JPH06334A - Filter for dust removal and denitration - Google Patents

Filter for dust removal and denitration

Info

Publication number
JPH06334A
JPH06334A JP4156479A JP15647992A JPH06334A JP H06334 A JPH06334 A JP H06334A JP 4156479 A JP4156479 A JP 4156479A JP 15647992 A JP15647992 A JP 15647992A JP H06334 A JPH06334 A JP H06334A
Authority
JP
Japan
Prior art keywords
denitration
exhaust gas
dust
filter
dust removal
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
JP4156479A
Other languages
Japanese (ja)
Inventor
Norio Maki
教雄 牧
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.)
Kurabo Industries Ltd
Kurashiki Spinning Co Ltd
Original Assignee
Kurabo Industries Ltd
Kurashiki Spinning 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 Kurabo Industries Ltd, Kurashiki Spinning Co Ltd filed Critical Kurabo Industries Ltd
Priority to JP4156479A priority Critical patent/JPH06334A/en
Publication of JPH06334A publication Critical patent/JPH06334A/en
Pending legal-status Critical Current

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Landscapes

  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Catalysts (AREA)
  • Processes For Solid Components From Exhaust (AREA)
  • Treating Waste Gases (AREA)
  • Filtering Materials (AREA)

Abstract

PURPOSE:To carry out a dust removal and a denitration collectively without need of a wide installing area by attaching a bag filter to a honeycomb style supportor supporting a denitration catalyst and treating a waste gas to be treated which is formed by mixing ammonia into a waste gas contg. soot and dust and nitrogen oxides. CONSTITUTION:A bag filter 2 consisting of a wavon fabric or non-wavon fabric of fiber is attached to an inside or an outside honeycomb style supporter 1 made of titanium oxide, zeolite, etc., supporting a denitration catalist made of gold, platinum, etc. By using the filter for the dust removal and the denitration, waste gas contg. the soot and dust and the nitrogen oxides is further injected with ammonia for a denitration and is treated. Thus, the dust removal and the denitration are collectively carried out and lowering of a denitration efficiency caused by attachment and sedimentation of the soot and the dust is prevented, and a soot and a dust attached to the filter are cleaned and removed.

Description

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

【0001】[0001]

【産業上の利用分野】この発明は、除塵能と脱硝能を兼
有する排ガス処理用のフィルターに関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a filter for treating exhaust gas which has both dust removing ability and denitrifying ability.

【0002】一般家庭や各種の工場等から排出される多
量のごみや産業廃棄物等の焼却炉からの排ガスには媒塵
のほかに窒素酸化物等の有害成分を含んでおり、該排ガ
スの処理は重要な問題となっている。従来から一般的に
使用されている比較的処理効率の高い排ガス処理装置
は、図6に示すように、脱硝装置(12)および金属製網
状保持体(11)に装着したバッグフィルター(2)を具備
する除塵装置(13)から構成されているために、広い設
置面積を必要とするだけでなく、脱硝装置と除塵装置を
個々独立に制御しなければならず、操作が複雑になると
いう問題がある。
Exhaust gas discharged from incinerators such as large amounts of dust and industrial waste discharged from general households and various factories contains harmful substances such as nitrogen oxides in addition to dust particles. Processing has become an important issue. As shown in FIG. 6, an exhaust gas treatment apparatus which has been used generally in the past and has a relatively high treatment efficiency includes a denitration device (12) and a bag filter (2) attached to a metal net-like holder (11). Since it is composed of the dust remover (13) provided, there is a problem that not only a large installation area is required, but also the denitration device and the dust remover must be individually controlled, which makes the operation complicated. is there.

