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JPH0788329A - Treatment of waste gas containing organohalogen compound - Google Patents

Treatment of waste gas containing organohalogen compound

Info

Publication number
JPH0788329A
JPH0788329A JP5256333A JP25633393A JPH0788329A JP H0788329 A JPH0788329 A JP H0788329A JP 5256333 A JP5256333 A JP 5256333A JP 25633393 A JP25633393 A JP 25633393A JP H0788329 A JPH0788329 A JP H0788329A
Authority
JP
Japan
Prior art keywords
exhaust gas
catalyst
heat storage
heat exchanger
temperature
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
JP5256333A
Other languages
Japanese (ja)
Inventor
Takahiro Oshita
孝裕 大下
Ryuichi Ishikawa
龍一 石川
Tsutomu Higo
勉 肥後
Mitsuyoshi Kaneko
充良 金子
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.)
Ebara Corp
Original Assignee
Ebara Corp
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 Ebara Corp filed Critical Ebara Corp
Priority to JP5256333A priority Critical patent/JPH0788329A/en
Publication of JPH0788329A publication Critical patent/JPH0788329A/en
Pending legal-status Critical Current

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  • Incineration Of Waste (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Abstract

PURPOSE:To decompose and remove the poisonous org. halogen compds. such as dioxine in a waste gas generated from the incineration of various wastes while suppressing the resynthesis of the compds. CONSTITUTION:A waste gas contg. org. halogen compds. discharged from combustion equipment 1 is passed through a catalyst bed to decompose and remove the compds. The catalyst bed is set as the heat accumulator of a regenerative heat exchanger 3. An NOx removing catalyst is preferably used as the catalyst of the bed, air is used as the cooling medium of the heat exchanger, and the heated air is preferably used as the combustion air of the equipment 1.

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、有機ハロゲン化合物を
含有する排ガス処理方法に係り、特に、焼却炉排ガス等
に含まれるポリ塩化ジベンゾダイオキシンやポリ塩化ジ
ベンゾフラン等の毒性有機ハロゲン化合物を触媒を用い
て分解除去する排ガスの処理方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating an exhaust gas containing an organic halogen compound, and in particular, using a toxic organic halogen compound such as polychlorinated dibenzodioxin or polychlorinated dibenzofuran contained in an incinerator exhaust gas using a catalyst. The present invention relates to a method for treating exhaust gas, which is decomposed and removed by means of.

【0002】[0002]

【従来の技術】産業廃棄物や都市廃棄物を処理する焼却
施設等から発生する排ガス中に含有されているダイオキ
シン、PCB、クロロフェノール等の極微量の毒性有機
塩素化合物については、除去技術の研究の歴史が浅く、
個々の技術としては実用化されつつあるが経済性を含め
たトータルシステムとしての確立には至っていない。
2. Description of the Related Art Research on removal technology for trace amounts of toxic organic chlorine compounds such as dioxins, PCBs and chlorophenols contained in exhaust gas generated from incineration facilities for treating industrial waste and municipal waste. Has a short history,
Although it is being put to practical use as an individual technology, it has not been established as a total system including economic efficiency.

【0003】このうちダイオキシンと呼ばれている物質
はポリ塩化ジベンゾダイオキシンという化合物であり、
塩素の数によって二塩化物、四塩化物、五塩化物、六塩
化物などがあり、異性体は70種以上に及び、特に四塩
化ジベンゾダイオキシン(T4 CDD)は最強の毒性物
質として知られている。またダイオキシンは非常に安定
な物質で水に溶けず、半永久的に毒性が消失しないこと
からその強い毒性と相まって環境汚染の重要化学物質と
考えられている。一般に、ダイオキシン類を含む毒性有
機塩素化合物の分解除去技術としては、高温燃焼を行な
う所謂直燃式処理法、活性炭等による吸着法、薬剤によ
る洗浄法、触媒による分解法等が知られている。
Of these, the substance called dioxin is a compound called polychlorinated dibenzodioxin,
Depending on the number of chlorine, there are dichlorides, tetrachlorides, pentachlorides, hexachlorides, etc. There are more than 70 isomers, and dibenzodioxin tetrachloride (T 4 CDD) is known to be the strongest toxic substance. ing. Dioxin is a very stable substance that does not dissolve in water and its toxicity does not disappear semipermanently, so it is considered to be an important chemical substance for environmental pollution in combination with its strong toxicity. In general, as a technique for decomposing and removing toxic organic chlorine compounds including dioxins, a so-called direct combustion type treatment method in which high temperature combustion is performed, an adsorption method with activated carbon, a cleaning method with a chemical agent, a decomposition method with a catalyst and the like are known.

