JPH11156157A - Method and apparatus for treatment of exhaust gas of incinerator - Google Patents

Method and apparatus for treatment of exhaust gas of incinerator

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Publication number
JPH11156157A
JPH11156157A JP9323062A JP32306297A JPH11156157A JP H11156157 A JPH11156157 A JP H11156157A JP 9323062 A JP9323062 A JP 9323062A JP 32306297 A JP32306297 A JP 32306297A JP H11156157 A JPH11156157 A JP H11156157A
Authority
JP
Japan
Prior art keywords
exhaust gas
photocatalyst
incinerator
ultraviolet lamp
titanium oxide
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
JP9323062A
Other languages
Japanese (ja)
Inventor
Kazuaki Iijima
和明 飯嶋
Nobuhiko Kikuchi
順彦 菊地
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.)
Sanki Engineering Co Ltd
Original Assignee
Sanki Engineering Co Ltd
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 Sanki Engineering Co Ltd filed Critical Sanki Engineering Co Ltd
Priority to JP9323062A priority Critical patent/JPH11156157A/en
Publication of JPH11156157A publication Critical patent/JPH11156157A/en
Pending legal-status Critical Current

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  • Treating Waste Gases (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Catalysts (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a method and an apparatus for treatment of an exhaust gas of an incinerator wherein maintenance and control are easy without making its equipment and apparatus large-scaled and they are free from influence from fly ash. SOLUTION: An exhaust gas discharged from an incineration ash separator 4 is passed through a photocatalytic device 5 provided by combining a photocatalytic carrier supporting a catalyst having titanium oxide as a principal constituent, and an ultraviolet lamp to remove hazardous material contained in the exhaust gas by decomposition. An exhaust line of an incineration furnace 1 is provided by arranging a cooling device 3, an incineration ash separator 4 and the photocatalytic device 5 in this order, and the photocatalytic device 5 is provided by combining a zigzag pohocatalytic carrier for carrying a catalyst having titanium oxide as main component, and an ultraviolet lamp.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、焼却炉から発生す
る排ガス中に含まれるダイオキシン類を含む有機塩素化
合物等の有害物質を除去する焼却炉の排ガス処理方法及
びその装置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 and an apparatus for treating an exhaust gas of an incinerator for removing harmful substances such as organic chlorine compounds containing dioxins contained in the exhaust gas generated from the incinerator.

【0002】[0002]

【従来の技術】焼却炉から発生する排ガス中に含まれる
ダイオキシン類は、毒性が強く、発生量の低減が求めら
れている。一般に、ダイオキシンとは、75種類の異性
体を持つPCDDs(ポリ塩化ジベンゾ-p- ダイオキシ
ン)や135種類の異性体を持つPCDFs(ポリ塩化
ジベンゾフラン)の総称であり、毒性の強い物質であ
り、更にCP(クロロフェノール)やCB(クロロベン
ゼン)等のPCDDs,PCDFsの前駆物質も含まれ
ている。本発明においては、これらをダイオキシン類と
称する。
2. Description of the Related Art Dioxins contained in exhaust gas generated from incinerators are highly toxic, and it is required to reduce the amount of dioxins generated. In general, dioxin is a general term for PCDDs (polychlorinated dibenzo-p-dioxins) having 75 types of isomers and PCDFs (polychlorinated dibenzofurans) having 135 types of isomers, and is a highly toxic substance. Precursors of PCDDs and PCDFs such as CP (chlorophenol) and CB (chlorobenzene) are also included. In the present invention, these are referred to as dioxins.

【0003】又、廃棄物焼却プラントにおいて、ガスク
ーラ又は反応塔から捕集される灰、電気集塵器またはバ
グフィルタから捕集される灰のような飛灰には、ダイオ
キシン類が微量含まれていることが問題となっている。
飛灰は、これらダイオキシン類生成反応の触媒として作
用し、ダイオキシン類の生成を促進することが知られて
いる。
In a waste incineration plant, fly ash such as ash collected from a gas cooler or a reaction tower or ash collected from an electric dust collector or a bag filter contains a trace amount of dioxins. Is a problem.
Fly ash is known to act as a catalyst for these dioxin-forming reactions and promote the production of dioxins.

【0004】従来、焼却炉においては、燃焼温度を85
0℃以上に安定に焼却することによって、ダイオキシン
類の発生量を抑え、又、排ガスを350℃以下まで急冷
することによって、排ガス中の再生成を防ぎ、更にダス
トフィルタによってダストと共に除去している。然し、
この方法によっても、環境に放出されるダイオキシン類
の量が満足できるものではなかった。
Conventionally, in an incinerator, a combustion temperature of 85
The amount of dioxins generated is suppressed by incineration stably at 0 ° C or higher, and the exhaust gas is quenched to 350 ° C or lower to prevent regeneration in the exhaust gas and further removed together with dust by a dust filter. . But
Even with this method, the amount of dioxins released into the environment was not satisfactory.

