にSOの酸化連鎖反応のトリガーとなるOHラジカルを生成するまたはHNO を導入する手段が設けられた前記OHラジカル生成剤またはNで希釈した前記OHラジカル生成剤の導入手段および該フロー管中でのHOラジカルの生成を監視し制御する手段を少なくとも含むSOを含む排気ガスの処理設置。
【0008】
【本発明の実施の態様】
本発明をより詳細に説明する。A.本発明の方法および装置において、SOの酸化反応は以下の各反応の工程からなるものと推測される。 1,OH + SO + M → HOSO + M (R1) 2,HOSO +O→ SO +HO (R) 3,NO+HO →NO +OH (R)ここで、Mは、他のガス成分であり、例えばNなどである。前記連鎖反応を阻害する反応として、 4,OH+HO→ HO+ O (R)すなわち、この阻害反応を抑制するために、OHやHOの濃度を10ppm以下に低く保つ必要がある。B.本発明の工程の概略を図面にしたがって説明する。Fuは燃焼炉であり、例えば石炭燃焼ボイラーである。Fuからの排ガスは例えばブロワーBによりフロー反応器FRに送風される。該FRは図示してないが適当な加熱手段H、電気加熱ヒータ(リボンヒーター)により反応器内面は例えば、327℃に維持されている。Fuの上流側にはラジカル連鎖によるSOの酸化反応を開始させるHやHNOをGRラジカル形成剤触媒(Pt網)Catを通してFR中に導入される。FR中ではGRラジカルが生成され、前記反応(1)〜(3)のラジカル連鎖酸化反応により排ガス中のSOは、SOに酸化され、更に排ガス中の水と反応して硫酸ミストとなり、該ミストの捕集装置S、例えば電気集塵機により回収される。該装置には、HOの生成を間接的にOHラジカルの生成を観察して測定する手段、例えば、Nd:YAGレーザの2倍の高調波を用いて検出発光波長を測定することにより観察できた。
【0009】
【実施例】
実施例1
ホウ珪酸ガラスガラス製(SiO;81%、B:12.7%、Al;2,3%、NaO;4.0%、KO;0.04%、Fe;0.03)の内表面温度を327±5℃に維持したフロー反応管に、1000ppmの濃度でSO(更にNOを含んでいても良い。少量のHOが存在する。)を含むガスVEXを10〜150cm/secの線速度で導入する。該フロー反応管にHを含むガスを前記ガスに対して1〜10%のわりあいで、表面が上記温度に加熱されている管を通して供給する。フロー管では、前記素反応からなるラジカル連鎖反応によりSOが酸化されてSOが生成し、更にVEX存在する少量の水分により硫酸ミストとなり、下流に設けられた、電気集塵器(EP)により硫酸として回収される。
【0010】
該フロー管には、HOを間接的に検出するために、Nd:YAGレーザの2倍の高調波を用いた検出装置(図示なし)が設けられており、反応温度とHOの発生量を観察した。その結果を○印で図2bに示す。327℃近傍では、前記ラジカル連鎖の反応が進行していることが示されている。因みに図2aの実線はPt触媒によるHO発生量と反応温度との相関を示す。
【0011】
【発明の効果】
以上述べたように、本発明はHOという、加熱ガラス表面触媒機能により安定的に供給されるラジカルをSOのラジカル連鎖酸化反応に利用できるようにすることにより、化学薬剤の使用が少なく、かつ効率的なSOの酸化処理を実現できたという優れた効果をもたすものである。
【図面の簡単な説明】
【図1】 本発明のラジカル連鎖反応によるSO酸化処理のための装置に一態様
【図2】 ホウ珪酸ガラス表面の触媒活性によるHOラジカルの生成量実測値および予測値(実線)と反応温度の相関(b)、とPt触媒によるHOラジカルの生成量予測値と反応温度の相関(a)
【符号の説明】
Fu 燃焼炉(燃焼ボイラー) B ブロワー H フロー反応器加熱ヒータGR ラジカル発生剤 FR フロー反応器 EP 電気集塵器GT 処理済みガス St 排ガススタック
[0001]
BACKGROUND OF THE INVENTION
The present invention performs the processing method of the processing method and the exhaust gas in the exhaust gas containing SO 2 that can generate the HO 2 radical controlled stably maintain the OH generation reaction in the radical chain reaction of oxidation of SO 2 Related to installation.