【0003】このような問題の一つの解決策として、無
機質繊維に脱硝触媒(酸化チタン)をコーティングして成
る燃焼排ガス処理用触媒フィルターを使用して、媒塵や
窒素酸化物を一括処理する技術が提案されている(特開
平3−221146号公報参照)。しかしながら、この
種のフィルターを使用する場合には、繊維表面上への媒
塵の付着堆積によって除塵効率だけでなく、脱硝効率も
低下し、しかも、付着堆積した媒塵を除去するフィルタ
ーの清掃に際して、触媒層の剥離や離脱防止の観点か
ら、十分な風圧や機械的な振動をフィルターに加えるこ
とができない等の理由から、十分な清掃ができないとい
う難点がある。また、該フィルター自体には十分な保形
性がないので、使用に際しては、別に保持体を併用しな
ければならない。
As one of the solutions to such a problem, a technology for collectively treating dust particles and nitrogen oxides by using a catalyst filter for treating combustion exhaust gas, which is formed by coating a denitration catalyst (titanium oxide) on an inorganic fiber Has been proposed (see Japanese Patent Laid-Open No. 3-221146). However, when using this type of filter, not only the dust removal efficiency but also the denitrification efficiency decreases due to the adhesion and accumulation of dust particles on the fiber surface, and in addition, when cleaning the filter to remove the accumulated dust particles. However, from the viewpoint of preventing peeling and separation of the catalyst layer, there is a drawback that sufficient cleaning cannot be performed because sufficient wind pressure or mechanical vibration cannot be applied to the filter. Further, since the filter itself does not have a sufficient shape-retaining property, it is necessary to additionally use a holder during use.

【0004】[0004]

【発明が解決しようとする課題】この発明は当該分野に
おける上記の事情に鑑み、広い設置面積を必要とせずに
除塵と脱硝を一括しておこなうことができるだけでな
く、媒塵の付着堆積による脱硝効率の低下がなく、しか
も、十分に清掃でき、また別に保持体を必要としない排
ガス処理用のフィルターを提供するためになされたもの
である。
SUMMARY OF THE INVENTION In view of the above situation in the field, the present invention is not only capable of performing dust removal and denitration collectively without requiring a large installation area, but also denitration by deposition of dust particles. The purpose of the present invention is to provide a filter for treating exhaust gas that does not have a decrease in efficiency, can be sufficiently cleaned, and does not require a holder.

【0005】[0005]

【課題を解決するための手段】即ちこの発明は、脱硝触
媒を担持したハニカム状保持体にバッグフィルターを装
着して成る除塵脱硝フィルターに関する。
That is, the present invention relates to a dust-removing denitration filter comprising a bag-like filter mounted on a honeycomb-shaped holding body carrying a denitration catalyst.

【0006】以下、本発明を、本発明の好適な実施態様
を示す添付図に基づいて説明する。図1は、本発明によ
る除塵脱硝フィルターの一態様を示す平面図である。図
2は、図1のA−A線より見た模式的な立面図である。
図3は図2の部分的な拡大展開立面図である。図4は、
本発明による除塵脱硝フィルターを具備したパルスジェ
ット型の排ガス処理装置の模式的な構成図である。図5
は、本発明による除塵脱硝フィルターを具備した逆圧払
落し型の排ガス処理装置の模式的な構成図である。
The present invention will be described below with reference to the accompanying drawings showing preferred embodiments of the present invention. FIG. 1 is a plan view showing an embodiment of the dust removal denitration filter according to the present invention. FIG. 2 is a schematic elevation view seen from the line AA of FIG.
FIG. 3 is a partially enlarged exploded elevational view of FIG. Figure 4
FIG. 1 is a schematic configuration diagram of a pulse jet type exhaust gas treatment apparatus equipped with a dust removal denitration filter according to the present invention. Figure 5
FIG. 1 is a schematic configuration diagram of a reverse pressure blow-off type exhaust gas treatment apparatus equipped with a dust removal denitration filter according to the present invention.

【0007】本発明による除塵脱硝フィルターは、脱硝
触媒を担持したハニカム状保持体(1)にバッグフィルタ
ー(2)を装着して構成される。排ガスをパルスジェット
方式で処理する場合には、ハニカム状保持体(1)の外側
にバッグフィルター(2)を装着するが(図4参照)、排ガ
スを逆圧払落し方式で処理する場合には、ハニカム状保
持体(1)の内側にバッグフィルター(2)を装着する(図
5参照)。
The dedusting denitration filter according to the present invention is constructed by mounting a bag filter (2) on a honeycomb-shaped holder (1) carrying a denitration catalyst. When the exhaust gas is processed by the pulse jet method, the bag filter (2) is attached to the outside of the honeycomb-shaped holder (1) (see FIG. 4), but when the exhaust gas is processed by the reverse pressure blow-off method. The bag filter (2) is attached to the inside of the honeycomb-shaped holder (1) (see FIG. 5).