【0005】そこで、ダストフィルタの前に活性炭を吹
き込み、活性炭によりダイオキシン類を吸着除去した
り、ダストフィルタの後に活性炭吸着槽を設けて吸着処
理後、この活性炭を再生し、再利用するものが提案され
ている(例えば、特開平7−75720号公報)。又、
酸化チタン触媒を用いたものも提案されている(例え
ば、特開平2−35914号公報、特開平5−3373
36号公報、特公平7−75656号公報、特公平7−
106299号公報、特許第2542290号公報、特
許第2609393号公報)。
[0005] Therefore, it has been proposed to blow activated carbon before the dust filter to adsorb and remove dioxins by the activated carbon, or to provide an activated carbon adsorption tank after the dust filter to perform adsorption treatment, and then regenerate and reuse the activated carbon. (For example, JP-A-7-75720). or,
A catalyst using a titanium oxide catalyst has also been proposed (for example, JP-A-2-35914, JP-A-5-3373).
Japanese Patent Publication No. 36, Japanese Patent Publication No. 7-75656 and Japanese Patent Publication No. 7-75656
No. 106299, Japanese Patent No. 2542290, Japanese Patent No. 2609393).

【0006】[0006]

【発明が解決しようとする課題】然し乍ら、例えば、特
開平7−75720号公報に記載された発明では、活性
炭を再生するか、処理処分する必要があるため、装置が
大きく、複雑となる。又、特開平2−35914号公報
に記載された発明では、除塵された排ガスを150℃以
上、好ましくは170〜300℃の温度で反応容器に導
入するため、運転管理が面倒である。
However, for example, in the invention described in Japanese Patent Application Laid-Open No. 7-75720, it is necessary to regenerate or dispose of activated carbon, so that the apparatus is large and complicated. In the invention described in JP-A-2-35914, since the exhaust gas from which dust has been removed is introduced into the reaction vessel at a temperature of 150 ° C. or higher, preferably 170 to 300 ° C., operation management is troublesome.

【0007】特開平5−337336号公報に記載され
た発明では、助剤としてNH3を連続的又は間欠的に添
加するため、設備費、運転費が嵩むと共に、運転管理が
煩わしいという問題がある。特公平7−75656号公
報に記載された発明では、使用温度範囲が250℃以
上、空間速度が50000以下で、且つ触媒表面積1m
2当たりのガス量が250m3/hr(at temp.)以下とす
るため、運転管理が面倒である。
In the invention described in Japanese Patent Application Laid-Open No. 5-337336, NH 3 is continuously or intermittently added as an auxiliary agent, so that there is a problem that equipment costs and operation costs are increased and operation management is troublesome. . In the invention described in Japanese Patent Publication No. 7-75656, the operating temperature range is 250 ° C. or more, the space velocity is 50000 or less, and the catalyst surface area is 1 m.
Since the gas amount per 2 is 250 m 3 / hr (at temp.) Or less, operation management is troublesome.

【0008】特公平7−106299号公報に記載され
た発明では、集塵部に導入される前で処理するため、飛
灰が触媒に付着し易く、維持管理が困難である。特許第
2542290号公報に記載された発明では、助剤とし
てアンモニアを連続的又は間欠的に添加するため、設備
費、運転費が嵩むと共に、運転管理が煩わしいという問
題がある。
[0008] In the invention described in Japanese Patent Publication No. 7-106299, since the treatment is performed before being introduced into the dust collecting portion, fly ash easily adheres to the catalyst, and maintenance and management are difficult. In the invention described in Japanese Patent No. 2542290, since ammonia is continuously or intermittently added as an auxiliary agent, there is a problem that equipment costs and operation costs are increased and operation management is troublesome.

【0009】特許第2609393号公報に記載された
発明では、使用温度範囲が150〜450℃以上、空間
速度が20000以下で、且つ触媒表面積1m2当たり
のガス量が100m3/hr(at temp.)以下とするた
め、運転管理が面倒である。本発明は斯かる従来の問題
点を解決するためになされたもので、その目的は、設
備、装置を大型化することなく維持管理が容易で飛灰に
よる影響を受けない焼却炉の排ガス処理方法及びその装
置を提供することにある。
In the invention described in Japanese Patent No. 2609393, the operating temperature range is 150 to 450 ° C. or more, the space velocity is 20,000 or less, and the gas amount per 1 m 2 of the catalyst surface area is 100 m 3 / hr (at temp. ) Operation management is troublesome because: The present invention has been made to solve such a conventional problem, and an object of the present invention is to provide an exhaust gas treatment method for an incinerator that is easy to maintain without increasing the size of facilities and equipment and is not affected by fly ash. And an apparatus therefor.

