JPH06343828A - Waste gas treatment - Google Patents

Waste gas treatment

Info

Publication number
JPH06343828A
JPH06343828A JP5163168A JP16316893A JPH06343828A JP H06343828 A JPH06343828 A JP H06343828A JP 5163168 A JP5163168 A JP 5163168A JP 16316893 A JP16316893 A JP 16316893A JP H06343828 A JPH06343828 A JP H06343828A
Authority
JP
Japan
Prior art keywords
exhaust gas
catalyst
oxide
bag filter
filter cloth
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP5163168A
Other languages
Japanese (ja)
Inventor
Masahiko Matsumoto
正彦 松本
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
JIYABISU KK
Original Assignee
JIYABISU KK
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by JIYABISU KK filed Critical JIYABISU KK
Priority to JP5163168A priority Critical patent/JPH06343828A/en
Publication of JPH06343828A publication Critical patent/JPH06343828A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To attain the improvement of dust collecting efficiency, the prevention of pressure loss and the improvement of economization, etc., to also attain a sufficient application to existing equipment, to efficiently remove nitrogen oxide from waste gas, and to also easily make a bag filter. CONSTITUTION:A reducing agent for nitrogen oxide and a reducing catalyst are injected from a reducing agent jetting device 4 and a reducing catalyst jetting device 5 to waste gas on the upstream side of a bag filter installed in a waste gas filter 6 to reduce the nitrogen oxide in the waste gas until the reducing catalyst reaches filter cloth of the bag filter, and the reducing catalyst is collected by the bag filter. The nitrogen oxide in the waste gas which has not been reduced before it reaches the filter cloth is reduced by the catalyst collected by the filter cloth and discharged in the air. Thus, nitrogen oxide is removed from waste gas by using filter cloth currently in use without a special treatment being newly made on the filter cloth.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、発電所のボイラ、都市
ごみ焼却炉、産業廃棄物焼却炉、製鉄焼結炉等から発生
し、酸性ガス、窒素酸化物、煤塵を含む排ガスを浄化処
理する排ガス処理方法に関する。
[Field of Industrial Application] The present invention purifies exhaust gas generated from a boiler of a power plant, an incinerator of municipal solid waste, an incinerator of industrial waste, a sinter of iron making, etc., containing acid gas, nitrogen oxides, and dust. Exhaust gas treatment method.

【0002】[0002]

【従来の技術】従来、この種の排ガスを浄化処理するに
は、例えば、図3ないし図5の系統図に示すような方法
が知られている。
2. Description of the Related Art Conventionally, in order to purify this kind of exhaust gas, for example, a method shown in the system diagrams of FIGS. 3 to 5 is known.

【0003】その一例について説明すると、図3に示す
ように、まず、焼却炉31から発生した高温の排ガスを
冷却装置32に導いて排ガス処理に適した温度まで冷却
する。次に、排ガスに酸性ガス吸収剤噴霧装置33から
酸性ガス吸収剤を噴霧し、排ガス中のHCl、SOX等
の酸性ガスを酸性ガス吸収剤に吸収させて除去する。次
に、排ガスを排ガス濾過装置34へ導き、そのバグフィ
ルタで排ガス中の煤塵を除去する。このようにして酸性
ガス、煤塵を除去してはいるが、窒素酸化物が無処理の
ままの排ガスを煙突、排風機等から成る排風装置35に
より大気中に排出する。
Explaining one example thereof, as shown in FIG. 3, first, high temperature exhaust gas generated from the incinerator 31 is guided to a cooling device 32 and cooled to a temperature suitable for exhaust gas treatment. Next, the acidic gas absorbent is sprayed from the acidic gas absorbent spraying device 33 to the exhaust gas, and the acidic gas such as HCl and SOX in the exhaust gas is absorbed by the acidic gas absorbent and removed. Next, the exhaust gas is guided to the exhaust gas filtering device 34, and the bag filter removes soot and dust from the exhaust gas. Although the acidic gas and the soot and dust are removed in this manner, the exhaust gas in which the nitrogen oxides have not been treated is exhausted to the atmosphere by the exhaust device 35 including a chimney, an exhaust fan, and the like.

