JPH10238741A - Catalytic combustion type thermal storage exhaust gas treating apparatus - Google Patents
Catalytic combustion type thermal storage exhaust gas treating apparatusInfo
- Publication number
- JPH10238741A JPH10238741A JP9043769A JP4376997A JPH10238741A JP H10238741 A JPH10238741 A JP H10238741A JP 9043769 A JP9043769 A JP 9043769A JP 4376997 A JP4376997 A JP 4376997A JP H10238741 A JPH10238741 A JP H10238741A
- Authority
- JP
- Japan
- Prior art keywords
- exhaust gas
- catalyst
- heat storage
- heating chamber
- untreated
- 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
Links
Landscapes
- Chimneys And Flues (AREA)
- Incineration Of Waste (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Catalysts (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、排ガス中に含まれ
る可燃性有害成分や可燃性悪臭成分を触媒の存在下にお
いて酸化燃焼又は熱分解させて無害無臭な物質に変化さ
せて浄化処理すると共に、その際に生ずる熱を回収して
再利用する触媒燃焼式蓄熱排ガス処理装置に関する。[0001] The present invention relates to a purifying treatment by converting flammable harmful components and flammable odor components contained in exhaust gas into harmless and odorless substances by oxidizing and burning or thermally decomposing them in the presence of a catalyst. The present invention relates to a catalytic combustion type heat storage exhaust gas treatment apparatus for recovering and reusing heat generated at that time.
【0002】[0002]
【従来の技術】塗装ブース,塗装乾燥炉,印刷用乾燥
炉,プラスチックや合板の製造設備,食品加工設備,産
業廃棄物処理設備あるいは香料製造設備などの各種施設
内においては、塗料,インキ,溶剤,接着剤,合成樹脂
あるいは化学薬品等から、アルコール類,エステル類
や,有害で特有の臭気を持つフェノール類,アルデヒド
類等の可燃性有害悪臭成分が発生する。2. Description of the Related Art In various facilities such as a coating booth, a coating drying oven, a printing drying oven, a plastic or plywood manufacturing facility, a food processing facility, an industrial waste treatment facility, or a fragrance manufacturing facility, paint, ink, and solvent are used. Combustible harmful odor components such as alcohols, esters, phenols and aldehydes having harmful and peculiar odors are generated from adhesives, adhesives, synthetic resins or chemicals.
【0003】 このような有害悪臭成分を含んだ排ガス
は、公害防止の観点から直接大気中に放出することはで
きないので、通常は、浄化処理を施して、無害無臭化し
た状態で放出している。代表的な浄化処理方法として
は、排ガス中の有害悪臭成分を700〜900℃の高温
下で酸化燃焼又は熱分解して炭酸ガスと水に変化させて
無害無臭化する直接燃焼法が知られている。これは、浄
化処理効果が他の処理法と比較しても劣らず、また、可
燃性の有害悪臭成分に対しては全般的に適用できるとい
う長所があるが、その反面、燃料消費量が大であり、燃
費が嵩むことによりランニングコストが嵩むという短所
がある。[0003] Since exhaust gas containing such harmful odor components cannot be directly released into the atmosphere from the viewpoint of pollution prevention, it is usually subjected to a purification treatment and released in a harmless and odorless state. . As a typical purification treatment method, there is known a direct combustion method in which harmful odor components in exhaust gas are oxidized and burned or thermally decomposed at a high temperature of 700 to 900 ° C. to change into carbon dioxide and water to make them harmless and odorless. I have. This has the advantage that the purification effect is not inferior to other treatment methods and that it can be applied to combustible odorous odor components in general, but on the other hand, fuel consumption is large. However, there is a disadvantage that running cost is increased due to increased fuel efficiency.
【0004】 そこで、燃費を抑えてランニングコスト
を軽減させるために、排ガス中に含まれる可燃性有害悪
臭成分を触媒の存在下で酸化燃焼又は熱分解させる触媒
燃焼法が提案されている。これは、白金系,コバルト
系,ニッケル系などの触媒の存在下において酸化燃焼又
は熱分解反応を進行させ、可燃性有害悪臭成分を炭酸ガ
スと水とに分解させて無害無臭化する方法であり、直接
燃焼法に比較して低温の300〜450℃程度で浄化処
理することができるので、ランニングコストを軽減でき
るというメリットがある。また最近では、触媒存在下で
酸化燃焼又は熱分解させて浄化処理した高温の処理済排
ガスの熱を有効に利用して、さらにランニングコストを
軽減する触媒燃焼式蓄熱排ガス処理装置が提案されてい
る(特開平5−66005号公報参照)。[0004] Therefore, in order to suppress fuel consumption and reduce running costs, there has been proposed a catalytic combustion method in which flammable harmful odor components contained in exhaust gas are oxidized and burned or thermally decomposed in the presence of a catalyst. This is a method in which oxidizing combustion or thermal decomposition reaction proceeds in the presence of a platinum-based, cobalt-based, nickel-based catalyst, etc. to decompose combustible harmful odorous components into carbon dioxide gas and water to make them harmless and odorless. Since the purification treatment can be performed at a low temperature of about 300 to 450 ° C. as compared with the direct combustion method, there is an advantage that running costs can be reduced. Further, recently, a catalytic combustion type thermal storage exhaust gas treatment apparatus has been proposed in which the running cost is further reduced by effectively utilizing the heat of high-temperature treated exhaust gas purified by oxidative combustion or thermal decomposition in the presence of a catalyst. (See JP-A-5-66005).