【0010】[0010]

【課題を解決するための手段】請求項1記載の発明は、
焼却灰分離装置から排出される排ガスを、酸化チタンを
主成分とする触媒を担持する光触媒担体と紫外線ランプ
とを組み合わせて成る光触媒装置を通過させ、排ガス中
に含まれる有害物質を分解除去することを特徴とする。
According to the first aspect of the present invention,
Exhaust gas discharged from the incineration ash separation device is passed through a photocatalyst device combining a photocatalyst carrier carrying a catalyst containing titanium oxide as a main component and an ultraviolet lamp to decompose and remove harmful substances contained in the exhaust gas. It is characterized by.

【0011】請求項2記載の発明は、請求項1記載の焼
却炉の排ガス処理方法において、有害物質が、ダイオキ
シン類を含む有機塩素化合物であることを特徴とする。
請求項3記載の発明は、焼却炉の排ガスラインに、冷却
装置、焼却灰分離装置及び光触媒装置を順に配して成
り、光触媒装置は、酸化チタンを主成分とする触媒を担
持する葛折状の光触媒担体と紫外線ランプとを組み合わ
せて成ることを特徴とする。
According to a second aspect of the present invention, in the exhaust gas treatment method for an incinerator according to the first aspect, the harmful substance is an organic chlorine compound containing dioxins.
The invention according to claim 3 is characterized in that a cooling device, an incineration ash separation device, and a photocatalyst device are sequentially arranged in an exhaust gas line of an incinerator, and the photocatalyst device has a concavity-like shape that carries a catalyst containing titanium oxide as a main component. Characterized in that the photocatalyst carrier is combined with an ultraviolet lamp.

【0012】請求項4記載の発明は、請求項3記載の焼
却炉の排ガス処理装置において、光触媒装置は、ハニカ
ム状物又はシートを織り込んだフィルタ状物に酸化チタ
ンを担持して成る光触媒担体を、葛折状に容器内に配す
ると共に、上流側に反射板を設けた紫外線ランプを光触
媒担体の上流側に配して成ることを特徴とする。請求項
5記載の発明は、請求項3記載の焼却炉の排ガス処理装
置において、反射板は、二重構造をなし、内部に清浄空
気の通路が形成されると共に、光触媒装置内の排ガスの
流れ方向に清浄空気を噴出する噴出口が形成されている
ことを特徴とする。
According to a fourth aspect of the present invention, in the exhaust gas treatment device for an incinerator according to the third aspect, the photocatalyst device comprises a photocatalyst carrier comprising titanium oxide supported on a honeycomb-like material or a filter-like material in which sheets are woven. And an ultraviolet lamp provided with a reflector on the upstream side and arranged on the upstream side of the photocatalyst carrier, while being arranged in a container in a distorted manner. According to a fifth aspect of the present invention, in the exhaust gas treatment device for an incinerator according to the third aspect, the reflecting plate has a double structure, a passage for clean air is formed therein, and a flow of exhaust gas in the photocatalytic device. A jet port for jetting clean air in a direction is formed.

【0013】(作用)請求項1乃至請求項3記載の発明
においては、焼却灰分離装置によって飛灰が取り除かれ
た排ガスを、酸化チタンを主成分とする触媒を担持する
光触媒担体と紫外線ランプとを組み合わせて成る光触媒
装置を通過させることによって、排ガス中に含まれる有
害物質を光触媒により分解除去することができる。
(Function) According to the first to third aspects of the present invention, the exhaust gas from which fly ash has been removed by the incineration ash separation device is supplied to a photocatalyst carrier carrying a catalyst mainly composed of titanium oxide and an ultraviolet lamp. The harmful substances contained in the exhaust gas can be decomposed and removed by the photocatalyst by passing through a photocatalyst device comprising a combination of the above.

【0014】光触媒(アナターゼ型のTiO2)の表面
に紫外線を当てると、電子e-と正孔h+が生成する。電
子e-と正孔h+が空気中の水分を分解して過酸化水素と
水酸基ラジカルを生成する。この水酸基ラジカルは強い
酸化力があり、そのエネルギは120kcal/mol
である。多くの結合エネルギは、120kcal/mo
lよりも低いため、光触媒によって分解される。
When ultraviolet rays are applied to the surface of the photocatalyst (TiO 2 of the anatase type), electrons e and holes h + are generated. The electrons e and the holes h + decompose water in the air to generate hydrogen peroxide and hydroxyl radicals. This hydroxyl radical has strong oxidizing power, and its energy is 120 kcal / mol.
It is. Many binding energies are 120 kcal / mo
l, it is decomposed by the photocatalyst.