【0004】従来の他の例としては、図4に示すよう
に、焼却炉31から発生した高温の排ガスに還元剤噴霧
装置36から窒素酸化物の還元剤を噴射し、高温還元を
行わせ、その後、図3に示す上記従来例と同様に、排ガ
ス中の酸性ガス除去、煤塵除去を行い、排風装置35に
より大気中に排出する。
As another conventional example, as shown in FIG. 4, a reducing agent of a nitrogen oxide is injected from a reducing agent spraying device 36 into a high temperature exhaust gas generated from an incinerator 31 to perform high temperature reduction, After that, as in the above-described conventional example shown in FIG. 3, the acidic gas in the exhaust gas and soot and dust are removed, and the air is exhausted to the atmosphere by the air exhaust device 35.

【0005】従来の更に他の例としては、図5に示すよ
うに、ガス冷却装置32により冷却した排ガスに酸性ガ
ス吸収剤噴霧装置33から酸性ガス吸収剤を噴霧して、
排ガス中の酸性ガスを除去し、続いて、排ガスを排ガス
濾過装置34へ導き、そのバグフィルタで排ガス中の煤
塵を除去し、更に、環境対策として、脱硝装置37を別
に設け、還元剤噴射装置36から還元剤を噴射した排ガ
スを脱硝装置37へ導いて排ガス中の窒素酸化物を除去
し、酸性ガス、煤塵、窒素酸化物を除去した排ガスを排
風装置35により大気中に排出する。
As another conventional example, as shown in FIG. 5, the exhaust gas cooled by the gas cooling device 32 is sprayed with an acidic gas absorbent from an acidic gas absorbent spraying device 33,
The acid gas in the exhaust gas is removed, then the exhaust gas is guided to the exhaust gas filtering device 34, the dust filter in the exhaust gas is removed by the bag filter, and a denitration device 37 is additionally provided as an environmental measure, and a reducing agent injection device is provided. The exhaust gas from which the reducing agent has been injected from 36 is guided to the denitration device 37 to remove nitrogen oxides in the exhaust gas, and the exhaust gas from which acid gas, soot dust and nitrogen oxides have been removed is exhausted to the atmosphere by the exhaust device 35.

【0006】しかしながら、図3の処理方法では、窒素
酸化物が無処理であるので、環境汚染の原因となる。ま
た、図4の処理方法では、ある程度の窒素酸化物を還元
除去することはできるが、触媒を用いていないため、除
去率が低く、依然として環境汚染の原因となる。図5に
示す処理方法は、環境汚染防止上、最も望ましいが、脱
硝装置37の建設費、維持費が高価となるばかりでな
く、広い用地を必要とするなどの問題がある。
However, in the treatment method of FIG. 3, no nitrogen oxide is treated, which causes environmental pollution. Further, in the treatment method of FIG. 4, nitrogen oxide can be reduced and removed to some extent, but since no catalyst is used, the removal rate is low, which still causes environmental pollution. The treatment method shown in FIG. 5 is the most desirable from the viewpoint of preventing environmental pollution, but there is a problem that not only the construction cost and maintenance cost of the denitration device 37 become expensive, but also a wide site is required.

【0007】上記のような従来の問題を解決するため、
特公平3−69570号公報、特開平1−293123
号公報等に記載されているように、最近、冷却した排ガ
スに酸性ガス吸収剤および窒素酸化物の還元剤を噴射
し、生成した反応物および残余の酸性ガス吸収剤を他の
煤塵と共に、還元触媒をあらかじめ担持させたバグフィ
ルタで捕集し、窒素酸化物を還元触媒に接触させて還元
剤により還元させるようにした排ガスの処理装置や処理
方法が提案されている。
In order to solve the above conventional problems,
Japanese Patent Publication No. 3-69570, Japanese Patent Laid-Open No. 1-293123.
Recently, as described in Japanese Patent Publication No. 1993-242, etc., an acidic gas absorbent and a reducing agent of nitrogen oxides are recently injected into cooled exhaust gas, and the produced reaction product and the residual acidic gas absorbent are reduced together with other soot dust. There has been proposed an exhaust gas treating apparatus and a treating method in which a catalyst is collected by a bag filter previously loaded, and nitrogen oxide is brought into contact with a reducing catalyst to be reduced by a reducing agent.