【0004】このうち直燃式処理法は、前記毒性有機塩
素化合物の完全酸化分解を燃焼プロセスで行なうもので
あり、実施に際しては1000℃以上の高温維持が必要
とされている。ところが焼却炉内の燃焼温度は800〜
950℃であるから、有機塩素化合物を酸化分解するに
は炉内温度を更に高めるか、或は再燃焼部を設ける必要
がある。しかるに炉内温度を上昇させる場合は炉の全面
的な改造を必要とする上に、950℃以上では焼却物の
灰分が溶融して炉壁を損傷あるいは炉壁に付着するとい
う問題がある。
Of these, the direct combustion type treatment method is one in which complete oxidative decomposition of the toxic organochlorine compound is carried out by a combustion process, and it is necessary to maintain a high temperature of 1000 ° C. or higher when carrying out the method. However, the combustion temperature in the incinerator is 800-
Since the temperature is 950 ° C., it is necessary to further raise the temperature in the furnace or provide a reburning section in order to oxidatively decompose the organic chlorine compound. However, in order to raise the temperature in the furnace, there is a problem that the furnace must be completely remodeled, and if the temperature is 950 ° C. or higher, the ash content of the incinerator is melted and the furnace wall is damaged or adheres to the furnace wall.

【0005】また、再燃焼部を設ける方法の場合には排
ガス総量の増加や再燃焼用燃料によるランニングコスト
の上昇が極めて大きくなるという欠点が発生する。しか
も、排ガス中の被処理物質濃度が希薄であるので処理効
率はどうしても低くならざるを得ない。一方吸着法では
廃活性炭の再生処理が、また洗浄法では廃液の2次処理
が夫々必要となり、しかもこれらの2次処理手段が非常
に厄介であるので実用的な分解除去技術とは言えない。
Further, in the case of the method of providing the re-combustion section, there is a drawback that the total amount of exhaust gas and the running cost due to the fuel for re-combustion increase significantly. Moreover, since the concentration of the substance to be treated in the exhaust gas is low, the treatment efficiency is inevitably low. On the other hand, the adsorption method requires regeneration of waste activated carbon, and the washing method requires secondary treatment of waste liquid. Further, these secondary treatment means are very troublesome, and thus cannot be said to be a practical decomposition and removal technique.

【0006】最も実用的と期待されている触媒による分
解法は、ある温度領域(200〜500℃)でダイオキ
シン等を分解することが発見されている。しかるに、現
状の方法は次のような使用上の制約がある。 触媒の洗浄機能がないので、触媒の貫通孔(排ガス
通路)の開口寸法を大きくしなければならないため、触
媒単位容積当りの表面積が小さくなり、触媒が大容量に
なる。
It has been discovered that the catalytic decomposition method, which is expected to be most practical, decomposes dioxin and the like in a certain temperature range (200 to 500 ° C.). However, the current method has the following restrictions on use. Since the catalyst has no cleaning function, the opening size of the through hole (exhaust gas passage) of the catalyst has to be increased, so that the surface area per unit volume of the catalyst becomes small and the catalyst has a large capacity.

【0007】 触媒の貫通孔の開口寸法を小さくし
て、触媒単位容積当りの表面積を大きくすると触媒の容
量を小さくすることができるが、洗滌機能がないので、
この場合にはバグフィルタ等で除じんをした後に設置し
なければならない。一方、触媒の活性温度領域(250
℃〜450℃)は、バグフィルタの耐熱温度(200℃
〜250℃)よりも高いため、バグフィルタ通過後の排
ガスを再加熱しなければならないという実用上の制約が
ある。
If the opening size of the through holes of the catalyst is made small and the surface area per unit volume of the catalyst is made large, the capacity of the catalyst can be made small, but since there is no cleaning function,
In this case, it must be installed after removing dust with a bag filter. On the other hand, the active temperature range of the catalyst (250
℃ -450 ℃ is the heat resistant temperature of bag filter (200 ℃)
Since the temperature is higher than ˜250 ° C.), there is a practical limitation that the exhaust gas after passing through the bag filter must be reheated.