【0015】ダイオキシン類の代表として、2,3,
7,8−TCDDがある。これが最も毒性が強い。その
化学構造式は、化1に示すように、ベンゼン環2つが2
つの酸素を間にして結合し、又、それぞれ2つの塩素を
結合している。ここで、C−O結合エネルギ70.0k
cal/mol、C−Cl結合エネルギ66.5kca
l/mol、C−H結合エネルギ99.5kcal/m
olであるが、いずれも水酸基ラジカルの酸化エネルギ
120kcal/molよりも低く、分解されることが
考えられる。
As representatives of dioxins, 2,3
There is 7,8-TCDD. This is the most toxic. The chemical structural formula is, as shown in Chemical Formula 1, where two benzene rings are 2
Two oxygens in between and two chlorines each. Here, the C—O binding energy 70.0 k
cal / mol, C-Cl binding energy 66.5 kca
1 / mol, CH bond energy 99.5 kcal / m
ol, the oxidation energy of each of the hydroxyl radicals is lower than 120 kcal / mol, and it can be considered that they are decomposed.

【化1】 請求項4記載の発明においては、光触媒装置が、ハニカ
ム状物又はシートを織り込んだフィルタ状物に酸化チタ
ン触媒から成る光触媒を担持して成る光触媒担体を、葛
折状に容器内に配すると共に、上流側に反射板を設けた
紫外線ランプを光触媒担体の上流側に配することによっ
て構成されているので、排ガスが光触媒担体に接触する
段階で、水酸基ラジカルによって確実に分解することが
できる。
Embedded image In the invention according to claim 4, the photocatalyst device disposes a photocatalyst carrier in which a photocatalyst made of a titanium oxide catalyst is supported on a honeycomb-like material or a filter-like material in which a sheet is woven, and the photocatalyst device is arranged in a container in a cross-shaped manner Since an ultraviolet lamp provided with a reflection plate on the upstream side is arranged on the upstream side of the photocatalyst carrier, the exhaust gas can be surely decomposed by hydroxyl radicals at the stage of contact with the photocatalyst carrier.

【0016】請求項5記載の発明においては、反射板の
内部から光触媒装置内の排ガスの流れ方向に清浄空気を
噴出するので、万一微量の飛灰が混入しても、飛灰を紫
外線ランプに触れさせることなく、排気流に沿って排出
することができる。
According to the fifth aspect of the present invention, since clean air is ejected from the inside of the reflector in the flow direction of the exhaust gas in the photocatalyst device, even if a small amount of fly ash is mixed, the fly ash is discharged by the ultraviolet lamp. Can be discharged along the exhaust flow without touching the air.

【0017】[0017]

【発明の実施の形態】以下、本発明の実施形態を図面に
基づいて説明する。
Embodiments of the present invention will be described below with reference to the drawings.

【0018】図1乃至図3は、本発明に係る焼却炉の排
ガス処理方法及びその装置の第一実施形態を示す(請求
項1乃至請求項4記載の発明に対応)。焼却炉1の排ガ
スライン2には、冷却装置3、バグフィルタ等の焼却灰
分離装置4、光触媒装置5、送風機6及び煙突7が順に
配してある。ここで、焼却炉1、冷却装置3、焼却灰分
離装置4、送風機6、煙突7は公知であるからその説明
は省略する。
FIGS. 1 to 3 show a first embodiment of an incinerator exhaust gas treatment method and apparatus according to the present invention (corresponding to the first to fourth aspects of the present invention). In the exhaust gas line 2 of the incinerator 1, a cooling device 3, an incineration ash separation device 4 such as a bag filter, a photocatalyst device 5, a blower 6, and a chimney 7 are arranged in this order. Here, since the incinerator 1, the cooling device 3, the incineration ash separation device 4, the blower 6, and the chimney 7 are known, their description is omitted.

【0019】光触媒装置5は、排ガス入口11及び排ガ
ス出口12を有する筒状容器から成る反応容器10内
に、反応容器10の排ガス通路を遮るように酸化チタン
を主成分とする触媒を担持する葛折状の光触媒担体20
を間隔をおいて2列配すると共に、各葛折状の光触媒担
体20の上流側に対向して上流側に反射板31を配した
紫外線ランプ30を配している。
The photocatalyst device 5 includes a reaction vessel 10 comprising a cylindrical vessel having an exhaust gas inlet 11 and an exhaust gas outlet 12, which carries a catalyst containing titanium oxide as a main component so as to block the exhaust gas passage of the reaction vessel 10. Folded photocatalyst carrier 20
Are arranged in two rows at an interval, and an ultraviolet lamp 30 is disposed opposite to the upstream side of each of the photocatalyst carriers 20 and has a reflection plate 31 disposed on the upstream side.

【0020】ここで、葛折状の光触媒担体20では、排
ガスが流れるための圧力損失が100mmAqよりも高
くならないように、ハニカム状物又はシートを織り込ん
だフィルタ状物から成る支持部材21が形成されてい
る。又、光触媒担体20は、ハニカム状物又はシートを
織り込んだフィルタ状物から成る支持部材21に、蒸着
(CVD等)、塗布、浸漬等の公知の方法に従って酸化
チタンが担持されている。
Here, in the photocatalyst carrier 20 having a skewed shape, a supporting member 21 made of a honeycomb-like material or a filter-like material in which a sheet is woven is formed so that the pressure loss for flowing the exhaust gas does not become higher than 100 mmAq. ing. In the photocatalyst carrier 20, titanium oxide is supported on a support member 21 made of a honeycomb-like material or a filter-like material in which a sheet is woven according to a known method such as vapor deposition (CVD or the like), coating, and dipping.