【0008】ハニカム状保持体(1)に担持する脱硝触媒
としては、従来から排ガスの脱硝処理に使用されている
触媒、例えば、金、白金、パラジウム、酸化ケイ素、酸
化アルミニウム、酸化チタン、酸化鉄、酸化銅、酸化バ
ナジウム、酸化マンガン、酸化クロム、酸化モリブデン
および酸化タングステン等から成る群から選択される1
種または2種以上の触媒を適宜使用すればよい。脱硝触
媒の担持量は、触媒の種類や触媒活性、担体の種類およ
び排ガス中の窒素酸化物の濃度等に応じて適定すればよ
いが、通常は0.1〜50重量%である。
The denitration catalyst supported on the honeycomb-shaped holder (1) is a catalyst that has been conventionally used for denitration treatment of exhaust gas, for example, gold, platinum, palladium, silicon oxide, aluminum oxide, titanium oxide, iron oxide. , Copper oxide, vanadium oxide, manganese oxide, chromium oxide, molybdenum oxide, tungsten oxide and the like 1
One kind or two or more kinds of catalysts may be appropriately used. The amount of the denitration catalyst supported may be appropriately determined depending on the type of catalyst, catalytic activity, type of carrier, concentration of nitrogen oxides in the exhaust gas, etc., but is usually 0.1 to 50% by weight.

【0009】上記の触媒が担持されるハニカム状保持体
(1)の材質としてはゼオライト、シリカ、アルミナおよ
び酸化チタン等が例示されるが、保持強度や比表面積等
の観点からは酸化チタン、ゼオライトが好ましい。
Honeycomb-shaped holder on which the above catalyst is supported
Examples of the material of (1) include zeolite, silica, alumina, titanium oxide and the like, but titanium oxide and zeolite are preferable from the viewpoint of holding strength and specific surface area.

【0010】脱硝触媒を担持したハニカム状保持体(1)
の一般的な製造法は、酸化チタンやゼオライト等の担体
粉末(粒径は特に限定的ではないが、通常は0.1μm〜
1mmである)に、上記の金属酸化物等の触媒を混合し、
所定のハニカム形状に加圧成形後、焼成する方法であ
る。
Honeycomb support (1) carrying a denitration catalyst
The general production method of the carrier powder is a carrier powder such as titanium oxide or zeolite (the particle size is not particularly limited, but usually 0.1 μm to
1 mm) and a catalyst such as the above metal oxide are mixed,
This is a method of press-molding into a predetermined honeycomb shape and then firing.

【0011】保持体(1)のハニカムの立面形態は通常は
矩形または菱形であり、該ハニカムは保持体(1)の中心
に向ってガス通過面積が減少する構造を有するので、図
4に示すようなパルスジェット方式で排ガスを処理する
場合には、被処理ガスは進行に伴ってその流速は増大
し、従って分子拡散を増大させるので、脱硝効率を向上
させる。
The honeycomb of the holder (1) is usually in a rectangular or rhombic shape, and the honeycomb has a structure in which the gas passage area decreases toward the center of the holder (1). When the exhaust gas is treated by the pulse jet method as shown, the flow rate of the gas to be treated increases as it progresses, and therefore the molecular diffusion increases, so that the denitration efficiency is improved.

【0012】保持体(1)の寸法、例えば内径(図1の
K)、外径(図1のL)、触媒層の奥行き、触媒層の厚
さ、全周分割数、貫通孔の外周部ピッチ(図3のa)、貫
通孔の内周部ピッチ(図3のb)、貫通孔の外周辺(図3の
c)、貫通孔の内周辺(図のd)、触媒層ユニットの高さ、
触媒層段数および貫通孔の相当直径(=孔断面積×4/
孔内周長さ)等は被処理排ガス量、排ガス中の窒素酸化
物の濃度、触媒活性、比表面積および保持強度等に応じ
て適宜選定すればよく、特に限定的ではないが、常用さ
れる寸法は以下の通りである。
Dimensions of the holding body (1), for example, inner diameter (K in FIG. 1), outer diameter (L in FIG. 1), depth of catalyst layer, thickness of catalyst layer, total circumferential division number, outer peripheral portion of through hole Pitch (a in FIG. 3), inner peripheral pitch of the through hole (b in FIG. 3), outer periphery of the through hole (in FIG. 3)
c), the inner periphery of the through hole (d in the figure), the height of the catalyst layer unit,
Number of catalyst layers and equivalent diameter of through holes (= hole cross-sectional area x 4 /
(Hole inner peripheral length) and the like may be appropriately selected according to the amount of exhaust gas to be treated, the concentration of nitrogen oxides in the exhaust gas, the catalytic activity, the specific surface area and the retention strength, etc., but are not particularly limited, but are commonly used. The dimensions are as follows.