【0008】[0008]

【発明が解決しようとする課題】しかしながら、上記の
ような従来技術では、濾布に触媒を担持させるため、厚
手の濾布を用いる必要があり、この濾布を通過する排ガ
スの圧力損失は、通常の濾布の場合と比較し、著しく大
きくなる。また、濾布に触媒を担持させるには、触媒粉
末を混合した液に濾布を浸漬した後、濾布をその液から
引き上げて表面処理養生を行い、養生後の濾布を別の調
整液に浸漬し、乾燥工程を経て焼成する。その結果、触
媒は濾布にその目が詰まった状態で担持されるため、濾
布を通過する排ガスの圧力損失をより大きくしている。
しかも、一般に使用される濾布と比較して著しく高価と
なる。また、触媒は排ガスに長時間さらされると、排ガ
ス中の不純物により触媒活性が失われるが、上記のよう
に触媒は濾布に担持させ、新たに補給されることがない
ため、窒素酸化物の還元効率が次第に低下する。これを
防止するには、触媒を担持させたバグフィルタ全体を比
較的頻繁に交換しなければならず、経済的に不利である
ばかりでなく、その間、排ガス処理を行うことができな
いため、交換作業の時間的制約を受ける。また、濾布
は、ある時間使用すると、排ガス中の煤塵により表面を
覆われ、排ガスの圧力損失が大きくなるため、適宜、逆
洗を行う必要があるが、この逆洗時に濾布に担持されて
いる触媒が剥離、脱落し、窒素酸化物の還元効率が低下
する。更に、濾布に担持されている触媒は濾布が曲げら
れたり、こすられたりすると容易に脱落するため、バグ
フィルタを製作する際、相当な配慮が必要となり、製作
に手数を要するばかりでなく、高価になるなどの問題が
ある。
However, in the prior art as described above, it is necessary to use a thick filter cloth to support the catalyst on the filter cloth, and the pressure loss of the exhaust gas passing through this filter cloth is Compared with the case of ordinary filter cloth, it becomes significantly larger. Further, in order to support the catalyst on the filter cloth, after dipping the filter cloth in the liquid mixed with the catalyst powder, the filter cloth is pulled out from the solution to perform surface treatment curing, and the filter cloth after curing is adjusted with another adjusting liquid. It is dipped in, and dried and baked. As a result, the catalyst is carried on the filter cloth with its eyes closed, so that the pressure loss of the exhaust gas passing through the filter cloth is further increased.
Moreover, it is significantly more expensive than the commonly used filter cloth. Further, when the catalyst is exposed to exhaust gas for a long time, the catalytic activity is lost due to impurities in the exhaust gas, but as described above, the catalyst is supported on the filter cloth and is not newly replenished. The reduction efficiency gradually decreases. In order to prevent this, the entire bag filter carrying the catalyst must be replaced relatively often, which is not economically disadvantageous, and exhaust gas treatment cannot be performed during that time, so replacement work is not possible. Subject to time constraints. In addition, the filter cloth, when used for a certain period of time, has its surface covered with soot and dust in the exhaust gas and causes a large pressure loss of the exhaust gas, so it is necessary to perform backwashing as appropriate. The existing catalyst peels off and falls off, reducing the reduction efficiency of nitrogen oxides. Furthermore, the catalyst carried on the filter cloth easily falls off when the filter cloth is bent or rubbed, so considerable care must be taken when manufacturing the bag filter, and not only is it troublesome to manufacture. There are problems such as becoming expensive.