【0005】 図2は、このような方式の排ガス処理装
置1を示し、未処理排ガスを所定の温度まで加熱するガ
スバーナなどの加熱装置2を備えた排ガス加熱室3に対
して複数の蓄熱室5A〜5Cが並設され、当該蓄熱室5
A〜5C内には、高温の処理済排ガスを排出させる際に
その熱を回収し、低温の未処理排ガスを導入する際に予
め回収した熱で当該排ガスを予熱する蓄熱層4が配設さ
れている。そして、前記排ガス加熱室3と各蓄熱室5A
〜5Cを連通する夫々の開口部6には、前記排ガス加熱
室3で加熱された排ガス中の可燃性有害悪臭成分を酸化
燃焼又は熱分解して無害無臭の物質に変化させる白金
系,コバルト系,ニッケル系などの触媒で形成される触
媒層7A〜7Cが形成されている。前記各蓄熱室5A〜
5Cには、蓄熱層4を挟んで排ガス加熱室3の反対側
に、排ガス加熱室3に未処理排ガスを導入する未処理排
ガス導入ダクト8A〜8Cと、排ガス加熱室3で加熱さ
れ触媒層7A〜7Cを通過して浄化処理された処理済排
ガスを外部に排出する処理済排ガス排出ダクト9A〜9
Cと、排ガス加熱室3から導入される少量の加熱排ガス
で各蓄熱室5A〜5C内に残る未処理排ガスを排出させ
て導入側の蓄熱室5A〜5Cに還流させるパージダクト
10A〜10Cが接続されている。FIG. 2 shows an exhaust gas treatment apparatus 1 of this type, in which a plurality of heat storage chambers 5 A are provided for an exhaust gas heating chamber 3 provided with a heating device 2 such as a gas burner for heating untreated exhaust gas to a predetermined temperature. To 5C, and the heat storage chamber 5
A to 5C are provided with a heat storage layer 4 for recovering heat when discharging the high-temperature treated exhaust gas and preheating the exhaust gas with the previously recovered heat when introducing the low-temperature untreated exhaust gas. ing. The exhaust gas heating chamber 3 and each heat storage chamber 5A
Pt-based and cobalt-based materials that oxidize, burn, or thermally decompose flammable harmful odor components in the exhaust gas heated in the exhaust gas heating chamber 3 to convert them into harmless and odorless materials. And catalyst layers 7A to 7C formed of a nickel-based catalyst or the like. Each of the heat storage chambers 5A-
5C, untreated exhaust gas introduction ducts 8A to 8C for introducing untreated exhaust gas into the exhaust gas heating chamber 3 on the opposite side of the exhaust gas heating chamber 3 across the heat storage layer 4, and a catalyst layer 7A heated in the exhaust gas heating chamber 3 Exhaust gas exhaust ducts 9A to 9C for exhausting the purified exhaust gas that has been purified by passing through the exhaust gases 9A to 9C
And purge ducts 10A to 10C for discharging untreated exhaust gas remaining in each of the heat storage chambers 5A to 5C with a small amount of heated exhaust gas introduced from the exhaust gas heating chamber 3 and returning the exhaust gas to the heat storage chambers 5A to 5C on the introduction side. ing.
【0006】 そして、前記各ダクト8A〜8C,9A
〜9C,10A〜10Cには、オートダンパ11A〜1
1C,12A〜12C,13A〜13Cが介装され、こ
れらを所定のタイミングで導通/遮断させて、排ガスの
導入側及び排出側を交互に切り換える。これにより、一
の蓄熱室5A〜5Cから導入した未処理排ガスを、排ガ
ス加熱室3で加熱した後、触媒層7A〜7Cに通して浄
化処理を行い、処理済排ガスを他の蓄熱室5A〜5Cか
ら処理済排ガスを排出させると共に、排ガスの導入側及
び排出側を交互に切り換えて連続的に浄化処理するよう
に成されている。[0006] Each of the ducts 8A to 8C, 9A
~ 9C, 10A ~ 10C have auto dampers 11A ~ 1
1C, 12A to 12C, and 13A to 13C are interposed, and these are turned on / off at a predetermined timing to alternately switch the introduction side and the discharge side of the exhaust gas. Thereby, after the untreated exhaust gas introduced from one of the heat storage chambers 5A to 5C is heated in the exhaust gas heating chamber 3, the purification treatment is performed through the catalyst layers 7A to 7C, and the treated exhaust gas is converted into the other heat storage chambers 5A to 5C. The exhaust gas is discharged from 5C, and the purification side is continuously performed by alternately switching the introduction side and the exhaust side of the exhaust gas.
【0007】 具体的には、まず、オートダンパ11
A,12B,13Cを開き、それ以外のオートダンパを
閉じておく。この場合、未処理排ガスは導入側の蓄熱室
5Aを通って排ガス加熱室3に導入され、所定の処理温
度(例えば300〜450℃)に加熱された後、触媒層
7Bを通過する際に浄化処理される。そして、高温の処
理済排ガスの熱を蓄熱室5Bの蓄熱層4で回収した後、
処理済排ガスを排出ダクト9Bから外部へ排出する。ま
た、このとき、排ガス加熱室3で加熱された高温排ガス
の一部が蓄熱室5Cに残る未処理排ガスを押し出してパ
ージし、その未処理排ガスがパージダクト10Cを通っ
て導入側の蓄熱室5Aに還流される。Specifically, first, the auto damper 11
A, 12B and 13C are opened, and the other auto dampers are closed. In this case, the untreated exhaust gas is introduced into the exhaust gas heating chamber 3 through the heat storage chamber 5A on the introduction side, is heated to a predetermined processing temperature (for example, 300 to 450 ° C.), and is purified when passing through the catalyst layer 7B. It is processed. Then, after collecting the heat of the high-temperature treated exhaust gas in the heat storage layer 4 of the heat storage chamber 5B,
The treated exhaust gas is discharged from the discharge duct 9B to the outside. At this time, a part of the high-temperature exhaust gas heated in the exhaust gas heating chamber 3 pushes out and purifies the untreated exhaust gas remaining in the heat storage chamber 5C, and the untreated exhaust gas passes through the purge duct 10C to the introduction-side heat storage chamber 5A. It is refluxed.
【0008】 そして、例えば60秒経過したときに、
オートダンパ11B,12C,13Aを開き、それ以外
のオートダンパを閉じる。この場合、蓄熱の終了した蓄
熱室5Bから未処理排ガスを導入し、パージが終了した
蓄熱室5Cから処理済排ガスを排出させると共に、内部
に未処理ガスの残る蓄熱室5Aのパージを行う。さらに
60秒経過したときに、オートダンパ11C,12A,
13Bを開き、それ以外のオートダンパを閉じる。この
場合、蓄熱室5Cから未処理排ガスを導入させ、蓄熱室
5Aから処理済排ガス外部に排出させ、蓄熱室5Bのパ
ージを行う。Then, for example, when 60 seconds have elapsed,
The automatic dampers 11B, 12C and 13A are opened, and the other automatic dampers are closed. In this case, the untreated exhaust gas is introduced from the heat storage chamber 5B where the heat storage has been completed, the treated exhaust gas is discharged from the heat storage chamber 5C where the purging has been completed, and the heat storage chamber 5A in which the unprocessed gas remains remains purged. When a further 60 seconds have elapsed, the automatic dampers 11C, 12A,
13B is opened, and the other auto dampers are closed. In this case, the untreated exhaust gas is introduced from the heat storage chamber 5C, discharged to the outside of the treated exhaust gas from the heat storage chamber 5A, and the heat storage chamber 5B is purged.