【0013】内径:10〜500mm 外径:20〜500mm 触媒層の奥行き:5〜100mm 触媒層の厚さ:0.1〜5mm 全周分割数:4〜100分割/1周 貫通孔の外周部ピッチ:3〜75mm 貫通孔の内周部ピッチ:2〜70mm 貫通孔の外周辺:2〜75mm 貫通孔の内周辺:1〜70mm 触媒層ユニットの高さ:50〜1000mm 触媒層の段数:1〜10 貫通孔の相当直径(排ガス入口側):1〜75mm 貫通孔の相当直径(排ガス出口側):1〜75mmInner diameter: 10 to 500 mm Outer diameter: 20 to 500 mm Depth of catalyst layer: 5 to 100 mm Thickness of catalyst layer: 0.1 to 5 mm Total number of divisions: 4 to 100 divisions / one rotation Outer periphery of through hole Pitch: 3 to 75 mm Inner circumference of through hole Pitch: 2 to 70 mm Outer periphery of through hole: 2 to 75 mm Inner periphery of through hole: 1 to 70 mm Height of catalyst layer unit: 50 to 1000 mm Number of steps of catalyst layer: 1 -10 Equivalent diameter of through hole (exhaust gas inlet side): 1 to 75 mm Equivalent diameter of through hole (exhaust gas outlet side): 1 to 75 mm

【0014】上記の保持体(1)の外側または内側に装着
されるバッグフィルター(2)としては、従来から焼却炉
の排ガスの除塵に常用されているバッグフィルター、例
えば、材質が無機質繊維、テフロン、耐熱ナイロン、ポ
リイミド、炭素繊維、ステンレスおよび上記の混合物で
あり、織布また不織布にしたバッグフィルターを適宜使
用すればよい。
The bag filter (2) mounted on the outer side or the inner side of the holding body (1) is a bag filter conventionally used for dust removal of exhaust gas from incinerators, for example, inorganic fiber or Teflon. , Heat-resistant nylon, polyimide, carbon fiber, stainless steel and a mixture of the above, and a woven or non-woven bag filter may be appropriately used.

【0015】本発明による上記の除塵脱硝フィルターの
使用態様は、第4図に示すようなパルスジェット型の使
用態様と第5図に示すような逆圧払落し型の使用態様に
大別される。
The usage of the above-mentioned dust removal denitration filter according to the present invention is roughly classified into the usage of the pulse jet type as shown in FIG. 4 and the usage of the reverse pressure blow-off type as shown in FIG. .