【0008】 現状の触媒には、排ガスを減温する機
能がないため、例えば300℃の排ガス中に設置したと
すると、この部分でダイオキシン等を分解できても、そ
の後のバグフィルター等の集じん器の耐熱温度まで排ガ
ス温度を下げる過程、即ち通常ボイラ効率等の熱利用効
率を高めるために節炭器や空気予熱器が設置されるが、
この部分で、飛灰や冷却伝熱面である金属等が関与し
て、ダイオキシン類が再合成されることが明らかになっ
た。この再合成を抑制する手段として現在提案されてい
るのは、水噴霧急速減温だけであるが、この方法はエネ
ルギー回収効率の点で問題がある。
Since the current catalyst does not have a function of reducing the temperature of exhaust gas, if it is installed in the exhaust gas at 300 ° C., for example, even if dioxin and the like can be decomposed at this portion, dust collection by a bag filter or the like after that is possible. The process of lowering the exhaust gas temperature to the heat resistant temperature of the furnace, that is, a economizer and an air preheater are installed to increase the heat utilization efficiency such as the boiler efficiency.
In this part, it was revealed that the fly ash and the metal, which is the heat transfer surface for cooling, are involved to re-synthesize dioxins. The only method currently proposed for suppressing this re-synthesis is rapid water spray temperature reduction, but this method has a problem in terms of energy recovery efficiency.

【0009】[0009]

【発明が解決しようとする課題】本発明は、上記従来技
術の問題点を解決し、各種廃棄物の焼却処理から発生す
るダイオキシン等の毒性有機塩素化合物の再合成を抑制
しつつ分解除去し、ダイオキシン等の再合成温度領域以
下に触媒内で減温することのできる排ガス処理方法を提
供することを課題とする。
DISCLOSURE OF THE INVENTION The present invention solves the above-mentioned problems of the prior art, decomposes and removes while suppressing the resynthesis of toxic organic chlorine compounds such as dioxins generated from the incineration of various wastes, An object of the present invention is to provide an exhaust gas treatment method capable of reducing the temperature in the catalyst to a temperature below the re-synthesis temperature range of dioxins and the like.

【0010】[0010]

【課題を解決するための手段】上記課題を解決するため
に、本発明では、燃焼装置から排出する有機ハロゲン化
合物を含有する排ガスを触媒層を通して分解除去する排
ガスの処理方法において、前記触媒層が蓄熱式熱交換器
の蓄熱体として設置されていることとしたものである。
In order to solve the above-mentioned problems, the present invention provides a method for treating exhaust gas which decomposes and removes exhaust gas containing an organic halogen compound discharged from a combustion device through a catalyst layer, wherein the catalyst layer is It is supposed to be installed as a heat storage body of a heat storage type heat exchanger.

【0011】上記のように、本発明においては、焼却炉
排ガス等に含まれるポリ塩化ジベンゾダイオキシンやポ
リ塩化ジベンゾフラン等の毒性有機ハロゲン化合物を、
触媒を用いて除去する方法において、該触媒を担持した
触媒層を、蓄熱式熱交換器の蓄熱体として、排ガスを減
温する過程で毒性有機塩素化合物の再合成を抑制すると
同時に分解除去する。上記において、触媒層の触媒とし
ては、窒素酸化物除去( Denox )触媒あるいは改造De
nox触媒を用いることにより、有機塩素化合物の再合
成を抑制すると同時に分解除去する他に、脱硝機能をも
合せて有させることができる。
As described above, in the present invention, toxic organohalogen compounds such as polychlorinated dibenzodioxin and polychlorinated dibenzofuran contained in incinerator exhaust gas are
In the method of removing by using a catalyst, the catalyst layer supporting the catalyst is used as a heat storage body of a heat storage heat exchanger to suppress re-synthesis of toxic organochlorine compounds while decomposing and removing them in the process of reducing the temperature of exhaust gas. In the above, the catalyst of the catalyst layer is a nitrogen oxide removal (Denox) catalyst or a modified De
By using the nox catalyst, it is possible not only to suppress the resynthesis of the organic chlorine compound but also to decompose and remove it, and also to have a denitration function.