【0021】光触媒としては、TiO2を用い、TiO2
に、Pt、Ag、Pd、RuO2、Co34から選ばれ
た一種以上を添加したものが好適に用いることができ
る。尚、光触媒は、通常は、半導体材料が効果的であ
り、入手も容易なので好ましい。効果や経済性の面から
は、Se,Ti,Zn,Cu,Sn,Al,Ga,I
n,P,As,Sb,Bi,Cd,S,Te,Ni,F
e,Co,Ag,Mo,Sr,W,Cr,Pb等の化合
物、合金または酸化物が好ましく、これらは単独で、又
は2種類以上を複合して用いることができる。例えば、
化合物としては、AlP,AlAs,GaP,AlS
b,GaAs,InP,GaSb,InAs,InS
b,CdS,CdSe,ZnS,MoS2 ,WS2,酸
化物としてはTiO2,Bi23,CuO,CuO2,Z
nO,MoO3,InO3,Ag2O,PbO,SrTi
3,BaTiO3,Co34,Fe23,NiO,Ru
2,WO3,ZrOがある。
[0021] As the photocatalyst, using a TiO 2, TiO 2
To which at least one selected from the group consisting of Pt, Ag, Pd, RuO 2 , and Co 3 O 4 is preferably used. Incidentally, the photocatalyst is usually preferable because a semiconductor material is effective and easily available. In terms of effect and economy, Se, Ti, Zn, Cu, Sn, Al, Ga, I
n, P, As, Sb, Bi, Cd, S, Te, Ni, F
Compounds, alloys or oxides such as e, Co, Ag, Mo, Sr, W, Cr, and Pb are preferable, and these can be used alone or in combination of two or more. For example,
Compounds include AlP, AlAs, GaP, AlS
b, GaAs, InP, GaSb, InAs, InS
b, CdS, CdSe, ZnS, MoS 2 , WS 2 , and oxides such as TiO 2 , Bi 2 O 3 , CuO, CuO 2 , Z
nO, MoO 3 , InO 3 , Ag 2 O, PbO, SrTi
O 3 , BaTiO 3 , Co 3 O 4 , Fe 2 O 3 , NiO, Ru
There are O 2 , WO 3 and ZrO.

【0022】紫外線ランプ30は、石英管32に覆われ
ており、反応容器10の壁面においてコネクタを介して
電源に連絡している。ここで、紫外線ランプ30として
は、紫外線を含む光を放射するランプであれば特に限定
されないが、具体的には、低圧水銀ランプが望ましく、
特に波長400nm以下の紫外線を高い効率で放射する
ものが好ましい。
The ultraviolet lamp 30 is covered with a quartz tube 32, and is connected to a power supply via a connector on the wall surface of the reaction vessel 10. Here, the ultraviolet lamp 30 is not particularly limited as long as it emits light including ultraviolet light, and specifically, a low-pressure mercury lamp is desirable.
In particular, those that emit ultraviolet light having a wavelength of 400 nm or less with high efficiency are preferable.

【0023】尚、紫外線ランプ30と石英管32との間
に冷却空気を通気し、ランプ温度を低く維持している。
反射板31は、各葛折状の光触媒担体20の上流側にお
いて紫外線ランプ30と対向して配してある。この反射
板31により、紫外線ランプ30から照射される紫外線
は、葛折状の光触媒担体20に効率良く届くことができ
る。
Cooling air is passed between the ultraviolet lamp 30 and the quartz tube 32 to keep the lamp temperature low.
The reflection plate 31 is arranged on the upstream side of each photocatalyst carrier 20 facing the ultraviolet lamp 30. The reflection plate 31 allows the ultraviolet light emitted from the ultraviolet lamp 30 to efficiently reach the photocatalyst carrier 20 in a skewed shape.

【0024】更に、反応容器10には、点検口13が設
けてある。次に、このように構成された本実施形態に係
る本発明に係る焼却炉の排ガス処理装置を用いた処理方
法について説明する。常法に従って焼却炉1が運転され
ると、焼却炉1の排ガスライン2を介して約800℃の
排ガスが排出される。処で、ダイオキシン類は、800
〜300℃の温度域で再生することから、冷却装置3で
急冷され、焼却灰分離装置4の入口温度が200℃とさ
れる。そして、焼却灰分離装置4では、排ガス中の飛灰
等の固形物を除去する。
Further, the reaction container 10 is provided with an inspection port 13. Next, a treatment method using the thus configured incinerator exhaust gas treatment apparatus according to the present invention according to the present embodiment will be described. When the incinerator 1 is operated according to a conventional method, exhaust gas of about 800 ° C. is discharged through the exhaust gas line 2 of the incinerator 1. Where dioxins are 800
Since it is regenerated in the temperature range of ~ 300 ° C, it is rapidly cooled by the cooling device 3 and the inlet temperature of the incineration ash separation device 4 is set to 200 ° C. The incineration ash separation device 4 removes solids such as fly ash in the exhaust gas.