【0009】 そして、さらに60秒経過したときに、
再びオートダンパ11A,12B,13Cを開き、それ
以外のオートダンパを閉じて、これを繰り返すことによ
り、排ガスの導入側と排出側を交互に切り換えて連続的
に排ガスの浄化処理を行う。Then, when another 60 seconds have passed,
The automatic dampers 11A, 12B, and 13C are opened again, the other automatic dampers are closed, and this is repeated, whereby the exhaust gas purifying process is continuously performed by alternately switching the exhaust gas introduction side and the exhaust side.
【0010】[0010]
【発明が解決しようとする課題】ところで、このような
触媒燃焼式蓄熱排ガス処理装置を塗装乾燥炉の排ガス処
理装置として使用した場合に、従来2〜3年の寿命があ
った触媒層7A〜7Cの寿命が短くなり、排ガス条件に
よっては数カ月と著しく短くなるという問題を生じた。
特に、この種の触媒は、活性アルミナをコーティングし
たハニカム状の触媒担体に、触媒性能の優れた白金を担
持させた高価なものを用いることが多いため、触媒寿命
が短くなると、触媒の交換に要する費用が嵩む。そし
て、本発明者らがその原因を調べたところ、塗膜の硬質
化や酸性雨対策として塗料に混入されているシロキサン
等に含まれるシリカ成分が蒸発し、特に、シロキサンが
大量に含まれた塗料を塗装する場合には大量のシリカが
排出され、そのシリカ成分が触媒毒として作用し、触媒
の表面に無機質の皮膜を形成するために、触媒の活性が
失われていることが判明した。また、このようなシリカ
に限らず、排ガス中に、塩素などのハロゲン元素,鉛,
亜鉛,ヒ素,水銀,リン,イオウなどの触媒毒が含まれ
ている場合には、同様に触媒が被毒されてその寿命が縮
まるという問題がある。By the way, when such a catalytic combustion type heat storage exhaust gas treatment apparatus is used as an exhaust gas treatment apparatus for a coating and drying furnace, the catalyst layers 7A to 7C having a life of 2 to 3 years conventionally. Has a problem in that the service life is shortened, and depending on exhaust gas conditions, it is significantly shortened to several months.
In particular, since this type of catalyst often uses an expensive catalyst in which platinum having excellent catalytic performance is supported on a honeycomb-shaped catalyst carrier coated with activated alumina, if the catalyst life is shortened, replacement of the catalyst is required. Costs increase. When the present inventors investigated the cause, the silica component contained in the siloxane and the like mixed in the paint as a measure for hardening the coating film and acid rain was evaporated, and in particular, a large amount of the siloxane was contained. When applying the paint, a large amount of silica was discharged, and it was found that the activity of the catalyst was lost because the silica component acted as a catalyst poison and formed an inorganic film on the surface of the catalyst. Not only silica but also halogens such as chlorine, lead,
When a catalyst poison such as zinc, arsenic, mercury, phosphorus, and sulfur is contained, the catalyst is similarly poisoned and has a problem of shortening its life.
【0011】 そこで、本発明は未処理排ガスにそのよ
うな触媒毒となる物質が含まれている場合であっても、
触媒の被毒を低減して、触媒寿命を延ばすことを技術的
課題としている。[0011] Therefore, the present invention is applicable to a case where the untreated exhaust gas contains such a catalyst poisonous substance.
The technical task is to reduce catalyst poisoning and extend the life of the catalyst.
【0012】[0012]
【課題を解決するための手段】この課題を解決するため
に、本発明は、高温の処理済排ガスを排出させる際にそ
の熱を回収し、低温の未処理排ガスを導入する際に当該
排ガスを予熱する蓄熱層を有する複数の蓄熱室が、未処
理排ガスを所定の温度まで加熱する加熱装置を備えた排
ガス加熱室に対して並設され、前記排ガス加熱室と各蓄
熱層の間には未処理排ガス中に含まれる可燃性成分を酸
化燃焼又は熱分解させて浄化処理する触媒層が形成され
て成り、一の蓄熱室から導入された未処理排ガスを前記
排ガス加熱室及び前記触媒層で浄化処理した後、その処
理済排ガスを他の蓄熱室から排出すると共に、排ガスの
導入側及び排出側を順次交互に切り換えて連続的に処理
を行う触媒燃焼式蓄熱排ガス処理装置において、排ガス
中に含まれる触媒毒を吸着する触媒毒吸着フィルタが、
前記各触媒層の蓄熱室側及び排ガス加熱室側のいずれか
一方又は双方に交換可能に装着されると共に、当該触媒
毒吸着フィルタが担体に活性アルミナをコーティングし
て形成され、又は、活性アルミナをコーティングした担
体にアルカリ金属又はアルカリ土類金属を担持させて形
成されたことを特徴とする。SUMMARY OF THE INVENTION In order to solve this problem, the present invention recovers heat when discharging a high-temperature treated exhaust gas, and removes the heat when introducing a low-temperature untreated exhaust gas. A plurality of heat storage chambers having a heat storage layer for preheating are arranged in parallel with an exhaust gas heating chamber provided with a heating device for heating the untreated exhaust gas to a predetermined temperature, and there is no unheated gas between the exhaust gas heating chamber and each heat storage layer. A catalyst layer for purifying by oxidizing, burning or thermally decomposing combustible components contained in the treated exhaust gas is formed, and the untreated exhaust gas introduced from one heat storage chamber is purified by the exhaust gas heating chamber and the catalyst layer. After the treatment, the treated exhaust gas is discharged from other heat storage chambers, and the exhaust gas is contained in the exhaust gas in a catalytic combustion type heat storage exhaust gas treatment device that continuously switches the exhaust gas introduction side and discharge side sequentially and continuously performs the treatment. Catalyst Catalyst poisons adsorption filter for adsorbing found
Attached to one or both of the heat storage chamber side and the exhaust gas heating chamber side of each of the catalyst layers, and the catalyst poison adsorption filter is formed by coating the carrier with activated alumina, or It is characterized by being formed by supporting an alkali metal or an alkaline earth metal on a coated carrier.