【0016】図4に示すパルスジェット型の場合には、
焼却炉(図示せず)から排出される排ガス(温度は通常約
500〜100℃に調整され、100℃よりも低くなる
と触媒活性の低下がもたらされる)にアンモニア注入口
(4)から脱硝用アンモニアが注入され、該混合ガス(ア
ンモニアの濃度は窒素酸化物濃度に対応して注入される
が、通常0〜1000ppmである)は排ガス導入口
(7)から排ガス処理装置本体内へ導入され、該装置本体
内に配設されたハニカム状の保持体(1)の外側にバッグ
フィルター(2)を装着して成る除塵脱硝フィルターを通
過後、排ガス排出口(8)から系外へ排出される。排ガス
の除塵と脱硝を単一のフィルターによっておこなうこと
ができるので、従来装置(図6参照)の場合のような脱硝
装置を別設する必要はない。除塵脱硝フィルターはサポ
ーター(3)によって支持される。バッグフィルター(2)
の目詰りが生じたときには、エアーコンプレッサー(6)
から圧搾空気を除塵脱硝フィルターの内側へ送給するこ
とによって、バッグフィルター(2)に付着したダストを
払い落とし、該ダストはダスト排出口(10)から系外へ
排出される。また、省エネルギー、省資源および環境汚
染防止等の観点からフィルターで処理後の排ガスの一部
を、空気導入口(9)から導入される空気と共に、ファン
(5)を用いて処理ラインに再循環させ、これを被処理排
ガスの冷却に利用すると同時に、残存するアンモニアの
一部を再利用することができる。
In the case of the pulse jet type shown in FIG. 4,
The exhaust gas discharged from the incinerator (not shown) (the temperature is usually adjusted to about 500 to 100 ° C and the catalytic activity is lowered when the temperature is lower than 100 ° C), the ammonia inlet is provided.
Ammonia for denitration is injected from (4), and the mixed gas (the concentration of ammonia is injected corresponding to the concentration of nitrogen oxides, usually 0 to 1000 ppm) is the exhaust gas inlet.
After passing through the dust removal denitration filter which is introduced from (7) into the main body of the exhaust gas treatment device and is equipped with the bag filter (2) on the outside of the honeycomb-shaped holding body (1) disposed in the main body of the device, It is discharged from the exhaust gas discharge port (8) to the outside of the system. Since dust removal and denitration of exhaust gas can be performed by a single filter, it is not necessary to separately provide a denitration device as in the case of the conventional device (see FIG. 6). The dedusting denitration filter is supported by the supporter (3). Bag filter (2)
When the clogging of the occurs, the air compressor (6)
By sending the compressed air from the inside to the dust removing denitration filter, the dust adhering to the bag filter (2) is wiped off, and the dust is discharged from the dust discharge port (10) to the outside of the system. In addition, from the viewpoint of energy saving, resource saving and environmental pollution prevention, a part of the exhaust gas after being treated with a filter is used together with the air introduced from the air inlet (9) and the fan.
By using (5), it is possible to recirculate it to the treatment line and use it for cooling the exhaust gas to be treated, and at the same time, reuse part of the remaining ammonia.

【0017】排ガスの系内での流速は、保持体(1)の形
態や寸法、バッグフィルターの型式、被処理排ガス量、
排ガス中のダストや窒素酸化物の量および触媒活性等に
よって左右され、特に限定的ではないが、上述の形態や
寸法を有する保持体やバッグフィルターを使用する場合
に通常採用される流速は次の通りである: 排ガス導入口での流速:0.1〜5m/min 排ガス排出口での流速:0.1〜5m/min 触媒層でのSV:50〜30,000hr-1 平均濾過速度:0.1〜5m/min
The flow velocity of the exhaust gas in the system depends on the form and size of the holder (1), the type of bag filter, the amount of exhaust gas to be treated,
It depends on the amount of dust and nitrogen oxides in the exhaust gas and the catalytic activity, and is not particularly limited, but the flow rate that is usually adopted when using a holder or bag filter having the above-described form and dimensions is as follows. Is as follows: Flow rate at exhaust gas inlet: 0.1-5 m / min Flow rate at exhaust gas outlet: 0.1-5 m / min SV in catalyst bed: 50-30,000 hr -1 Average filtration rate: 0 1 to 5 m / min