【0025】その後、排ガスは、排ガス入口11を介し
て光触媒装置5に流入する。光触媒装置5では、酸化チ
タンを主成分とする触媒を担持する葛折状の光触媒担体
20に対して紫外線ランプ30から紫外線が照射され、
光触媒担体20上に電子e-と正孔h+が生成されてい
る。この光触媒担体20上に排ガスが流入すると、排ガ
ス中のダイオキシン類は、光触媒担体20上への紫外線
照射により放出された電子の作用により、CO2、H
2O、HClに分解、除去され、電子の作用で分解され
なかったダイオキシン類は、光触媒担体20を通過する
際に光触媒担体20の表面で分解、除去される。
After that, the exhaust gas flows into the photocatalyst device 5 through the exhaust gas inlet 11. In the photocatalyst device 5, ultraviolet light is irradiated from the ultraviolet lamp 30 to the quasi-shaped photocatalyst carrier 20 that carries a catalyst containing titanium oxide as a main component,
Electrons e and holes h + are generated on the photocatalyst carrier 20. When the exhaust gas flows into the photocatalyst carrier 20, dioxins in the exhaust gas generate CO 2 , H 2 by the action of electrons emitted by the irradiation of the photocatalyst carrier 20 with ultraviolet rays.
Dioxins decomposed and removed into 2 O and HCl and not decomposed by the action of electrons are decomposed and removed on the surface of the photocatalyst carrier 20 when passing through the photocatalyst carrier 20.

【0026】この処理が2回行われた後、排ガスは排ガ
ス出口12から排出され、その後、送風機6を介して煙
突7から大気中へ放出される。以上のように、本実施形
態では、焼却灰分離装置4によって排ガス中の飛灰等の
固形物を除去した後に、光触媒装置5により排ガス中の
ダイオキシン類を除去するので、活性炭を利用したり、
NH3やアンモニウム等の助剤を添加したりする従来法
に比し、無用な後処理が無く、装置が大型化せず、運転
管理が簡単である。
After this process has been performed twice, the exhaust gas is discharged from the exhaust gas outlet 12 and then discharged from the chimney 7 through the blower 6 to the atmosphere. As described above, in the present embodiment, dioxins in the exhaust gas are removed by the photocatalyst device 5 after removing solids such as fly ash in the exhaust gas by the incineration ash separation device 4, so that activated carbon can be used.
Compared with the conventional method in which an auxiliary agent such as NH 3 or ammonium is added, there is no unnecessary post-treatment, the apparatus does not increase in size, and operation management is simple.

【0027】而も、運転管理、保守は、紫外線ランプ3
0の交換が主であり、操作量が低減する。因みに、紫外
線ランプ30の寿命は、約1年である。又、光触媒担体
20は、葛折状をなしているため、排ガスとの接触時間
が長く取れる。而も、2段階での処理が行われるため、
排ガス中のダイオキシン類を確実に分解除去することが
可能となる。
The operation management and maintenance are performed by the ultraviolet lamp 3.
The replacement of 0 is mainly performed, and the operation amount is reduced. Incidentally, the life of the ultraviolet lamp 30 is about one year. In addition, since the photocatalyst carrier 20 is in a distorted shape, the contact time with the exhaust gas can be long. Also, since the processing is performed in two stages,
Dioxins in exhaust gas can be reliably decomposed and removed.

【0028】更に、反射板31が光触媒担体20の上流
側に配設されているので、僅かに混入する虞のある飛灰
が紫外線ランプ30に付着するのを防止することができ
る。従って、飛灰による影響を最小限に止めることがで
きる。尚、本実施形態では、光触媒担体20を2組設け
た場合について説明したが、更に光触媒担体20を併設
しても良い。
Further, since the reflection plate 31 is provided on the upstream side of the photocatalyst carrier 20, it is possible to prevent fly ash which may be slightly mixed from adhering to the ultraviolet lamp 30. Therefore, the effect of fly ash can be minimized. In this embodiment, the case where two sets of the photocatalyst carriers 20 are provided is described, but the photocatalyst carriers 20 may be further provided.