【0013】 本発明によれば、触媒層の蓄熱室側に触
媒毒吸着フィルタが配設されている場合は、蓄熱室から
導入される未処理排ガスが、蓄熱層を通過して所定の温
度まで予熱されて触媒毒吸着フィルタを通過して触媒層
に至る。したがって、蓄熱層を通過して所定温度に予熱
されたときに吸着温度に達する触媒毒が効率よく吸着さ
れる。また、触媒層の排ガス加熱室側に触媒毒吸着フィ
ルタが配設されている場合は、排ガス加熱室で高温に加
熱された未処理排ガスが、触媒毒吸着フィルタを通過し
て触媒層に至る。したがって、高温に加熱されて触媒毒
となる物質に変化したものや、その温度で吸着しやすい
触媒毒が、その触媒毒吸着フィルタで捕捉される。According to the present invention, when the catalyst poison adsorption filter is provided on the heat storage chamber side of the catalyst layer, untreated exhaust gas introduced from the heat storage chamber passes through the heat storage layer to a predetermined temperature. It is preheated and passes through the catalyst poison adsorption filter to reach the catalyst layer. Therefore, the catalyst poison which reaches the adsorption temperature when it is preheated to a predetermined temperature through the heat storage layer is efficiently adsorbed. When a catalyst poison adsorption filter is provided on the exhaust gas heating chamber side of the catalyst layer, the untreated exhaust gas heated to a high temperature in the exhaust gas heating chamber passes through the catalyst poison adsorption filter and reaches the catalyst layer. Therefore, a substance that has been heated to a high temperature and changed to a substance that becomes a catalyst poison or a catalyst poison that is easily adsorbed at that temperature is captured by the catalyst poison adsorption filter.
【0014】 そして、触媒毒吸着フィルタは、担体に
γ−アルミナなどの活性アルミナをコーティングして形
成されているので、その表面積が極めて大きくなり、触
媒毒となる物質の吸着効率が非常に高い。また、活性ア
ルミナは、酸性物質に対してはアルカリ性を示し、塩基
性(アルカリ性)物質に対しては酸性を示す両性を有す
るので、いずれの性質を示す触媒毒に対してもこれを中
和させて吸着する。したがって、排ガス中に触媒毒とし
て酸性を示すもの及びアルカリ性を示すもののどちらが
含まれていても、これらを効率良く吸着して、触媒被毒
を防止し、触媒寿命を延ばすことができる。Since the catalyst poison adsorption filter is formed by coating the carrier with activated alumina such as γ-alumina, the surface area thereof is extremely large, and the efficiency of adsorbing the catalyst poison is extremely high. Activated alumina has both amphoteric properties, indicating alkalinity for acidic substances and acidity for basic (alkaline) substances. Therefore, it neutralizes catalyst poisons of any properties. To adsorb. Therefore, regardless of whether the exhaust gas contains acidic or alkaline catalyst poisons, these can be efficiently adsorbed to prevent catalyst poisoning and extend the catalyst life.
【0015】 また、触媒毒吸着フィルタとして、活性
アルミナをコーティングした担体にアルカリ金属又はア
ルカリ土類金属を担持させれば、当該アルカリ金属又は
アルカリ土類金属が活性アルミナにより多少中和される
ことを考慮しても触媒毒吸着フィルタの表面は強いアル
カリ性を示す。したがって、排ガス中に強い酸性を示す
シリカが大量に含まれている場合であっても、シリカは
アルカリ性の触媒毒吸着フィルタに吸着されて中和され
ることとなり、シリカによる触媒被毒をより効果的に低
減することができる。Further, as a catalyst poison adsorption filter, if an alkali metal or an alkaline earth metal is supported on a carrier coated with activated alumina, the alkali metal or alkaline earth metal is neutralized to some extent by the activated alumina. Even if the consideration is taken, the surface of the catalyst poison adsorption filter shows strong alkalinity. Therefore, even when a large amount of strongly acidic silica is contained in the exhaust gas, the silica is adsorbed by the alkaline catalyst poison adsorption filter and neutralized, and the catalyst poisoning by silica is more effectively performed. Can be effectively reduced.
【0016】 このように、排ガス中に含まれている触
媒毒は、排ガスが触媒層を通過する前に、その蓄熱室側
又は排ガス加熱室側に配設された触媒毒吸着フィルタに
吸着されるため、その分触媒層の被毒が低減されて触媒
層の寿命が長くなる。また、触媒毒吸着フィルタには白
金などの高価な貴金属が使用されていないので触媒層よ
り安価であり、したがって、これを頻繁に交換しても、
触媒層を交換する場合に比してコストが低減される。As described above, before the exhaust gas passes through the catalyst layer, the catalyst poison contained in the exhaust gas is adsorbed by the catalyst poison adsorption filter disposed on the heat storage chamber side or the exhaust gas heating chamber side. Therefore, the poisoning of the catalyst layer is reduced correspondingly, and the life of the catalyst layer is prolonged. Also, since the catalyst poison adsorption filter does not use expensive noble metals such as platinum, it is cheaper than the catalyst layer, and therefore, even if this is frequently replaced,
The cost is reduced as compared with the case where the catalyst layer is replaced.
【0017】[0017]
【発明の実施の形態】以下、本発明の実施の形態を図面
に基づいて具体的に説明する。図1は本発明に係る触媒
燃焼式蓄熱排ガス処理装置を示す概略構成図である。な
お、図2と重複する部分については同一符号を付して詳
細説明は省略する。Embodiments of the present invention will be specifically described below with reference to the drawings. FIG. 1 is a schematic configuration diagram showing a catalytic combustion type heat storage exhaust gas treatment apparatus according to the present invention. 2 are given the same reference numerals and the detailed description is omitted.
【0018】 本例の触媒燃焼式蓄熱排ガス処理装置1
は、各触媒層7A〜7Cの蓄熱室5A〜5C側又は排ガ
ス加熱室3側に、排ガス中に含まれる触媒毒を吸着する
触媒毒吸着フィルタ20,21が交換可能に装着されて
いる。触媒層7A〜7Cは、例えば活性アルミナやシリ
カ等から成るペレット型又はサドル型の触媒担体に触媒
となる白金,パラジウム合金,コバルト,ニッケル等の
貴金属を担持させたものや、コージエライト磁器で形成
されたハニカム状の触媒担体に、γ−アルミナ等の活性
アルミナをコーティングして、その上に、触媒となる白
金,パラジウム合金,コバルト,ニッケル等の貴金属を
担持させたものを用いている。[0018] Catalytic combustion type heat storage exhaust gas treatment apparatus 1 of the present embodiment
The catalyst poison adsorption filters 20 and 21 for adsorbing catalyst poisons contained in the exhaust gas are exchangeably mounted on the heat storage chambers 5A to 5C side or the exhaust gas heating chamber 3 side of each of the catalyst layers 7A to 7C. The catalyst layers 7A to 7C are formed by, for example, a pellet-type or saddle-type catalyst carrier made of activated alumina, silica, or the like, on which a noble metal such as platinum, palladium alloy, cobalt, or nickel as a catalyst is supported, or cordierite porcelain. The honeycomb-shaped catalyst carrier is coated with activated alumina such as γ-alumina, on which a noble metal such as platinum, palladium alloy, cobalt, nickel or the like as a catalyst is supported.