【0009】本発明は、上記のような従来の問題を解決
するものであり、バグフィルタを構成する濾布に集塵、
排ガスの圧力損失および価格のみを考慮して最適の材料
を選定することができ、しかも、通常のバグフィルタの
圧力損失を上回らないようにすることができ、したがっ
て、集塵効率の向上、圧力損失の防止、経済性の向上等
を図ることができるとともに、既設の設備にも充分適用
することができ、また、バグフィルタの頻繁な交換を要
することなく、触媒による窒素酸化物の還元効率を向上
させることができ、したがって、窒素酸化物を排ガス中
から効率良く除去することができ、更にはバグフィルタ
の製作時の取扱いが簡単となり、したがって、バグフィ
ルタを簡単に、かつ安価に製作することができるように
した排ガス処理方法を提供することを目的とするもので
ある。
The present invention solves the above-mentioned conventional problems, and collects dust on a filter cloth constituting a bag filter,
The optimum material can be selected only by considering the pressure loss of exhaust gas and the price, and moreover, the pressure loss of the ordinary bag filter can be prevented, thus improving the dust collection efficiency and pressure loss. Can be applied to existing equipment, and the efficiency of nitrogen oxide reduction by the catalyst can be improved without the need for frequent bag filter replacement. Therefore, the nitrogen oxides can be efficiently removed from the exhaust gas, and the bag filter can be easily handled during manufacturing. Therefore, the bag filter can be manufactured easily and at low cost. It is an object of the present invention to provide an exhaust gas treatment method made possible.

【0010】[0010]

【課題を解決するための手段】上記目的を達成するため
の本発明の技術的手段は、バグフィルタの上流側で排ガ
スに窒素酸化物の還元剤および窒素酸化物の還元触媒を
注入して排ガス中の窒素酸化物を還元し、上記還元触媒
を上記バグフィルタで捕集し、上記バグフィルタに到達
する以前に還元されなかった排ガス中の窒素酸化物を上
記バグフィルタにより捕集された触媒で還元させるよう
にしたものである。
The technical means of the present invention for achieving the above object is to inject a reducing agent for nitrogen oxides and a reducing catalyst for nitrogen oxides into the exhaust gas on the upstream side of the bag filter. Reduce the nitrogen oxides in the, the reducing catalyst is collected by the bag filter, the nitrogen oxides in the exhaust gas that was not reduced before reaching the bag filter is the catalyst collected by the bag filter. It is designed to be reduced.

【0011】そして、上記技術的手段において、アンモ
ニア等から成る窒素酸化物の還元剤をガス状態で排ガス
中に注入し、酸化バナジウム、酸化チタン、酸化タング
ステン、酸化クロム、酸化鉄、酸化銅、酸化マンガンの
一種以上から成る窒素酸化物の還元触媒を粉体、スラリ
ーのいずれかの状態で排ガス中に注入することができ
る。
In the above technical means, a reducing agent for nitrogen oxides such as ammonia is injected into the exhaust gas in a gas state, and vanadium oxide, titanium oxide, tungsten oxide, chromium oxide, iron oxide, copper oxide, oxide A nitrogen oxide reduction catalyst composed of one or more manganese can be injected into the exhaust gas in the form of powder or slurry.

【0012】[0012]