【0018】図5に示す逆圧払落し型の排ガス処理装置
は、ハニカム状保持体(1)の内側にバッグフィルター
(2)を装着して成る除塵脱硝フィルターがボトムプレー
ト(14)によって支持されて配設された濾過室(16)、
濾過緊張室(17)およびホッパー(15)から構成される
排ガス処理装置本体が、ダンパー(18)を介して並列的
に3ユニット連接されたものであり、排ガスを濾過する
工程とバッグフィルター(2)に付着したダストを払落す
逆圧工程が交互におこなわれ、排ガスが連続的に処理さ
れる(図5では、右側と中側のユニットは濾過中の状態
を示し、左側のユニットは逆圧中の状態を示す)。この
態様の場合には、アンモニア注入口(4)から注入された
アンモニアを含む被処理排ガスは排ガス導入口(7)から
ホッパー(15)内を経て、バッグフィルター(2)の内側
から保持体(1)へ送給され、除塵と脱硝処理を付された
後、濾過緊張室(17)を経て、排ガス排出口(8)から系
外へ排出される。この場合も、空気導入口(9)から導入
される空気と共に、処理された排ガスの一部を再循環さ
せ、これを被処理排ガスの冷却に利用すると共に、残存
するアンモニアの一部を再利用することができる。な
お、目詰まりしたバッグフィルター(2)からのダストの
払落しは、ファン(5)からの逆圧によっておこなわれ
る。
The reverse pressure blow-off type exhaust gas treating apparatus shown in FIG. 5 has a bag filter inside the honeycomb-shaped holder (1).
A filtration chamber (16) in which a dust removal denitration filter formed by mounting (2) is supported and arranged by a bottom plate (14),
The main body of the exhaust gas treatment device including the filtration tension chamber (17) and the hopper (15) is connected in parallel through the damper (18) in three units. The process for filtering the exhaust gas and the bag filter (2) The reverse pressure step of removing the dust adhering to) is performed alternately, and the exhaust gas is continuously treated (in Fig. 5, the right and middle units indicate the state of filtering, the left unit the reverse pressure). State). In the case of this embodiment, the treated exhaust gas containing ammonia injected from the ammonia inlet (4) passes from the exhaust gas inlet (7) into the hopper (15), and then from the inside of the bag filter (2) to the holder ( After being sent to 1) and subjected to dust removal and denitration treatment, it is discharged from the exhaust gas discharge port (8) to the outside of the system through the filtration tension chamber (17). Also in this case, a part of the treated exhaust gas is recirculated together with the air introduced from the air introduction port (9), and this is used for cooling the exhaust gas to be treated and a part of the remaining ammonia is reused. can do. The dust from the clogged bag filter (2) is removed by the back pressure from the fan (5).

【0019】図5に示す態様の場合も、排ガスの系内の
流速は特に限定的ではないが、上述の形態や寸法を有す
る保持体やバッグフィルターを使用する場合に通常採用
される流速は次の通りである: 排ガス導入口での流速:0.1〜5m/min 排ガス排出口での流速:0.1〜5m/min 触媒層でのSV:50〜30,000hr-1 平均濾過速度:0.1〜5m/min
In the case of the embodiment shown in FIG. 5 as well, the flow rate of exhaust gas in the system is not particularly limited, but the flow rate normally adopted when using the holder or bag filter having the above-described form and dimensions is as follows. As follows: Flow rate at exhaust gas inlet: 0.1-5 m / min Flow rate at exhaust gas outlet: 0.1-5 m / min SV in catalyst bed: 50-30,000 hr -1 Average filtration rate: 0.1-5m / min

【0020】[0020]

【実施例】以下本発明を実施例によって説明する実施例1〜6 下記の調製法に従って、図1〜図3に示す形態および以
下の表1または表2に示す寸法を有し、脱硝触媒として
酸化バナジウム、酸化銅、酸化アルミニウム、酸化タン
グステンが担持された酸化チタン製のハニカム状保持体
を得た。保持体の調製法: 脱硝触媒として、V534wt
%、CuO15wt%、WO31wt%およびγ−Al2
350wt%の混合物を担体の酸化チタンと混合し、乾
燥後400℃で30分間焼成した。焼成後の触媒の担持
量は10wt%であった。
EXAMPLES Examples 1 to 6 for explaining the present invention by way of examples In accordance with the following preparation methods, the denitration catalysts having the configurations shown in FIGS. A honeycomb-shaped holding body made of titanium oxide supporting vanadium oxide, copper oxide, aluminum oxide, and tungsten oxide was obtained. Preparation method of support: As denitration catalyst, V 2 O 5 34 wt
%, CuO 15 wt%, WO 3 1 wt% and γ-Al 2 O
The 3 50 wt% of the mixture is mixed with titanium oxide carrier was baked for 30 minutes at 400 ° C. after drying. The supported amount of the catalyst after firing was 10 wt%.