【0012】また、上記において、蓄熱式熱交換器は、
冷却側媒体として空気を用い、該加熱された空気を燃焼
装置の燃焼用空気、特に二次燃焼用空気として利用する
ことができ、該熱交換器を通る排ガスと前記空気の流れ
を向流として、1サイクル当り確実に空気による逆洗を
することにより、触媒への灰の付着や灰による閉塞を防
止することができる。前記触媒層である蓄熱体は、貫通
孔の相当直径が2mm以上で、かつ開口率が50%以上
のハニカム構造体であるのがよい。そして、上記の蓄熱
式熱交換器では、排ガス温度を入口で300〜450℃
のものを、出口で150〜250℃にまで減温すること
ができる。
Further, in the above, the heat storage type heat exchanger is
Air is used as a cooling medium, and the heated air can be used as combustion air for a combustion device, particularly as secondary combustion air, and the flow of exhaust gas and the air passing through the heat exchanger as a countercurrent flow. By reliably backwashing with air per cycle, it is possible to prevent ash from adhering to the catalyst and blocking by ash. The heat storage body which is the catalyst layer is preferably a honeycomb structure having a through hole with an equivalent diameter of 2 mm or more and an opening ratio of 50% or more. And in the said heat storage type heat exchanger, exhaust gas temperature is 300-450 degreeC at an inlet.
Can be cooled to 150-250 ° C at the outlet.

【0013】[0013]

【作用】本発明は、産業廃棄物や都市廃棄物を処理する
焼却炉排ガス中に含まれるポリ塩化ジベンゾダイオキシ
ンやポリ塩化ジベンゾフラン等の毒性有機塩素化合物
を、触媒を用いて除くものであるが、該触媒を用いた触
媒層を蓄熱式熱交換器の蓄熱体として、排ガスを減温す
る過程で毒性有機塩素化合物の再合成を抑制しつつ分解
除去するものである。
The present invention uses a catalyst to remove toxic organic chlorine compounds such as polychlorinated dibenzodioxins and polychlorinated dibenzofurans contained in exhaust gas from incinerators for treating industrial wastes and municipal wastes. The catalyst layer using the catalyst is used as a heat storage body of a heat storage heat exchanger to decompose and remove the toxic organochlorine compound while suppressing the resynthesis of the toxic organochlorine compound in the process of reducing the temperature of the exhaust gas.

【0014】ダイオキシン等の再合成及び分解するため
の反応温度は極めて重要な因子であるが、この温度領域
は、再合成も分解もほぼ同じであることが大きな特徴で
ある。両者共250℃〜450℃好ましくは250〜4
00℃の温度領域である。200℃未満では、除去効率
が低いことに加え、排ガス中のHClやSOxによる触
媒被毒が大きくなり、劣化促進が著しくなる。一方反応
温度が高過ぎると、触媒の変質を招く恐れがあり、長時
間の使用が困難となるので500℃以下に抑えることが
望まれる。
The reaction temperature for resynthesizing and decomposing dioxin and the like is an extremely important factor, and this temperature region is largely characterized in that resynthesis and decomposition are almost the same. Both are 250 to 450 ° C., preferably 250 to 4
This is a temperature range of 00 ° C. If the temperature is lower than 200 ° C, not only the removal efficiency is low, but also the poisoning of the catalyst by HCl or SOx in the exhaust gas becomes large and the deterioration is significantly accelerated. On the other hand, if the reaction temperature is too high, the catalyst may be deteriorated and it becomes difficult to use it for a long time.