【作用】本発明によれば、バグフィルタの上流側で窒素
酸化物の還元剤および還元触媒を排ガス中に注入して窒
素酸化物を還元するようにし、バグフィルタを構成する
濾布に還元触媒をあらかじめ担持させないので、濾布
は、従来から使用されている機能を損うことなく、ま
た、新たな特殊な加工を施すことなく、集塵、排ガスの
圧力損失および価格のみを考慮して最適の材料を選定す
ることができ、しかも、通常のバグフィルタの圧力損失
を上回らないようにすることができる。また、常に新し
い還元触媒を補給して触媒活性を維持することができ、
しかも、還元触媒が排ガス中を浮遊している間に窒素酸
化物の還元反応を進行させることができるので、バグフ
ィルタの頻繁な交換を要することなく、還元触媒による
窒素酸化物の還元効率を向上させることができる。更
に、バグフィルタにあらかじめ還元触媒を担持させない
ので、製作時の取扱いが簡単となる。
According to the present invention, the reducing agent for nitrogen oxides and the reducing catalyst are injected into the exhaust gas on the upstream side of the bag filter to reduce the nitrogen oxides, and the reducing catalyst is provided on the filter cloth constituting the bag filter. Since the filter cloth is not carried in advance, the filter cloth is optimal considering only dust collection, pressure loss of exhaust gas and price without deteriorating the function conventionally used and without new special processing. The material can be selected, and the pressure loss of a normal bag filter can be prevented from exceeding. Moreover, it is possible to constantly replenish a new reducing catalyst to maintain the catalytic activity,
Moreover, since the reduction reaction of nitrogen oxides can proceed while the reduction catalyst is floating in the exhaust gas, the reduction efficiency of nitrogen oxides by the reduction catalyst can be improved without requiring frequent replacement of the bag filter. Can be made. Further, since the reducing catalyst is not previously loaded on the bag filter, the handling at the time of manufacture becomes easy.

【0013】[0013]

【実施例】以下、本発明の一実施例について図面を参照
しながら説明する。図1は本発明の一実施例における排
ガス処理方法を示す系統図、図2は同排ガス処理方法に
よる濾過方法を示す説明図である。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of the present invention will be described below with reference to the drawings. FIG. 1 is a system diagram showing an exhaust gas treatment method in one embodiment of the present invention, and FIG. 2 is an explanatory diagram showing a filtration method by the exhaust gas treatment method.

【0014】図1に示すように、まず、焼却炉1から発
生し、酸性ガス、窒素酸化物、煤塵を含む高温の排ガス
をガス冷却装置2へ導いて排ガス処理に適した温度まで
冷却する。
As shown in FIG. 1, first, high-temperature exhaust gas generated from the incinerator 1 and containing acid gas, nitrogen oxides, and soot is guided to a gas cooling device 2 and cooled to a temperature suitable for exhaust gas treatment.

【0015】次に、ガス冷却装置2からの排ガスに酸性
ガス吸収剤噴霧装置3から水酸化カルシウム、炭酸カル
シウム、酸化カルシウム、水酸化マグネシウム、炭酸マ
グネシウム、酸化マグネシウム等の酸性ガス吸収剤を噴
霧し、排ガス中のHCl、SOX等の酸性ガスを酸性ガ
ス吸収剤に吸収させて除去する。
Next, the exhaust gas from the gas cooling device 2 is sprayed with an acidic gas absorbent such as calcium hydroxide, calcium carbonate, calcium oxide, magnesium hydroxide, magnesium carbonate, magnesium oxide from the acidic gas absorbent spraying device 3. The acidic gas such as HCl and SOX in the exhaust gas is absorbed and removed by the acidic gas absorbent.

【0016】次に、酸性ガスが除去された窒素酸化物含
有排ガス中に還元剤噴射装置4および還元触媒噴射装置
5から窒素酸化物の還元剤および窒素酸化物の還元触媒
を順次噴射して注入する。還元剤としては、例えば、ア
ンモニアを用い、還元触媒としては、例えば、酸化バナ
ジウム、酸化チタン、酸化タングステン、酸化クロム、
酸化鉄、酸化銅、酸化マンガンを単体、若しくは選択混
合して用いる。このとき、還元剤はガス状態で排ガス中
に注入し、還元触媒は粉体、若しくはスラリーの状態で
排ガス中に注入する。この注入により還元触媒が排ガス
中で浮遊している間に排ガス中のNOX等の窒素酸化物
の一部を還元剤で還元しながら、排ガス濾過装置6へ導
く。この排ガス濾過装置6は図2に示すように、従来か
ら使用されているバグフィルタ8を備えている。
Next, a reducing agent injection device 4 and a reducing catalyst injection device 5 sequentially inject a reducing agent of nitrogen oxides and a reducing catalyst of nitrogen oxides into the nitrogen oxide-containing exhaust gas from which the acidic gas has been removed and inject them. To do. As the reducing agent, for example, ammonia is used, and as the reducing catalyst, for example, vanadium oxide, titanium oxide, tungsten oxide, chromium oxide,
Iron oxide, copper oxide, and manganese oxide are used alone or as a selective mixture. At this time, the reducing agent is injected into the exhaust gas in a gas state, and the reducing catalyst is injected into the exhaust gas in a powder or slurry state. By this injection, while the reducing catalyst is suspended in the exhaust gas, a part of nitrogen oxides such as NOX in the exhaust gas is reduced by the reducing agent and is guided to the exhaust gas filtering device 6. As shown in FIG. 2, the exhaust gas filtering device 6 includes a bag filter 8 which has been conventionally used.