【0019】 また、前記触媒毒吸着フィルタ20,2
1は、例えばコージエライト磁器やステンレスで形成さ
れたハニカム状の担体にγ−アルミナ等の活性アルミナ
をコーティングし、さらにその上に、リチウムLi,ナ
トリウムNa,カリウムK,セシウムCsなどのアルカ
リ金属や、マグネシウムMg,カルシウムCa,ストロ
ンチウムSr,バリウムBaなどのアルカリ土類金属を
担持させたものを用いている。前記担体にアルカリ金属
又はアルカリ土類金属を担持させる場合は、炭酸塩又は
酢酸塩の形で、活性アルミナ100gに対して好ましく
は約0.01〜0.5 モル程度の量,より好ましくは0.2 〜0.
3 モル程度の量を付着させて担持させる。この場合に、
炭酸及び酢酸はいずれも無害な物質であるので、製造過
程において有害物質が排出されることはない。また、こ
れらを担体から完全に除去できないまま触媒毒吸着フィ
ルタ20,21として用いて排ガス処理しても、排ガス
中に含まれている触媒毒は炭酸又は酢酸と置換されて当
該吸着フィルタ20,21に吸着され、置換された炭酸
又は酢酸が当該吸着フィルタ20,21から排出される
ので、環境に悪影響を及ぼすことがない。また、触媒毒
吸着フィルタ20,21を形成するハニカム状の担体
は、圧力損失が少ないので、触媒毒吸着フィルタ20,
21を設けることによって排ガス流量が著しく低下する
ことがなく、また、整流性に優れているので、触媒層7
A〜7Cに均一に排ガスを流すことができる。The catalyst poison adsorption filters 20 and 2
1 is to coat a honeycomb-shaped carrier made of, for example, cordierite porcelain or stainless steel with activated alumina such as γ-alumina, and further thereon, an alkali metal such as lithium Li, sodium Na, potassium K, and cesium Cs; A material carrying an alkaline earth metal such as magnesium Mg, calcium Ca, strontium Sr, and barium Ba is used. When an alkali metal or alkaline earth metal is supported on the carrier, it is preferably in the form of a carbonate or an acetate in an amount of about 0.01 to 0.5 mol, more preferably 0.2 to 0.1 mol per 100 g of activated alumina.
Amount of about 3 mol is attached and supported. In this case,
Since carbonic acid and acetic acid are both harmless substances, no harmful substances are emitted during the manufacturing process. In addition, even if these are used as the catalyst poison adsorption filters 20 and 21 without exhausting them from the carrier, the catalyst poisons contained in the exhaust gas are replaced by carbonic acid or acetic acid and the adsorption filters 20 and 21 are removed. The carbonic acid or acetic acid that has been adsorbed and displaced is discharged from the adsorption filters 20 and 21, so that the environment is not adversely affected. Further, the honeycomb-shaped carrier forming the catalyst poison adsorption filters 20 and 21 has a small pressure loss.
By providing the catalyst layer 21, the flow rate of the exhaust gas is not significantly reduced and the rectification is excellent, so that the catalyst layer 7
Exhaust gas can be uniformly flowed to A to 7C.
【0020】 以上が本発明の一例構成であって、次に
その作用について説明する。本例の触媒燃焼式蓄熱排ガ
ス処理装置1を例えば塗装乾燥炉の排ガス処理装置とし
て使用する場合、塗装乾燥炉の排ガスを導く排ガスダク
ト(図示せず)を未処理排ガス導入ダクト8A〜8Cに
接続する。そして、オートダンパ11A〜11C,12
A〜12C,13A〜13Cを操作することにより、一
の蓄熱室5A(5B,5C)から導入された未処理排ガ
スを排ガス加熱室3及び前記触媒層7Bで浄化処理した
後、他の蓄熱室5B(5C,5A)から排出すると共
に、排ガスの導入側及び排出側を順次交互に切り換えて
連続的に処理を行うようにしている。The above is an example of the configuration of the present invention, and its operation will be described next. When the catalytic combustion type heat storage exhaust gas treatment apparatus 1 of the present embodiment is used, for example, as an exhaust gas treatment apparatus for a coating and drying furnace, an exhaust gas duct (not shown) for guiding exhaust gas from the coating and drying furnace is connected to the untreated exhaust gas introduction ducts 8A to 8C. I do. Then, the automatic dampers 11A to 11C, 12
By operating A to 12C and 13A to 13C, the untreated exhaust gas introduced from one heat storage chamber 5A (5B, 5C) is purified by the exhaust gas heating chamber 3 and the catalyst layer 7B, and then the other heat storage chamber. 5B (5C, 5A), and the exhaust gas introduction side and discharge side are alternately switched in order to perform the processing continuously.
【0021】 この場合、蓄熱室5A(5B,5C)に
導入された未処理排ガスは、その蓄熱層4を通過する際
に蓄熱層4に蓄えられた熱で予熱されて、触媒毒吸着フ
ィルタ20を通過した後、触媒層7Aに至る。このと
き、未処理排ガスに含まれる触媒毒のうち蓄熱層4で予
熱された温度で吸着される触媒毒は、触媒層7A(7
B,7C)に達する前に、触媒毒吸着フィルタ20に捕
捉される。したがって、未処理排ガスを導入する際に、
導入側の蓄熱室5A(5B,5C)に連続して配設され
た触媒層7A(7B,7C)には触媒毒がほとんど吸着
されず、触媒寿命が長くなる。In this case, the untreated exhaust gas introduced into the heat storage chamber 5A (5B, 5C) is preheated by the heat stored in the heat storage layer 4 when passing through the heat storage layer 4, and the catalyst poison adsorption filter 20 , And reaches the catalyst layer 7A. At this time, the catalyst poison adsorbed at the temperature preheated by the heat storage layer 4 among the catalyst poisons included in the untreated exhaust gas is the catalyst layer 7A (7
B, 7C) before being captured by the catalyst poison adsorption filter 20. Therefore, when introducing untreated exhaust gas,
The catalyst poisons are hardly adsorbed on the catalyst layers 7A (7B, 7C) continuously arranged in the heat storage chambers 5A (5B, 5C) on the introduction side, and the catalyst life is extended.