【0015】なお、本発明に適用される触媒については
特に制限を設けるものではないが、処理ガス中に含まれ
る硫黄化合物やハロゲン化合物等の影響を受けにくい耐
酸性のものが好ましい。Denox触媒あるいは改良D
enox触媒を、酸化条件下(6〜12%のO2 含有量
ないしはそれ以上)で、排ガス温度200〜500℃、
好ましくは、250〜400℃の温度領域に設置するこ
とにより、ダイオキシン等の有機塩素化合物や窒素酸化
物を分解することは、PCT/EP90/01685、
特開平3−8415号、特開平3−12221号各公報
等に記載され公知であり、本発明においてもこれらの触
媒を用いることができる。
The catalyst applied to the present invention is not particularly limited, but an acid resistant catalyst that is not easily affected by the sulfur compounds and halogen compounds contained in the processing gas is preferable. Denox catalyst or modified D
Exhaust gas temperature of 200-500 ° C. under oxidative conditions (6-12% O 2 content or higher)
Preferably, by disposing in a temperature range of 250 to 400 ° C. to decompose organic chlorine compounds such as dioxins and nitrogen oxides, PCT / EP90 / 01685,
These catalysts are known and described in JP-A-3-8415 and JP-A-3-122221, and these catalysts can be used in the present invention.

【0016】一方、250〜450℃の排ガス冷却部で
ダイオキシン等が再合成されることも、例えば、VGB
クラフトワークテクニック( VGB Kraft werk tecknik
) 69巻、1989年8月8日、S795〜802又
はVDIベリヒテ( VDI Berichte ) NR、895、1
991、S193〜210に記載のように公知である。
図2は、公知の触媒を用いた排ガスの処理方法の工程図
を示すものであるが、この方式では、後段の節炭器ある
いは空気予熱器でダイオキシン等が再合成されること。
そして触媒の洗滌機能がないため長時間運転すると、触
媒の開口部が飛灰により閉塞していくため、開口寸法に
制約がある等の問題点がある。
On the other hand, when dioxin and the like are resynthesized in the exhaust gas cooling section at 250 to 450 ° C., for example, VGB
Kraftwork Technique (VGB Kraft werk tecknik
) Volume 69, August 8, 1989, S795-802 or VDI Berichte NR, 895, 1
991, S193-210.
FIG. 2 shows a process chart of an exhaust gas treatment method using a known catalyst. In this method, dioxins and the like are resynthesized in a economizer or an air preheater at a subsequent stage.
Since the catalyst does not have a washing function and the catalyst is opened for a long time, the opening of the catalyst is blocked by fly ash, which poses a problem that the opening size is restricted.

【0017】実際に実用機で使用するとなると、図3に
示すように、バグフィルター等の集じん器で飛灰を除じ
んした後に設置されることになるが、集じん器通過後の
排ガスを、触媒の分解能がある温度領域まで再加熱しな
ければならないため、エネルギーの無駄使いとなってし
まう。図1は、本発明による触媒機能付蓄熱式熱交換
器、例えばユングストローム式空気予熱器等の連続的に
排ガスと接触熱交換する蓄熱体が変化循環するものを実
装置に設置した一例を示す工程図である。
When it is actually used in a practical machine, as shown in FIG. 3, it is installed after dust ash is removed by a dust collector such as a bag filter, but the exhaust gas after passing through the dust collector is removed. Since the catalyst has to be reheated to a certain temperature range, the energy is wasted. FIG. 1 shows an example in which a heat storage type heat exchanger with a catalytic function according to the present invention, for example, a Jungstrom type air preheater or the like, in which a heat storage body that continuously exchanges heat by contact with exhaust gas is changed and circulated, is installed in an actual apparatus. It is a process drawing.

【0018】排ガス中のダイオキシン等再合成温度領域
に、Denox触媒あるいは改造Denox触媒と、例
えばユングストローム式空気予熱器の蓄熱体として設置
することにより、該触媒がダイオキシン等の再合成を抑
制すると同時に分解しながら排ガス温度を後段のバグフ
ィルター等の集じん器へ通せる温度まで急激に減温する
ことができるものである。また、触媒はDenox触媒
でもあるので、窒素酸化物自体も分解する。
By installing a Denox catalyst or a modified Denox catalyst, for example, as a heat storage material of a Jungstrom type air preheater in a temperature range for regenerating dioxin in exhaust gas, the catalyst suppresses resynthesis of dioxin and the like at the same time. While decomposing, the exhaust gas temperature can be rapidly reduced to a temperature at which it can be passed through a dust collector such as a bag filter in the subsequent stage. Moreover, since the catalyst is also a Denox catalyst, the nitrogen oxide itself is decomposed.