【0017】そして、図2に示すように、排ガスG1は
バグフィルタ8の濾布9を通過する。このとき、排ガス
G1中の煤塵、酸性ガス吸収剤注入後に発成した酸性ガ
ス反応生成物、残余の酸性ガス吸収剤10および還元触
媒11を濾布9で捕集する。バグフィルタ8の上流側で
注入された還元剤、還元触媒により濾布9に到達する以
前に還元されなかった排ガスG1中の窒素酸化物は濾布
9に捕集された層を通過する際、その層の還元触媒11
に接触し、排ガスと共に到達した還元剤によって容易に
還元される。このようにして濾布9を通過した排ガスG
2は、酸性ガス、窒素酸化物、媒塵が除去されて浄化さ
れている。
Then, as shown in FIG. 2, the exhaust gas G1 passes through the filter cloth 9 of the bag filter 8. At this time, the dust in the exhaust gas G1, the acidic gas reaction product generated after the acidic gas absorbent is injected, the remaining acidic gas absorbent 10 and the reduction catalyst 11 are collected by the filter cloth 9. Nitrogen oxides in the exhaust gas G1 that have not been reduced before reaching the filter cloth 9 by the reducing agent and the reduction catalyst injected on the upstream side of the bag filter 8 pass through the layers collected by the filter cloth 9, Reduction catalyst 11 in that layer
And is easily reduced by the reducing agent that has reached with the exhaust gas. The exhaust gas G that has passed through the filter cloth 9 in this way
No. 2 is purified by removing acidic gas, nitrogen oxides and dust.

【0018】次に、浄化された排ガスを煙突、排風機等
から成る排風装置7により大気中に排出する。
Next, the purified exhaust gas is discharged into the atmosphere by an exhaust device 7 including a chimney, an exhaust fan and the like.

【0019】なお、還元触媒は酸性ガス吸収剤と共に排
ガス中に注入するようにしてもよい。このほか、本発明
は、その基本的技術思想を逸脱しない範囲で種々変更す
ることができる。
The reducing catalyst may be injected into the exhaust gas together with the acidic gas absorbent. In addition, the present invention can be variously modified without departing from the basic technical idea thereof.

【0020】[0020]