【0022】 また、排ガス加熱室3に導入された未処
理排ガスは、ガスバーナなどの加熱装置2で所定の処理
温度(300〜450℃)に加熱されて、触媒毒吸着フ
ィルタ21を通過した後、触媒層7B(7C,7A)で
浄化処理される。このとき、未処理排ガスに含まれる触
媒毒のうち排ガス加熱室3で加熱された温度で吸着され
る触媒毒や、排ガス加熱室3で加熱されることによって
生成された触媒毒は、触媒層7B(7C,7A)に達す
る前に、触媒毒吸着フィルタ21に捕捉される。したが
って、排ガス加熱室3で加熱された未処理排ガスを触媒
層7B(7C,7A)で浄化処理する際に、その触媒層
7B(7C,7A)には触媒毒がほとんど吸着されず、
触媒寿命が長くなる。The untreated exhaust gas introduced into the exhaust gas heating chamber 3 is heated to a predetermined processing temperature (300 to 450 ° C.) by a heating device 2 such as a gas burner and passes through a catalyst poison adsorption filter 21. Purification processing is performed in the catalyst layer 7B (7C, 7A). At this time, the catalyst poison adsorbed at the temperature heated in the exhaust gas heating chamber 3 and the catalyst poison generated by heating in the exhaust gas heating chamber 3 among the catalyst poisons contained in the untreated exhaust gas are the catalyst layers 7B Before reaching (7C, 7A), it is captured by the catalyst poison adsorption filter 21. Therefore, when the untreated exhaust gas heated in the exhaust gas heating chamber 3 is purified by the catalyst layer 7B (7C, 7A), almost no catalyst poison is adsorbed on the catalyst layer 7B (7C, 7A).
The catalyst life is extended.
【0023】そして、触媒毒吸着フィルタ20,21と
して、コージエライト磁器で形成されたハニカム状の担
体に例えばγ−アルミナなどの活性アルミナをコーティ
ングしているので、排ガスと触媒毒吸着フィルタ20,
21との接触面積が極めて大きくなり触媒毒の吸着効率
がよい。また、本例では、活性アルミナの上からアルカ
リ金属又はアルカリ土類金属を担持させているので、ア
ルカリ金属又はアルカリ土類金属が活性アルミナにより
多少中和されることを考慮しても触媒毒吸着フィルタ2
0,21の表面は強いアルカリ性を示す。したがって、
排ガス中に強い酸性を示すシリカが大量に含まれている
場合であっても、シリカはアルカリ性の触媒毒吸着フィ
ルタに吸着されて中和されることとなり、シリカによる
触媒被毒をより効果的に低減することができる。As the catalyst poison adsorption filters 20 and 21, the honeycomb-shaped carrier formed of cordierite porcelain is coated with activated alumina such as γ-alumina, so that the exhaust gas and the catalyst poison adsorption filters 20, 21 are coated.
The contact area with the catalyst poison 21 is extremely large, and the catalyst poison adsorption efficiency is good. Further, in this example, the alkali metal or the alkaline earth metal is supported on the activated alumina. Therefore, even when considering that the alkali metal or the alkaline earth metal is somewhat neutralized by the activated alumina, the adsorption of the catalyst poison is performed. Filter 2
The surface of 0,21 shows strong alkalinity. Therefore,
Even when a large amount of strongly acidic silica is contained in the exhaust gas, the silica is adsorbed and neutralized by the alkaline catalyst poison adsorption filter, and the catalyst poisoning by silica is more effectively performed. Can be reduced.
【0024】 なお、触媒毒吸着フィルタ20,21
は、触媒毒が吸着されて飽和状態になったときに新しい
ものと交換すればよい。この場合において、触媒毒吸着
フィルタ20,21には白金などの高価な触媒が使用さ
れていないので触媒層7A〜7Cより安価であり、した
がって、これを頻繁に交換しても、触媒層7A〜7Cを
交換する場合に比してコストが低減される。The catalyst poison adsorption filters 20 and 21
May be replaced with a new one when the catalyst poison is adsorbed and becomes saturated. In this case, since the catalyst poison adsorption filters 20 and 21 do not use an expensive catalyst such as platinum, they are less expensive than the catalyst layers 7A to 7C. The cost is reduced as compared with the case where 7C is replaced.
【0025】 また、上述の説明では、触媒毒吸着フィ
ルタ20,21として、活性アルミナをコーティングし
た担体にアルカリ金属又はアルカリ土類金属を担持させ
る場合について説明したが、アルカリ金属又はアルカリ
土類金属を担持させずに、担体に活性アルミナをコーテ
ィングしたものを触媒毒吸着フィルタ20,21として
使用してもよい。活性アルミナは、酸性物質に対しては
アルカリ性を示し、塩基性(アルカリ性)物質に対して
は酸性を示す両性を有するので、いずれの性質を示す触
媒毒に対してもこれを中和させて吸着する効果を有す
る。In the above description, the case where an alkali metal or an alkaline earth metal is supported on a carrier coated with activated alumina as the catalyst poison adsorption filters 20 and 21 has been described. Instead of carrying the carrier, a carrier coated with activated alumina may be used as the catalyst poison adsorption filters 20 and 21. Activated alumina has both amphoteric properties, indicating alkalinity for acidic substances and acidity for basic (alkaline) substances. Therefore, it neutralizes and adsorbs catalyst poisons of any property. It has the effect of doing.
【0026】 さらに、触媒毒吸着フィルタ20,21
が、触媒層7A〜7Cの蓄熱室5A〜5C側及び排ガス
加熱室3側の双方に配されている場合について説明した
が、本発明はこれに限るものではない。例えば、比較的
低い温度で吸着される触媒毒のみが未処理排ガスに含ま
れている場合は、触媒層7A〜7Cの蓄熱室5A〜5C
側のみに触媒毒吸着フィルタ20を設ければ足り、比較
的高い温度で吸着される触媒毒のみが未処理排ガスに含
まれている場合は、触媒層7A〜7Cの排ガス加熱室7
A〜7C側のみに触媒毒吸着フィルタ21を設ければ足
り、さらにこれらが混合して含まれているような場合
は、上述した説明のように双方に設ければよい。さら
に、蓄熱室5A〜5Cが三つ配された三塔式の触媒燃焼
式蓄熱排ガス処理装置1に適用した場合について説明し
たが、これに限らず、二塔式のものや,四塔式,六塔式
などの多塔式のものにも適用できることはもちろんであ
る。Further, the catalyst poison adsorption filters 20 and 21
Has been described on both the heat storage chambers 5A to 5C side of the catalyst layers 7A to 7C and the exhaust gas heating chamber 3 side, but the present invention is not limited to this. For example, when only the catalyst poison adsorbed at a relatively low temperature is contained in the untreated exhaust gas, the heat storage chambers 5A to 5C of the catalyst layers 7A to 7C are used.