【0029】図4は、本発明に係る焼却炉の排ガス処理
方法及びその装置の第二実施形態を示す(請求項1乃至
請求項5記載の発明に対応)。本実施形態では、僅かに
混入する虞のある飛灰が、紫外線ランプ30に付着し難
くするために、反射板31に飛灰付着防止機構を設けた
ものである。光触媒装置5は、バグフィルタ等の焼却灰
分離装置4の下流側に設けてあるので、基本的には飛灰
の付着は起こらないが、僅かに混入する虞がある。
FIG. 4 shows a second embodiment of an incinerator exhaust gas treatment method and apparatus according to the present invention (corresponding to the first to fifth aspects of the present invention). In the present embodiment, a fly ash adhesion preventing mechanism is provided on the reflection plate 31 in order to make it difficult for fly ash, which may be slightly mixed, to adhere to the ultraviolet lamp 30. Since the photocatalyst device 5 is provided on the downstream side of the incineration ash separation device 4 such as a bag filter, basically, fly ash does not adhere, but there is a possibility that the fly ash may be slightly mixed.

【0030】但し、この飛灰は、粒子径が非常に小さ
く、殆ど慣性力や重力の影響を受けず、空気の流れに伴
われて流れている。そこで、本実施形態では、反射板3
1を二重構造とし、反応容器10の外側に排ガスの流れ
と同等の流速で清浄空気を吹き込むようにした。即ち、
2枚の反射板311と312との間に外部から供給され
る清浄空気の通路33を形成することにより、反射板3
1の上下に長手方向に亘って噴出口34を形成した。こ
こで、上流側の反射板311は反射板312より長く設
定され、両者の間には、排ガスの流れの下流側に向いて
噴出口34が形成されるようになっている。
However, the fly ash has a very small particle diameter, is hardly affected by inertial force or gravity, and flows with the flow of air. Therefore, in the present embodiment, the reflection plate 3
1 has a double structure, and clean air is blown into the outside of the reaction vessel 10 at the same flow rate as the flow of the exhaust gas. That is,
By forming a passage 33 for clean air supplied from the outside between the two reflecting plates 311 and 312, the reflecting plate 3
Spouts 34 were formed over and under one over the longitudinal direction. Here, the upstream reflecting plate 311 is set to be longer than the reflecting plate 312, and a jet port 34 is formed between the two so as to face the downstream side of the flow of the exhaust gas.

【0031】これによって、紫外線ランプ30の回りに
排ガスが直接触れることが無くなり、紫外線ランプ30
に飛灰が付着する虞がなくなる。
As a result, the exhaust gas does not come into direct contact with the periphery of the ultraviolet lamp 30, and the ultraviolet lamp 30
There is no risk of fly ash adhering to the surface.

【0032】[0032]

【発明の効果】以上のように、請求項1乃至請求項5記
載の発明によれば、焼却灰分離装置によって排ガス中の
飛灰等の固形物を除去した後に、光触媒装置によって排
ガス中の有害物質の分解除去を行うので、設備、装置を
大型化することなく維持管理が容易で飛灰による影響を
受けることがない。
As described above, according to the first to fifth aspects of the present invention, after removing solid matter such as fly ash in the exhaust gas by the incineration ash separation device, harmful substances in the exhaust gas are removed by the photocatalytic device. Since the substance is decomposed and removed, maintenance and management are easy without increasing the size of the facilities and equipment, and there is no influence from fly ash.

【0033】請求項5記載の発明によれば、僅かに混入
する虞がある飛灰の紫外線ランプへの付着を確実に阻止
することができる。
According to the fifth aspect of the present invention, it is possible to reliably prevent fly ash, which may be slightly mixed, from adhering to the ultraviolet lamp.

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

【図1】本発明に係る焼却炉の排ガス処理方法及びその
装置の第一実施形態を示す説明図である。
FIG. 1 is an explanatory view showing a first embodiment of an incinerator exhaust gas treatment method and apparatus according to the present invention.

【図2】図1における光触媒装置の説明図である。FIG. 2 is an explanatory diagram of the photocatalyst device in FIG.

【図3】図2における光触媒装置の要部を示す説明図で
ある。
FIG. 3 is an explanatory view showing a main part of the photocatalyst device in FIG. 2;

【図4】本発明に係る焼却炉の排ガス処理方法及びその
装置の第二実施形態を示す説明図である。
FIG. 4 is an explanatory view showing a second embodiment of the method and apparatus for treating exhaust gas in an incinerator according to the present invention.

【符号の説明】[Explanation of symbols]

1 焼却炉 2 排ガスライン 3 冷却装置 4 焼却灰分離装置 5 光触媒装置 6 送風機 7 煙突 10 反応容器 20 光触媒担体 30 紫外線ランプ 31,311,312 反射板 33 通路 34 噴出口 DESCRIPTION OF SYMBOLS 1 Incinerator 2 Exhaust gas line 3 Cooling device 4 Incineration ash separation device 5 Photocatalyst device 6 Blower 7 Chimney 10 Reaction container 20 Photocatalyst carrier 30 Ultraviolet lamp 31, 311, 312 Reflector 33 Passage 34 Spout