【発明の効果】以上説明したように本発明によれば、バ
グフィルタの上流側で窒素酸化物の還元剤および還元触
媒を排ガス中に注入して窒素酸化物を還元するように
し、バグフィルタを構成する濾布に還元触媒をあらかじ
め担持させないので、濾布は、従来から使用されている
機能を損うこともなく、また、新たな特殊な加工を施す
ことなく、集塵、排ガスの圧力損失および価格のみを考
慮して最適の材料を選定することができ、しかも、通常
のバグフィルタの圧力損失を上回らないようにすること
ができる。したがって、集塵効率の向上、圧力損失の防
止、経済性の向上等を図ることができるとともに、既設
の設備にも充分適用することができる。また、常に新し
い還元触媒を補給して触媒活性を維持することができ、
しかも、還元触媒が排ガス中を浮遊している間に窒素酸
化物の還元反応を進行させることができるので、バグフ
ィルタの頻繁な交換を要することなく、還元触媒による
窒素酸化物の還元効率を向上させることができる。した
がって、窒素酸化物を排ガス中から効率良く除去するこ
とができる。更に、バグフィルタにあらかじめ還元触媒
を担持させないので、製作時の取扱いが簡単となり、し
たがって、バグフィルタを簡単に、かつ安価に製作する
ことができる。
As described above, according to the present invention, a nitrogen oxide reducing agent and a reducing catalyst are injected into the exhaust gas on the upstream side of the bag filter to reduce the nitrogen oxides. The filter cloth does not have a reducing catalyst pre-loaded on it, so the filter cloth does not lose its conventional function and does not undergo new special processing. The optimum material can be selected by considering only the price and the price, and the pressure loss of the usual bag filter can be prevented from being exceeded. Therefore, the dust collection efficiency can be improved, the pressure loss can be prevented, the economical efficiency can be improved, and the present invention can be sufficiently applied to the existing equipment. Moreover, it is possible to constantly replenish a new reducing catalyst to maintain the catalytic activity,
Moreover, since the reduction reaction of nitrogen oxides can proceed while the reduction catalyst is floating in the exhaust gas, the reduction efficiency of nitrogen oxides by the reduction catalyst can be improved without requiring frequent replacement of the bag filter. Can be made. Therefore, nitrogen oxides can be efficiently removed from the exhaust gas. Further, since the bag filter does not carry the reduction catalyst in advance, the handling at the time of manufacture is simplified, and therefore the bag filter can be manufactured easily and at low cost.

【図面の簡単な説明】[Brief description of drawings]

【図1】本発明の一実施例における排ガス処理方法を示
す系統図
FIG. 1 is a system diagram showing an exhaust gas treatment method according to an embodiment of the present invention.

【図2】同排ガス処理方法により排ガス処理を行う際、
濾布に触媒等が捕集されて層状に形成された状態を示す
説明図
[Fig. 2] When performing exhaust gas treatment by the same exhaust gas treatment method,
Explanatory drawing showing a state in which a catalyst or the like is collected on a filter cloth and formed into a layer

【図3】従来の排ガス処理方法の一例を示す系統図FIG. 3 is a system diagram showing an example of a conventional exhaust gas treatment method.

【図4】従来の排ガス処理方法の他の例を示す系統図FIG. 4 is a system diagram showing another example of a conventional exhaust gas treatment method.

【図5】従来の排ガス処理方法の更に他の例を示す系統
FIG. 5 is a system diagram showing still another example of a conventional exhaust gas treatment method.

【符号の説明】[Explanation of symbols]

1 焼却炉 2 ガス冷却装置 3 酸性ガス吸収噴霧装置 4 還元剤噴射装置 5 還元触媒噴射装置 6 排ガス濾過装置 7 排風装置 8 バグフィルタ 9 濾布 10 酸性ガス吸収剤等 11 還元触媒 1 Incinerator 2 Gas Cooling Device 3 Acid Gas Absorption Spraying Device 4 Reducing Agent Injection Device 5 Reduction Catalyst Injection Device 6 Exhaust Gas Filtration Device 7 Exhaust Air Device 8 Bag Filter 9 Filter Cloth 10 Acid Gas Absorbent etc. 11 Reduction Catalyst