【0019】以上のように4つの機能を同時に行い得る
複合機能を持った蓄熱式熱交換器である。なお、図1〜
3に示した排ガス温度は、一般的な温度を示したもので
あり、この温度を限定されるものではない。また、上記
においては、ダイオキシン等の毒性有機塩素化合物で説
明したが、本発明はダイオキシン等に限定されるもので
はなく、臭素、ヨウ素、フッ素等のハロゲンを含む有機
ハロゲン化合物も同様に処理することができる。
As described above, the heat storage heat exchanger has a composite function capable of simultaneously performing the four functions. 1 to
The exhaust gas temperature shown in 3 is a general temperature, and the temperature is not limited. Further, in the above description, a toxic organochlorine compound such as dioxin has been described, but the present invention is not limited to dioxin and the like, and an organohalogen compound containing halogen such as bromine, iodine and fluorine may be similarly treated. You can

【0020】[0020]

【実施例】以下、本発明を実施例により具体的に説明す
るが、本発明はこれに限定されるものではない。 実施例1 図4にこの実施例で用いた装置の工程図を示す。図4で
は、本発明の触媒機能付蓄熱式熱交換器を設置した工程
図と、同一条件で実験を行えるように、ダイオキシン等
の再合成温度領域に空気予熱器と水噴霧ガス冷却塔を設
置した場合の工程図で、各々ダクトを取換えて3種類の
実験を行い、効果の差を調べた。
EXAMPLES The present invention will be specifically described below with reference to examples, but the present invention is not limited thereto. Example 1 FIG. 4 is a process diagram of the apparatus used in this example. In FIG. 4, an air preheater and a water atomizing gas cooling tower are installed in the re-synthesis temperature region of dioxins and the like so that the experiment can be performed under the same conditions as the process diagram in which the heat storage heat exchanger with a catalytic function of the present invention is installed. In the process chart of the case, the ducts were replaced and three types of experiments were conducted to examine the difference in effect.

【0021】燃焼対象物はプラスチック系廃棄物で、条
件は廃熱ボイラ出口排ガス温度を350℃、バグフィル
ター入口排ガス温度を200℃まで減温するものとし
た。蓄熱式熱交換器の蓄熱体としての触媒層は、市販の
酸化チタン系の触媒を目開き4.0mmのハニカム成型
体で用いた。この触媒層の空間速度(SV値)は約10
000hr-1とした。ダイオキシン等の分析数値は、
2、3、7、8−TCDDの毒性等価換算濃度(EPA
方式・・・TEQで表示)とした。実験の結果を表1に
示す。
The object of combustion is plastic waste, and the conditions are such that the exhaust gas temperature at the waste heat boiler outlet is reduced to 350 ° C. and the exhaust gas temperature at the bag filter inlet is reduced to 200 ° C. As a catalyst layer as a heat storage body of the heat storage heat exchanger, a commercially available titanium oxide-based catalyst was used in a honeycomb molded body having an opening of 4.0 mm. The space velocity (SV value) of this catalyst layer is about 10
It was set to 000 hr -1 . Analytical values such as dioxin,
Toxic equivalent equivalent concentration of 2, 3, 7, 8-TCDD (EPA
Method ... displayed by TEQ). The results of the experiment are shown in Table 1.

【0022】[0022]

【表1】 [Table 1]

【0023】実験の結果、空気予熱ではダイオキシン等
の毒性等価換算濃度(TEQ)は4.6倍に増加してお
り、明らかにダイオキシン等の再合成が認められた。ガ
ス冷却塔では、ダイオキシン等の再合成が抑制されると
ともに、わずかであるが低減効果が認められた。触媒を
用いた蓄熱式熱交換器では、95%という高い分解能を
示し、再合成を起こす空気予熱器との比較では実に約1
00分の1のオーダーの差が見い出された。
As a result of the experiment, the toxicity equivalent conversion concentration (TEQ) of dioxin and the like increased by 4.6 times in air preheating, and it was clearly recognized that dioxin and the like were resynthesized. In the gas cooling tower, resynthesis of dioxins and the like was suppressed, and a slight reduction effect was observed. The heat storage type heat exchanger using a catalyst shows a high resolution of 95%, which is about 1 in comparison with the air preheater that causes re-synthesis.
A difference of the order of 1/00 was found.