【0021】得られたハニカム状保持体の外側または内
側にバッグフィルター(材質:ガラスクロス)を装着して
なる除塵脱硝フィルターを図4に示すパルスジェット型
排ガス処理装置(実施例1〜3)または図5に示す逆圧払
落し型排ガス処理装置(実施例4〜6)に組み込み、焼却
炉からの排ガスにアンモニアを100〜500ppm含有
させた被処理排ガスをこれらの装置を使用して処理し
た。排ガスの処理条件並びに脱硝率および除塵率を以下
の表1および表2に示す。
A pulse jet type exhaust gas treating apparatus (Examples 1 to 3) shown in FIG. 4 is a dust removing denitration filter in which a bag filter (material: glass cloth) is attached to the outside or inside of the obtained honeycomb-shaped holder. The apparatus was incorporated into the reverse pressure blow-off type exhaust gas treatment apparatus (Examples 4 to 6) shown in FIG. 5, and the treated exhaust gas containing 100 to 500 ppm of ammonia in the exhaust gas from the incinerator was treated using these apparatuses. The exhaust gas treatment conditions and the denitration rate and dust removal rate are shown in Tables 1 and 2 below.

【0022】[0022]

【表1】 [Table 1]

【0023】[0023]

【表2】 [Table 2]

【0024】[0024]

【発明の効果】本発明によれば、広い設置面積を必要と
せずに除塵と脱硝を一括しておこなうことができるだけ
でなく、媒塵の付着堆積による脱硝効率の低下がなく、
しかもフィルターに付着した媒塵の十分な除去清掃が可
能となり、また、保持体を別設する必要もない。
EFFECTS OF THE INVENTION According to the present invention, it is possible to perform dust removal and denitration collectively without requiring a large installation area, and there is no reduction in denitration efficiency due to deposition of dust particles.
Moreover, it becomes possible to sufficiently remove and clean the dust particles adhering to the filter, and it is not necessary to separately provide a holder.

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

【図1】 本発明による除塵脱硝フィルターの一態様を
示す平面図である。
FIG. 1 is a plan view showing an embodiment of a dust removal denitration filter according to the present invention.

【図2】 図1のA−A線より見た模式的な立面図であ
る。
FIG. 2 is a schematic elevation view seen from the line AA of FIG.

【図3】 図2の部分的な拡大展開立面図である。3 is a partially enlarged exploded elevational view of FIG.

【図4】 本発明による除塵脱硝フィルターを具備した
パルスジェット型の排ガス処理装置の模式的な構成図で
ある。
FIG. 4 is a schematic configuration diagram of a pulse jet type exhaust gas treatment apparatus equipped with a dust removal denitration filter according to the present invention.

【図5】 本発明による除塵脱硝フィルターを具備した
逆圧払落し型の排ガス処理装置の模式的な構成図であ
る。
FIG. 5 is a schematic configuration diagram of a reverse pressure blow-off type exhaust gas treatment apparatus equipped with a dust removal and denitration filter according to the present invention.

【図6】 バッグフィルターを具備した従来の排ガス処
理装置の模式的な構成図である。
FIG. 6 is a schematic configuration diagram of a conventional exhaust gas treatment apparatus equipped with a bag filter.

【符号の説明】[Explanation of symbols]

1 ハニカム状保持体 2 バッグフィルター 3 サポーター 4 アンモニア注入口 5 ファン 6 エアーコンプレッサー 7 排ガス導入口 8 排ガス排出口 9 空気導入口 10 ダスト排出口 11 金属製網状保持体 12 脱硝装置 13 除塵装置 14 ボトムプレート 15 ホッパー 16 濾過室 17 濾過緊張室 18 ダンパー 1 Honeycomb-shaped holder 2 Bag filter 3 Supporter 4 Ammonia inlet 5 Fan 6 Air compressor 7 Exhaust gas inlet 8 Exhaust gas outlet 9 Air inlet 10 Dust outlet 11 Metal mesh holder 12 Denitration device 13 Dust remover 14 Bottom plate 15 Hopper 16 Filtration chamber 17 Filtration tension chamber 18 Damper