[0002]
[Prior art]
SO X discharged into the atmosphere, especially SO 2, has been a problem as a cause of acid rain. In Europe and North America, SO X and NO X discharged from large-scale thermal power plants are acid rain. And the impact on forest and lake ecosystems is even more severe. In addition, the problem becomes a cross-border problem that cannot be solved by a single country. Furthermore, along with the globalization of the economy, this problem becomes a source of these exhaust gases not only in developed countries but also in developing countries. Are also causing complex problems in connection with economic growth.
[0003]
The resolution of the exhaust gas generation problems, such as SO 2, chemical and methods, such as SO 2 from combustion exhaust gas carried out by suppression win be the cause of SO 2 of the fuel itself as low-sulfur process of the fuel There are methods for removal by processes, etc., and studies have been made in the respective technical fields. In particular the development of the latter technical means is difficult to advance remove SO X generating compound is important when using coal as fuel. A solution to such a problem, particularly a dry method is effective for the treatment of SO 2 in a combustion facility with a poor water source, and the following technologies 1, 2 and the like have been proposed for such technology. Yes. 1, a method using a lime-gypsum reaction, that is, a method in which an alkaline earth desulfurization agent is blown into a combustion furnace or a flue, and is a method that does not use water and has an advantage of easy management of equipment. is there. 2. Further, as a dry method, there is an activated carbon adsorption method. The principle of this method is SO 2 adsorption by activated carbon, oxidation to SO 3 and H 2 SO 4 by reaction with H 2 O in exhaust gas. Although it is a method of collecting, there is a problem that costs are high. The electron beam method is used to dissociate part of O 2 and H 2 O in the exhaust gas to generate O, OH, HO 2 radicals and ions, and to oxidize SO 2 and NO 2 to produce sulfuric acid and nitric acid miss. Then, NH 3 is blown into the reactor to form an ammonium salt aerosol, which is collected by an electric dust collector (EP) such as Cottrell. The dry method called pulse corona induced plasma chemical process (PPCP method) is also a similar technique in which radical ion generation means is changed from the electron beam method to the above means in that radical ions are generated and an electric dust collector is used. .
[0004]
However, this method has disadvantages such as the use of many chemical materials and the cost of equipment and management, and it is difficult to put it to practical use as an SO 2 treatment technique in developing countries. However, the method using the radical ions mentioned in the latter half of the above 2 is attractive in that there is a possibility that the amount of drugs to be used is extremely small.
[0005]
[Problems to be solved by the invention]
Object of the present invention reduces the use of an agent, and to provide a reaction efficient SO 2 processing methods and apparatus. Under such circumstances, the present inventors can form a radical chain oxidation reaction system of SO 2 that can supply radicals involved in the oxidation of SO 2 in a stable and controlled manner, focusing on the reactivity of radicals. in the intensive study of the method and apparatus, it found that a system can be constructed capable of generating the radical Le O H involved in the oxidation of SO 2 with high efficiency, it was possible to solve the problem of the present invention.
[0006]
[Means for Solving the Problems]
The first invention (1) and more formed flow tube or at least the surface of at least the inner surface inner surface temperature was maintained at 327 ± 50 ° C. in a borosilicate glass is more formed on a borosilicate glass Exhaust gas containing SO 2 or SO 2 and NO in a flow tube provided with a member whose glass surface temperature is maintained at 327 ± 50 ° C., and OH radicals that trigger a radical oxidation chain reaction of SO 2 a H 2 O 2 or the exhaust gas treatment method comprising SO 2, characterized in that with the HNO 3 and type electrically oxidizing the SO 2 by chain reaction comprising the reaction of forming HO 2 radicals generate. Preferably, (2) the introduction of the H 2 O 2 or HNO 3 to produce OH radicals to the flow tube, H 2 O 2 or HNO 3 to a catalyst or ultraviolet light irradiation means and further main component a precious metal is disposed The exhaust gas treatment method comprising SO 2 according to claim 1, more preferably (3) the exhaust gas is generated by coal combustion. The exhaust gas treatment method containing SO 2 according to (1) or (2), more preferably (4) generation of HO 2 radicals in the oxidation chain reaction in an exhaust gas treatment flow pipe containing SO 2. is an exhaust gas processing method comprising the respective SO 2, characterized in that monitor and control that means is provided, and further, preferably, Nd in (5) HO 2 radical monitoring means generating a: Y Characterized in that said using double harmonic of the G laser is an exhaust gas processing method comprising the SO 2.