【0024】また、窒素酸化物の低減効果は、当然なが
ら触媒を用いた蓄熱式熱交換器のみにみられ、脱硝率約
65%を得た。なお、この実施例では、ユングストロー
ム式の蓄熱式熱交換器を用いたが、その他に蓄熱式熱交
換器としては、軸流形又は半径流形の回転蓄熱式のも
の、あるいは蓄熱室式のもの等が同様に用いることがで
きる。
As a matter of course, the effect of reducing nitrogen oxides was observed only in the heat storage heat exchanger using the catalyst, and the denitration rate was about 65%. In this embodiment, a Jungstrom type heat storage type heat exchanger was used, but as the heat storage type heat exchanger, an axial flow type or a radial flow type rotary heat storage type, or a heat storage chamber type is used. The same thing can be used.

【0025】[0025]

【発明の効果】本発明は以上のように構成されており、
焼却炉排ガスに含まれる毒性有機ハロゲン化合物を、そ
の再合成温度領域で触媒を用いて減温(熱回収)しなが
ら効果的に除去することに成功したものである。すなわ
ち、毒性有機ハロゲン化合物を分解するとともに、その
再合成温度領域を触媒を通過する間に減温(熱回収)
し、再合成を抑制するものであり、更に、窒素酸化物の
分解も行い得るものである。
The present invention is configured as described above,
It succeeded in effectively removing the toxic organohalogen compound contained in the exhaust gas from the incinerator while reducing the temperature (heat recovery) using a catalyst in the resynthesis temperature range. That is, the toxic organohalogen compound is decomposed, and the temperature is reduced (heat recovery) while passing through the catalyst in its resynthesis temperature range.
However, the re-synthesis is suppressed, and the nitrogen oxides can be decomposed.

【0026】以上四つの機能を同時に行い得る複合機能
を持った蓄熱式熱交換器である。本発明により、最も経
済的でかつ効果も大きく、しかもエネルギー損失もない
革新的な技術を提供できるものである。
A heat storage type heat exchanger having a composite function capable of simultaneously performing the above four functions. INDUSTRIAL APPLICABILITY According to the present invention, it is possible to provide an innovative technology which is the most economical and has a great effect and which does not cause energy loss.

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

【図1】本発明の触媒機能付蓄熱式熱交換器を用いた排
ガス処理装置の工程図。
FIG. 1 is a process diagram of an exhaust gas treating apparatus using a heat storage heat exchanger with a catalytic function of the present invention.

【図2】公知の触媒を用いた排ガス処理装置の一例を示
す工程図。
FIG. 2 is a process diagram showing an example of an exhaust gas treating apparatus using a known catalyst.

【図3】公知の触媒を用いた排ガス処理装置の他の例を
示す工程図。
FIG. 3 is a process diagram showing another example of an exhaust gas treating apparatus using a known catalyst.

【図4】実施例1に用いた実験装置を示す工程図。FIG. 4 is a process diagram showing the experimental apparatus used in Example 1.

【符号の説明】[Explanation of symbols]

1:焼却炉、2:廃熱ボイラ、3:触媒機能付蓄熱式熱
交換器、4:集塵器、5:煙突、6:触媒、7:節炭器
又は空気予熱器、8:水噴霧ガス冷却塔、9:空気
1: incinerator, 2: waste heat boiler, 3: heat storage heat exchanger with catalytic function, 4: dust collector, 5: stack, 6: catalyst, 7: economizer or air preheater, 8: water spray Gas cooling tower, 9: Air

───────────────────────────────────────────────────── フロントページの続き (72)発明者 金子 充良 東京都大田区羽田旭町11番1号 株式会社 荏原製作所内 ─────────────────────────────────────────────────── ─── Continuation of the front page (72) Inventor Mitsuyoshi Kaneko 11-11 Haneda Asahi-cho, Ota-ku, Tokyo Inside EBARA CORPORATION