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 バグフィルタの上流側で排ガスに窒素酸
化物の還元剤および窒素酸化物の還元触媒を注入して排
ガス中の窒素酸化物を還元し、上記還元触媒を上記バグ
フィルタで捕集し、上記バグフィルタに到達する以前に
還元されなかった排ガス中の窒素酸化物を上記バグフィ
ルタにより捕集された触媒で還元させることを特徴とす
る排ガス処理方法。
1. A nitrogen oxide reducing agent and a nitrogen oxide reduction catalyst are injected into the exhaust gas on the upstream side of the bag filter to reduce the nitrogen oxide in the exhaust gas, and the reduction catalyst is collected by the bag filter. The exhaust gas treatment method is characterized in that the nitrogen oxides in the exhaust gas that have not been reduced before reaching the bag filter are reduced by the catalyst collected by the bag filter.
【請求項2】 アンモニア等から成る窒素酸化物の還元
剤をガス状態で排ガス中に注入し、酸化バナジウム、酸
化チタン、酸化タングステン、酸化クロム、酸化鉄、酸
化銅、酸化マンガンの一種以上から成る窒素酸化物の還
元触媒を粉体、スラリーのいずれかの状態で排ガス中に
注入する請求項1記載の排ガス処理方法。
2. A nitrogen oxide reducing agent comprising ammonia or the like is injected into an exhaust gas in a gas state to comprise one or more of vanadium oxide, titanium oxide, tungsten oxide, chromium oxide, iron oxide, copper oxide and manganese oxide. The exhaust gas treatment method according to claim 1, wherein the reduction catalyst for nitrogen oxides is injected into the exhaust gas in a powder or slurry state.
JP5163168A 1993-06-07 1993-06-07 Waste gas treatment Pending JPH06343828A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5163168A JPH06343828A (en) 1993-06-07 1993-06-07 Waste gas treatment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5163168A JPH06343828A (en) 1993-06-07 1993-06-07 Waste gas treatment

Publications (1)

Publication Number Publication Date
JPH06343828A true JPH06343828A (en) 1994-12-20

Family

ID=15768535

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5163168A Pending JPH06343828A (en) 1993-06-07 1993-06-07 Waste gas treatment

Country Status (1)

Country Link
JP (1) JPH06343828A (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100650110B1 (en) * 1999-07-09 2006-11-24 토다 고교 가부시끼가이샤 Process for treating dioxin-containing exhaust gas and composite catalyst composition for inhibiting generation of dioxin
GB2442444A (en) * 2006-10-06 2008-04-09 Howard Paul Davis A process for catalytically removing NOx from a gas stream
JP2011161330A (en) * 2010-02-05 2011-08-25 Nippon Steel Corp Apparatus for denitrifying exhaust
CN104190193A (en) * 2014-08-22 2014-12-10 合肥工业大学 Method for performing synchronous desulfurization, denitrification and dust removal in bag type dust collector
CN104492189A (en) * 2014-11-30 2015-04-08 成都易态科技有限公司 Integrated dust removal-denitration treatment method for industrial furnace gas and special device for integrated treatment method
CN111530477A (en) * 2020-05-18 2020-08-14 中国科学院兰州化学物理研究所 Manganese-based ultralow-temperature denitration catalyst powder and preparation method thereof

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH01159034A (en) * 1987-12-16 1989-06-22 Mitsubishi Heavy Ind Ltd Denitration of exhaust gas from diesel engine

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH01159034A (en) * 1987-12-16 1989-06-22 Mitsubishi Heavy Ind Ltd Denitration of exhaust gas from diesel engine

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100650110B1 (en) * 1999-07-09 2006-11-24 토다 고교 가부시끼가이샤 Process for treating dioxin-containing exhaust gas and composite catalyst composition for inhibiting generation of dioxin
GB2442444A (en) * 2006-10-06 2008-04-09 Howard Paul Davis A process for catalytically removing NOx from a gas stream
JP2011161330A (en) * 2010-02-05 2011-08-25 Nippon Steel Corp Apparatus for denitrifying exhaust
CN104190193A (en) * 2014-08-22 2014-12-10 合肥工业大学 Method for performing synchronous desulfurization, denitrification and dust removal in bag type dust collector
CN104190193B (en) * 2014-08-22 2015-11-18 合肥工业大学 A kind of method of sack cleaner inter-sync desulfur denitrate dust collecting
CN104492189A (en) * 2014-11-30 2015-04-08 成都易态科技有限公司 Integrated dust removal-denitration treatment method for industrial furnace gas and special device for integrated treatment method
CN111530477A (en) * 2020-05-18 2020-08-14 中国科学院兰州化学物理研究所 Manganese-based ultralow-temperature denitration catalyst powder and preparation method thereof
CN111530477B (en) * 2020-05-18 2023-02-28 中国科学院兰州化学物理研究所 Manganese-based ultralow-temperature denitration catalyst powder and preparation method thereof

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