[0007]
The second of the present invention is more formed a flow pipe in which at least the inner surface of the flow tube or at least the surface of borosilicate glass is more formed on borosilicate glass the inner surface temperature with a heating means for maintaining the 327 ± 50 ° C. of And a flow pipe provided with a member provided with means for maintaining the temperature of the glass surface at 327 ± 50 ° C., and a preheating device for the gas for introducing exhaust gas containing SO 2 into the flow pipe. The OH radical generator or N 2 provided with means for introducing H 2 O 2 or HNO 3 that generates OH radicals that trigger the SO 2 oxidation chain reaction into the flow pipe Treatment installation of exhaust gas containing SO 2 comprising at least means for introducing the diluted OH radical generator and means for monitoring and controlling the production of HO 2 radicals in the flow tube .
[0008]
[Embodiments of the present invention]
The present invention will be described in more detail. A. In the method and apparatus of the present invention, the oxidation reaction of SO 2 is presumed to comprise the following reaction steps. 1, OH + SO 2 + M → HOSO 2 + M (R1) 2, HOSO 2 + O 2 → SO 3 + HO 2 (R 2 ) 3, NO + HO 2 → NO 2 + OH (R 3 ) where M is the other For example, N 2 or the like. As a reaction for inhibiting the chain reaction, 4, OH + HO 2 → H 2 O + O 2 (R 4 ), that is, in order to suppress this inhibition reaction, it is necessary to keep the concentration of OH or HO 2 at 10 ppm or less. B. The outline of the process of the present invention will be described with reference to the drawings. Fu is a combustion furnace, for example, a coal combustion boiler. The exhaust gas from Fu is blown to the flow reactor FR by the blower B, for example. Although the FR is not shown, the inner surface of the reactor is maintained at, for example, 327 ° C. by appropriate heating means H and an electric heater (ribbon heater). On the upstream side of the Fu it is introduced into the FR of H 2 O 2 or HNO 3 to initiate the oxidation reaction of SO 2 by radical chain through GR radical former catalysts (Pt networks) Cat. In the FR , a GR radical is generated, and SO 2 in the exhaust gas is oxidized to SO 3 by the radical chain oxidation reaction of the reactions (1) to (3), and further reacts with water in the exhaust gas to become sulfuric acid mist. The mist is collected by a collecting device S, for example, an electric dust collector. The said device, hand stage you measured by observing the generation of indirectly OH radical generation of HO 2, for example, Nd: by measuring the detected emission wavelength with twice the harmonic of a YAG laser I was able to observe.
[0009]
【Example】
Example 1
Borosilicate glass glass (SiO 2 ; 81%, B 2 O 7 : 12.7%, Al 2 O 3 ; 2,3%, Na 2 O; 4.0%, K 2 O; 0.04%, In a flow reaction tube in which the inner surface temperature of Fe 2 O 7 ; 0.03) is maintained at 327 ± 5 ° C., SO 2 (more NO may be contained at a concentration of 1000 ppm. A small amount of H 2 O is present. .) Is introduced at a linear velocity of 10 to 150 cm / sec. A gas containing H 2 O 2 is supplied to the flow reaction tube through a tube whose surface is heated to the above temperature in an amount of 1 to 10% with respect to the gas. In the flow tube, SO 2 is oxidized by radical chain reaction consisting of the elementary reaction to produce SO 3 , and further, a small amount of water present in VEX becomes sulfuric acid mist, and an electric precipitator (EP) provided downstream. Is recovered as sulfuric acid.
[0010]
In order to indirectly detect HO 2 , the flow tube is provided with a detection device (not shown) using harmonics twice that of the Nd: YAG laser, and the reaction temperature and the amount of HO 2 generated Was observed. The result is shown in FIG. In the vicinity of 327 ° C., it is shown that the radical chain reaction proceeds. Incidentally, the solid line in FIG. 2a shows the correlation between the amount of HO 2 generated by the Pt catalyst and the reaction temperature.
[0011]
【The invention's effect】
As described above, the present invention makes it possible to use HO 2 , a radical that is stably supplied by the heated glass surface catalytic function, in the radical chain oxidation reaction of SO 2 , thereby reducing the use of chemical agents, In addition, the present invention has an excellent effect that an efficient oxidation process of SO 2 can be realized.