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 焼却灰分離装置から排出される排ガス
を、酸化チタンを主成分とする触媒を担持する光触媒担
体と紫外線ランプとを組み合わせて成る光触媒装置を通
過させ、排ガス中に含まれる有害物質を分解除去するこ
とを特徴とする焼却炉の排ガス処理方法。
An exhaust gas discharged from an incineration ash separation device is passed through a photocatalyst device comprising a combination of a photocatalyst carrier carrying a catalyst containing titanium oxide as a main component and an ultraviolet lamp, and harmful substances contained in the exhaust gas. A method for treating exhaust gas in an incinerator, comprising decomposing and removing the waste gas.
【請求項2】 請求項1記載の焼却炉の排ガス処理方法
において、 有害物質が、ダイオキシン類を含む有機塩素化合物であ
ることを特徴とする焼却炉の排ガス処理方法。
2. The exhaust gas treatment method for an incinerator according to claim 1, wherein the harmful substance is an organic chlorine compound containing dioxins.
【請求項3】 焼却炉の排ガスラインに、冷却装置、焼
却灰分離装置及び光触媒装置を順に配して成り、 光触媒装置は、酸化チタンを主成分とする触媒を担持す
る葛折状の光触媒担体と紫外線ランプとを組み合わせて
成ることを特徴とする焼却炉の排ガス処理装置。
3. An incinerator exhaust gas line comprising a cooling device, an incineration ash separation device, and a photocatalyst device arranged in this order, wherein the photocatalyst device has a concavity-shaped photocatalyst carrier carrying a catalyst containing titanium oxide as a main component. And an ultraviolet lamp.
【請求項4】 請求項3記載の焼却炉の排ガス処理装置
において、 光触媒装置は、ハニカム状物又はシートを織り込んだフ
ィルタ状物に酸化チタンを担持して成る光触媒担体を、
葛折状に容器内に配すると共に、上流側に反射板を設け
た紫外線ランプを光触媒担体の上流側に配して成ること
を特徴とする焼却炉の排ガス処理装置。
4. The exhaust gas treatment device for an incinerator according to claim 3, wherein the photocatalyst device comprises a photocatalyst carrier comprising titanium oxide supported on a honeycomb-like material or a filter-like material in which a sheet is woven.
An exhaust gas treatment device for an incinerator, comprising: an ultraviolet lamp having a reflection plate provided on an upstream side and disposed in an upstream side of a photocatalyst carrier while being disposed in a container in a skewed manner.
【請求項5】 請求項3記載の焼却炉の排ガス処理装置
において、 反射板は、二重構造をなし、内部に清浄空気の通路が形
成されると共に、光触媒装置内の排ガスの流れ方向に清
浄空気を噴出する噴出口が形成されていることを特徴と
する焼却炉の排ガス処理装置。
5. The exhaust gas treatment device for an incinerator according to claim 3, wherein the reflection plate has a double structure, has a passage for clean air therein, and cleans in a flow direction of the exhaust gas in the photocatalyst device. An exhaust gas treatment device for an incinerator, wherein an exhaust port for ejecting air is formed.
JP9323062A 1997-11-25 1997-11-25 Method and apparatus for treatment of exhaust gas of incinerator Pending JPH11156157A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9323062A JPH11156157A (en) 1997-11-25 1997-11-25 Method and apparatus for treatment of exhaust gas of incinerator

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9323062A JPH11156157A (en) 1997-11-25 1997-11-25 Method and apparatus for treatment of exhaust gas of incinerator

Publications (1)

Publication Number Publication Date
JPH11156157A true JPH11156157A (en) 1999-06-15

Family

ID=18150675

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9323062A Pending JPH11156157A (en) 1997-11-25 1997-11-25 Method and apparatus for treatment of exhaust gas of incinerator

Country Status (1)

Country Link
JP (1) JPH11156157A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2001019515A1 (en) * 1999-09-09 2001-03-22 Hitachi Zosen Corporation Catalyst with discharge electrode or carrier
CN107899389A (en) * 2017-12-13 2018-04-13 北京中能天诚节能环保技术有限公司 The energy saving hybrid processing system of Industrial Stoves VOC exhaust gas
CN108211784A (en) * 2018-03-19 2018-06-29 西安建筑科技大学 A kind of purifier of high penetration support type axial direction photocatalysis treatment pernicious gas
GB2551468B (en) * 2016-04-13 2021-03-10 White Gary Photocatalytic air Purifier

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2001019515A1 (en) * 1999-09-09 2001-03-22 Hitachi Zosen Corporation Catalyst with discharge electrode or carrier
GB2551468B (en) * 2016-04-13 2021-03-10 White Gary Photocatalytic air Purifier
CN107899389A (en) * 2017-12-13 2018-04-13 北京中能天诚节能环保技术有限公司 The energy saving hybrid processing system of Industrial Stoves VOC exhaust gas
CN108211784A (en) * 2018-03-19 2018-06-29 西安建筑科技大学 A kind of purifier of high penetration support type axial direction photocatalysis treatment pernicious gas

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