It is sufficient to provide the catalyst poison adsorbing filter 20 only on the side, and when only the catalyst poison adsorbed at a relatively high temperature is contained in the untreated exhaust gas, the exhaust gas heating chamber 7 of the catalyst layers 7A to 7C is provided.
It is sufficient to provide the catalyst poison adsorption filter 21 only on the A to 7C sides, and when these are mixed and contained, they may be provided on both sides as described above. Furthermore, the case where the present invention is applied to a three-tower type catalytic combustion-type thermal storage exhaust gas treatment apparatus 1 in which three heat storage chambers 5A to 5C are arranged has been described. However, the present invention is not limited thereto, and a two-tower type, a four-tower type, Of course, it can be applied to a multi-tower type such as a six-tower type.
【0027】[0027]
【発明の効果】以上述べたように、本発明によれば、排
ガス中に含まれている触媒毒は、排ガスが触媒層を通過
する前に、その蓄熱室側又は排ガス加熱室側に配設され
た触媒毒吸着フィルタに吸着されるので、その分触媒層
の被毒が低減され、触媒寿命が延びるという優れた効果
がある。また、触媒毒吸着フィルタには白金などの高価
な触媒が付着されていないので触媒層より安価であり、
したがって、触媒毒吸着フィルタを頻繁に交換しても、
触媒層を交換する場合に比してコストが低減されるとい
う効果がある。さらに、触媒毒吸着フィルタとして、担
体にγ−アルミナなどの活性アルミナをコーティングし
ており、活性アルミナによりその表面積が極めて大きく
なるので、触媒毒となる物質の吸着効率が非常に高いと
いう効果があると同時に、活性アルミナは、酸性物質に
対してはアルカリ性を示し、塩基性(アルカリ性)物質
に対しては酸性を示す両性を有するので、いずれの性質
を示す触媒毒に対してもこれを中和させて効率良く吸着
するという大変優れた効果を有する。さらにまた、活性
アルミナの上からアルカリ金属又はアルカリ土類金属を
担持させれば、触媒毒吸着フィルタの表面は強いアルカ
リ性を示すため、排ガス中に、触媒毒として強い酸性を
示すシリカが大量に含まれている場合であっても、当該
シリカを高効率で吸着させ、シリカによる触媒被毒をよ
り著しく低減することができるという大変優れた効果を
奏する。As described above, according to the present invention, the catalyst poison contained in the exhaust gas is disposed on the heat storage chamber side or the exhaust gas heating chamber side before the exhaust gas passes through the catalyst layer. Since the catalyst poison adsorbing filter is adsorbed, the poisoning of the catalyst layer is reduced by that amount, and there is an excellent effect that the catalyst life is extended. In addition, the catalyst poison adsorption filter is less expensive than the catalyst layer because no expensive catalyst such as platinum is attached.
Therefore, even if the catalyst poison adsorption filter is frequently replaced,
There is an effect that the cost is reduced as compared with the case where the catalyst layer is replaced. Furthermore, as a catalyst poison adsorption filter, the carrier is coated with activated alumina such as γ-alumina, and the activated alumina has an extremely large surface area, so that there is an effect that the adsorption efficiency of a substance that becomes a catalyst poison is extremely high. At the same time, activated alumina has both amphoteric properties, indicating alkalinity for acidic substances and acidity for basic (alkaline) substances, and therefore neutralizes catalyst poisons of any nature. It has a very excellent effect of being efficiently adsorbed. Furthermore, if an alkali metal or an alkaline earth metal is supported on the activated alumina, the surface of the catalyst poison adsorption filter shows strong alkalinity, so that a large amount of silica showing strong acidity as catalyst poison is contained in the exhaust gas. Even if it is, the silica is adsorbed with high efficiency, and a very excellent effect that the catalyst poisoning by the silica can be significantly reduced can be achieved.
【図1】 本発明に係る触媒燃焼式蓄熱排ガス処理装置
を示す概略説明図。FIG. 1 is a schematic explanatory view showing a catalytic combustion type heat storage exhaust gas treatment apparatus according to the present invention.
【図2】 従来装置を示す概略説明図。FIG. 2 is a schematic explanatory view showing a conventional apparatus.
1・・・・・・排ガス処理装置 2・・・・・・加熱装置 3・・・・・・排ガス加熱室 4・・・・・・蓄熱層 5A〜5C・・蓄熱室 6・・・・・・開口部 7A〜7C・・触媒層 20,21・・・触媒毒吸着フィルタ DESCRIPTION OF SYMBOLS 1 ... Exhaust gas processing apparatus 2 ... Heating apparatus 3 ... Exhaust gas heating chamber 4 ... Thermal storage layer 5A-5C ... Thermal storage chamber 6 ... ..Opening portions 7A to 7C..Catalyst layer 20, 21 ... Catalyst poison adsorption filter
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI B01D 53/86 B01J 23/02 ZABA B01J 23/02 ZAB B01D 53/36 G F23J 15/00 H F23J 15/00 J (72)発明者 佐 野 善 博 愛知県豊田市柿本町一丁目9番地 トリニ ティ工業株式会社内 (72)発明者 隅 田 健 二 静岡県小笠郡大東町千浜7800番地 キャタ ラー工業株式会社内──────────────────────────────────────────────────の Continued on the front page (51) Int.Cl. 6 Identification code FI B01D 53/86 B01J 23/02 ZABA B01J 23/02 ZAB B01D 53/36 G F23J 15/00 H F23J 15/00 J (72) Inventor Yoshihiro Sano 1-9-9 Kakimotocho, Toyota City, Aichi Prefecture Inside Trinity Industry Co., Ltd. (72) Inventor Kenji Sumita 7800 Chihama, Oto-cho, Ogasa-gun, Shizuoka Prefecture Inside Cataler Industry Co., Ltd.