[Brief description of the drawings]
FIG. 1 shows an embodiment of the apparatus for SO 2 oxidation treatment by radical chain reaction of the present invention. FIG. 2 shows the reaction with the actual measurement value and the predicted value (solid line) of the amount of HO 2 radical produced by the catalytic activity of the borosilicate glass surface. Correlation between temperature correlation (b), predicted amount of HO 2 radical production by Pt catalyst and reaction temperature (a)
[Explanation of symbols]
Fu Combustion furnace (combustion boiler) B Blower H Flow reactor heater GR radical generator FR flow reactor EP Electric dust collector GT Treated gas St Exhaust gas stack

Claims (6)

内側表面温度が327±50℃維持された少なくとも内側表面がホウ珪酸ガラスにより形成されたフロー管または少なくとも表面がホウ珪酸ガラスにより形成されかつ該ガラス表面の温度が327±50℃に維持された部材を配設したフロー管にSOまたはSOおよびNOを含む被処理排気ガス、およびSOのラジカル酸化連鎖反応のトリガーとなるOHラジカルを生成するまたはHNO を導入してHOラジカルの生成反応を含む連鎖反応によりSOを酸化処理することを特徴とするSOを含む排気ガス処理方法。At least the inner surface is more formed flow tube or at least the surface of borosilicate glass is more formed on a borosilicate glass and the temperature of the glass surface 327 ± 50 ° C. inner surface temperature was maintained at 327 ± 50 ° C. H 2 O 2 or HNO 3 for generating an exhaust gas to be treated containing SO 2 or SO 2 and NO and OH radicals that trigger a radical oxidation chain reaction of SO 2 exhaust gas treatment method comprising SO 2, characterized in that introduced to oxidizing the SO 2 by chain reaction comprising the reaction of forming HO 2 radicals. フロー管へOHラジカルを生成させるH またはHNO の導入部に、更に貴金属を主成分とする触媒又は紫外線照射手段が配設されたH またはHNO の導入手段が設けられていることを特徴とする請求項1に記載のSOを含む排気ガス処理方法。 In the introduction of H 2 O 2 or HNO 3 to produce OH radicals to the flow tube, provided further means for introducing H 2 O 2 or HNO 3 to a catalyst or ultraviolet light irradiation means is arranged as a main component a precious metal The method for treating exhaust gas containing SO 2 according to claim 1. 排ガスが石炭燃焼により生成するものであることを特徴とする請求項1または2に記載のSOを含む排気ガス処理方法。The exhaust gas treatment method containing SO 2 according to claim 1 or 2, wherein the exhaust gas is generated by coal combustion. 該SOを含む排気ガス処理フロー管に該酸化連鎖反応におけるHOラジカルの生成を監視し制御する手段が設置されていることを特徴とする請求項1〜3のいずれかに記載のSOを含む排気ガス処理方法。The SO 2 according to any one of claims 1 to 3, wherein means for monitoring and controlling generation of HO 2 radicals in the oxidation chain reaction is installed in the exhaust gas treatment flow pipe containing the SO 2. An exhaust gas treatment method comprising: HOラジカルの生成の監視手段がNd:YAGレーザの2倍の高調波を用いることを特徴とする請求項4に記載のSOを含む排気ガス処理方法。5. The exhaust gas treatment method including SO 2 according to claim 4, wherein the HO 2 radical production monitoring means uses a harmonic twice as high as that of an Nd: YAG laser. フロー管の内面温度を327±50℃に維持する加熱手段を備えた少なくとも内面がホウ珪酸ガラスにより形成されたフロー管または少なくとも表面がホウ珪酸ガラスにより形成されかつ該ガラス表面の温度を327±50℃に維持する手段が設けられた部材を配設したフロー管、該フロー管にSOを含む排気ガスを導入する該ガスの予熱装置が設けられていてもよい排ガス導入部、該フロー管にSOの酸化連鎖反応のトリガーとなるOHラジカルを生成するまたはHNO を導入する手段が設けられた前記OHラジカル生成剤またはNで希釈した前記OHラジカル生成剤の導入手段および該フロー管中でのHOラジカルの生成を監視し制御する手段を少なくとも含むSOを含む排気ガスの処理設置。Temperature of at least the inner surface is more formed flow tube or at least the surface of borosilicate glass is more formed on a borosilicate glass and the glass surface with a heating means for maintaining the inner surface temperature of the flow tube 327 ± 50 ° C. A flow pipe provided with a member provided with a means for maintaining the temperature at 327 ± 50 ° C., and an exhaust gas introduction section that may be provided with a preheating device for introducing the exhaust gas containing SO 2 into the flow pipe, The OH radical generator or the OH radical generator diluted with N 2 provided with means for introducing H 2 O 2 or HNO 3 that generates OH radicals that trigger the SO 2 oxidation chain reaction into the flow tube processing installation of the introduction means and an exhaust gas containing at least containing SO 2 with means for monitoring and controlling the production of HO 2 radical in the flow tube.
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