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 脱硝触媒を担持したハニカム状保持体
(1)にバッグフィルター(2)を装着して成る除塵脱硝フ
ィルター。
1. A honeycomb-shaped holding body carrying a denitration catalyst.
A dust-removing denitration filter comprising a bag filter (2) attached to (1).
【請求項2】 媒塵と窒素酸化物を含有する排ガスにア
ンモニアを混入した被処理排ガスを、請求項1記載の除
塵脱硝フィルターを用いて処理することを特徴とする排
ガス処理方法。
2. A method for treating exhaust gas, which comprises treating an exhaust gas to be treated in which ammonia is mixed with an exhaust gas containing dust and nitrogen oxides, by using the dust-removal denitration filter according to claim 1.
【請求項3】 処理後の排ガスの一部を処理ラインに再
循環させる請求項2記載の排ガス処理方法。
3. The exhaust gas treatment method according to claim 2, wherein a part of the treated exhaust gas is recirculated to the treatment line.
JP4156479A 1992-06-16 1992-06-16 Filter for dust removal and denitration Pending JPH06334A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4156479A JPH06334A (en) 1992-06-16 1992-06-16 Filter for dust removal and denitration

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4156479A JPH06334A (en) 1992-06-16 1992-06-16 Filter for dust removal and denitration

Publications (1)

Publication Number Publication Date
JPH06334A true JPH06334A (en) 1994-01-11

Family

ID=15628660

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4156479A Pending JPH06334A (en) 1992-06-16 1992-06-16 Filter for dust removal and denitration

Country Status (1)

Country Link
JP (1) JPH06334A (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5620669A (en) * 1995-08-15 1997-04-15 W. L. Gore & Associates, Inc. Catalytic filter material and method of making same
JP2002079057A (en) * 2000-09-04 2002-03-19 Meidensha Corp Denitration method and apparatus therefor
WO2006006702A1 (en) * 2004-07-15 2006-01-19 Nikki-Universal Co., Ltd. Catalyst for purifying exhaust gas containing organic nitrogen compound and method for purifying such exhaust gas
US7651895B2 (en) 2005-03-28 2010-01-26 Seiko Epson Corporation Transistor, method for manufacturing thereof, substrate for an electrooptical device
CN105107330A (en) * 2015-09-17 2015-12-02 福建龙净环保股份有限公司 Integrated device for ultralow emission of flue gas, dust and NOX
CN107233789A (en) * 2017-06-30 2017-10-10 华电电力科学研究院 A kind of coal-fired flue-gas dust-removing denitrification integral system and its method of work
CN108854323A (en) * 2018-07-06 2018-11-23 江西博鑫精陶环保科技有限公司 A kind of preparation method of honeycomb wall flow high-temperature dust nitre one clarifier
CN113457667A (en) * 2021-07-16 2021-10-01 国家电投集团远达环保催化剂有限公司 Denitration and dust removal integrated catalyst and preparation method thereof

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5620669A (en) * 1995-08-15 1997-04-15 W. L. Gore & Associates, Inc. Catalytic filter material and method of making same
US5843390A (en) * 1995-08-15 1998-12-01 W. L. Gore & Associates, Inc. Method of using a catalytic filter
JP2002079057A (en) * 2000-09-04 2002-03-19 Meidensha Corp Denitration method and apparatus therefor
WO2006006702A1 (en) * 2004-07-15 2006-01-19 Nikki-Universal Co., Ltd. Catalyst for purifying exhaust gas containing organic nitrogen compound and method for purifying such exhaust gas
US8575054B2 (en) 2004-07-15 2013-11-05 Nikki-Universal Co., Ltd. Catalyst for purifying organic nitrogen compound-containing exhaust gas and method for purifying the exhaust gas
US7651895B2 (en) 2005-03-28 2010-01-26 Seiko Epson Corporation Transistor, method for manufacturing thereof, substrate for an electrooptical device
CN105107330A (en) * 2015-09-17 2015-12-02 福建龙净环保股份有限公司 Integrated device for ultralow emission of flue gas, dust and NOX
CN107233789A (en) * 2017-06-30 2017-10-10 华电电力科学研究院 A kind of coal-fired flue-gas dust-removing denitrification integral system and its method of work
CN108854323A (en) * 2018-07-06 2018-11-23 江西博鑫精陶环保科技有限公司 A kind of preparation method of honeycomb wall flow high-temperature dust nitre one clarifier
CN113457667A (en) * 2021-07-16 2021-10-01 国家电投集团远达环保催化剂有限公司 Denitration and dust removal integrated catalyst and preparation method thereof

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