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 燃焼装置から排出する有機ハロゲン化合
物を含有する排ガスを触媒層を通して分解除去する排ガ
スの処理方法において、前記触媒層が蓄熱式熱交換器の
蓄熱体として設置されていることを特徴とする排ガス処
理方法。
1. A method of treating exhaust gas, which decomposes and removes exhaust gas containing an organic halogen compound discharged from a combustion apparatus through a catalyst layer, wherein the catalyst layer is installed as a heat storage body of a heat storage heat exchanger. Exhaust gas treatment method.
【請求項2】 前記触媒層の触媒が、窒素酸化物除去触
媒であることを特徴とする請求項1記載の排ガス処理方
法。
2. The exhaust gas treatment method according to claim 1, wherein the catalyst of the catalyst layer is a nitrogen oxide removal catalyst.
【請求項3】 前記蓄熱式熱交換器は、冷却側媒体とし
て空気を用い、該加熱された空気を燃焼装置の燃焼用空
気として用いることを特徴とする請求項1又は2記載の
排ガス処理方法。
3. The exhaust gas treatment method according to claim 1, wherein the regenerative heat exchanger uses air as a cooling-side medium and uses the heated air as combustion air for a combustion device. .
【請求項4】 前記触媒層である蓄熱体が、貫通孔の相
当直径が2mm以上で、かつ開口率が50%以上のハニ
カム構造体であることを特徴とする請求項1、2又は3
記載の排ガス処理方法。
4. The heat storage body, which is the catalyst layer, is a honeycomb structure having through holes having an equivalent diameter of 2 mm or more and an opening ratio of 50% or more.
Exhaust gas treatment method described.
【請求項5】 前記蓄熱式熱交換器は、蓄熱体を通る排
ガスと冷却媒体の空気が向流で流れることを特徴とする
請求項3記載の排ガス処理方法。
5. The exhaust gas treatment method according to claim 3, wherein in the heat storage heat exchanger, the exhaust gas passing through the heat storage body and the air of the cooling medium flow in countercurrent.
【請求項6】 前記蓄熱式熱交換器では、排ガス温度を
300℃〜450℃から、150℃〜250℃まで減温
することを特徴とする請求項1〜5のいずれか1項記載
の排ガス処理方法。
6. The exhaust gas according to claim 1, wherein the heat storage heat exchanger reduces the exhaust gas temperature from 300 ° C. to 450 ° C. to 150 ° C. to 250 ° C. Processing method.
JP5256333A 1993-09-21 1993-09-21 Treatment of waste gas containing organohalogen compound Pending JPH0788329A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5256333A JPH0788329A (en) 1993-09-21 1993-09-21 Treatment of waste gas containing organohalogen compound

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5256333A JPH0788329A (en) 1993-09-21 1993-09-21 Treatment of waste gas containing organohalogen compound

Publications (1)

Publication Number Publication Date
JPH0788329A true JPH0788329A (en) 1995-04-04

Family

ID=17291220

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5256333A Pending JPH0788329A (en) 1993-09-21 1993-09-21 Treatment of waste gas containing organohalogen compound

Country Status (1)

Country Link
JP (1) JPH0788329A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0787521A1 (en) * 1995-08-08 1997-08-06 Ebara Corporation Method and apparatus for treating combustion exhaust gases
EP0893153A1 (en) * 1997-07-24 1999-01-27 Siemens Aktiengesellschaft Flue gas line and process of treating flue gas
CN105066149A (en) * 2015-08-13 2015-11-18 中国石油化工股份有限公司 Heat exchange method for low-temperature heat accumulating type catalytic oxidation treatment device

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0787521A1 (en) * 1995-08-08 1997-08-06 Ebara Corporation Method and apparatus for treating combustion exhaust gases
EP0893153A1 (en) * 1997-07-24 1999-01-27 Siemens Aktiengesellschaft Flue gas line and process of treating flue gas
WO1999004888A1 (en) * 1997-07-24 1999-02-04 Apparatebau Rothemühle Brandt + Kritzler Gmbh Flue gas pipe and method for treating flue gas
CN105066149A (en) * 2015-08-13 2015-11-18 中国石油化工股份有限公司 Heat exchange method for low-temperature heat accumulating type catalytic oxidation treatment device
CN105066149B (en) * 2015-08-13 2017-09-22 中国石油化工股份有限公司青岛安全工程研究院 Heat-exchange method for Low Temperature Storage hot type catalytic oxidation treatment device

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