Claims (1)
の熱を回収し、低温の未処理排ガスを導入する際に当該
排ガスを予熱する蓄熱層(4)を有する複数の蓄熱室
(5A〜5C)が、未処理排ガスを所定の温度まで加熱する
加熱装置(2)を備えた排ガス加熱室(3)に対して並
設され、前記排ガス加熱室(3)と各蓄熱層(4)の間
には未処理排ガス中に含まれる可燃性成分を酸化燃焼又
は熱分解させて浄化処理する触媒層(7A〜7C)が形成さ
れて成り、一の蓄熱室(5A〜5C)から導入された未処理
排ガスを前記排ガス加熱室(3)及び前記触媒層(7A〜
7C)で浄化処理した後、その処理済排ガスを他の蓄熱室
(5A〜5C)から排出すると共に、排ガスの導入側及び排
出側を順次交互に切り換えて連続的に処理を行う触媒燃
焼式蓄熱排ガス処理装置において、 排ガス中に含まれる触媒毒を吸着する触媒毒吸着フィル
タ(20, 21)が、前記各触媒層(7A〜7C)の蓄熱室(5A〜
5C)側及び排ガス加熱室(3)側のいずれか一方又は双
方に交換可能に装着されると共に、当該触媒毒吸着フィ
ルタ(20,21)が担体に活性アルミナをコーティングし
て形成され、又は、活性アルミナをコーティングした担
体にアルカリ金属又はアルカリ土類金属を担持させて形
成されたことを特徴とする触媒燃焼式蓄熱排ガス処理装
置。A plurality of heat storage chambers (5A to 5A) having a heat storage layer (4) for recovering heat when discharging a high-temperature treated exhaust gas and preheating the exhaust gas when introducing a low-temperature untreated exhaust gas. 5C) is provided in parallel with an exhaust gas heating chamber (3) provided with a heating device (2) for heating the untreated exhaust gas to a predetermined temperature, and the exhaust gas heating chamber (3) and each heat storage layer (4) A catalyst layer (7A to 7C) for purifying by oxidizing, burning, or thermally decomposing flammable components contained in the untreated exhaust gas is formed between them, and is introduced from one heat storage chamber (5A to 5C). The untreated exhaust gas is supplied to the exhaust gas heating chamber (3) and the catalyst layer (7A ~
After purifying in 7C), the treated exhaust gas is exhausted from the other heat storage chambers (5A to 5C), and the exhaust gas introduction side and exhaust side are alternately switched in order to perform continuous treatment. In the exhaust gas treatment apparatus, the catalyst poison adsorption filters (20, 21) for adsorbing catalyst poisons contained in the exhaust gas are provided in the heat storage chambers (5A to 5C) of each of the catalyst layers (7A to 7C).
The catalyst poison adsorption filter (20, 21) is formed by coating the carrier with activated alumina, and is exchangeably mounted on one or both of the 5C) side and the exhaust gas heating chamber (3) side, or A catalytic combustion type heat storage exhaust gas treatment apparatus formed by supporting an alkali metal or an alkaline earth metal on a carrier coated with activated alumina.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP9043769A JPH10238741A (en) | 1997-02-27 | 1997-02-27 | Catalytic combustion type thermal storage exhaust gas treating apparatus |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP9043769A JPH10238741A (en) | 1997-02-27 | 1997-02-27 | Catalytic combustion type thermal storage exhaust gas treating apparatus |
Publications (1)
Publication Number | Publication Date |
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JPH10238741A true JPH10238741A (en) | 1998-09-08 |
Family
ID=12672968
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP9043769A Pending JPH10238741A (en) | 1997-02-27 | 1997-02-27 | Catalytic combustion type thermal storage exhaust gas treating apparatus |
Country Status (1)
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JP (1) | JPH10238741A (en) |
Cited By (11)
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JP2003170024A (en) * | 2001-12-05 | 2003-06-17 | Babcock Hitachi Kk | Method for cleaning exhaust gas by heat storage system catalyst combustion process |
KR100458931B1 (en) * | 2001-09-07 | 2004-12-03 | 대양환경(주) | Rotary Regenerative NOx Abatement System with Distribution Wings |
CN104879760A (en) * | 2015-05-08 | 2015-09-02 | 中国科学院过程工程研究所 | Cylindrical thermal storage catalytic combustor |
JP2016503875A (en) * | 2012-12-12 | 2016-02-08 | スリーエム イノベイティブ プロパティズ カンパニー | Catalyst burner |
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CN111780140A (en) * | 2020-07-30 | 2020-10-16 | 南京大学环境规划设计研究院股份公司 | Heat accumulating type catalytic combustion device for VOCs treatment |
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CN115430259A (en) * | 2022-09-23 | 2022-12-06 | 深圳盈和环境物联科技有限公司 | Efficient and energy-saving waste gas purification system and method for circuit board oven |
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Cited By (13)
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---|---|---|---|---|
KR100458931B1 (en) * | 2001-09-07 | 2004-12-03 | 대양환경(주) | Rotary Regenerative NOx Abatement System with Distribution Wings |
JP2003170024A (en) * | 2001-12-05 | 2003-06-17 | Babcock Hitachi Kk | Method for cleaning exhaust gas by heat storage system catalyst combustion process |
JP2016503875A (en) * | 2012-12-12 | 2016-02-08 | スリーエム イノベイティブ プロパティズ カンパニー | Catalyst burner |
CN104879760A (en) * | 2015-05-08 | 2015-09-02 | 中国科学院过程工程研究所 | Cylindrical thermal storage catalytic combustor |
CN106582262A (en) * | 2015-10-19 | 2017-04-26 | 江苏中科睿赛污染控制工程有限公司 | Heat accumulating type VOCs catalytic oxidation device and technology |
CN108176223A (en) * | 2017-12-30 | 2018-06-19 | 江苏永益环保科技有限公司 | Paint booth organic waste gas catalytic combustion processing system |
CN109737434A (en) * | 2019-01-15 | 2019-05-10 | 长沙凯天工研院环保服务有限公司 | A kind of coating waste gas heating power oxidation minimum discharge system |
CN111780140A (en) * | 2020-07-30 | 2020-10-16 | 南京大学环境规划设计研究院股份公司 | Heat accumulating type catalytic combustion device for VOCs treatment |
CN114719273A (en) * | 2022-03-09 | 2022-07-08 | 山东保蓝环保工程有限公司 | Chemical waste gas treatment and tail end carbon dioxide processing apparatus |
CN115430259A (en) * | 2022-09-23 | 2022-12-06 | 深圳盈和环境物联科技有限公司 | Efficient and energy-saving waste gas purification system and method for circuit board oven |
CN115430259B (en) * | 2022-09-23 | 2024-09-27 | 深圳盈和环境物联科技有限公司 | Efficient and energy-saving waste gas purifying system and method for circuit board oven |
CN116447607A (en) * | 2023-04-19 | 2023-07-18 | 江苏洋井环保服务有限公司 | Industrial waste gas administers with innocent treatment device |
CN116447607B (en) * | 2023-04-19 | 2023-09-12 | 江苏洋井环保服务有限公司 | Industrial waste gas administers with innocent treatment device |
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