JPH06205918A - Operating method of filtration type dust collector - Google Patents

Operating method of filtration type dust collector

Info

Publication number
JPH06205918A
JPH06205918A JP5019660A JP1966093A JPH06205918A JP H06205918 A JPH06205918 A JP H06205918A JP 5019660 A JP5019660 A JP 5019660A JP 1966093 A JP1966093 A JP 1966093A JP H06205918 A JPH06205918 A JP H06205918A
Authority
JP
Japan
Prior art keywords
dust
type dust
dust collector
neutralizer
filtration type
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.)
Granted
Application number
JP5019660A
Other languages
Japanese (ja)
Other versions
JP3092373B2 (en
Inventor
Tadashi Oura
忠 大浦
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.)
Hitachi Plant Technologies Ltd
Original Assignee
Hitachi Plant Technologies 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
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Application filed by Hitachi Plant Technologies Ltd filed Critical Hitachi Plant Technologies Ltd
Priority to JP05019660A priority Critical patent/JP3092373B2/en
Publication of JPH06205918A publication Critical patent/JPH06205918A/en
Application granted granted Critical
Publication of JP3092373B2 publication Critical patent/JP3092373B2/en
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Links

Abstract

PURPOSE:To provide the operating method of a filtration type dust collector in which dust collecting capacity is kept constant even when the added quantity of a neutralizer is changed, by controlling the period of dust blow-off by the added quantity of the alkali neutralizer based on the concentration of acidic gas. CONSTITUTION:In a filtration type dust collector where an alkaline neutralizer is added to waste gas based on the concentration of acidic gas in the waste gas to perform neutralization reaction, and to collect dust by a filter cloth, when the added quantity of the neutralizer is large, the period of dust blow-off is shortened and when the added quantity of the neutralizer is small, the period of dust blow-off is prolonged. When a charcoal fire is buried in ash in an incinerator, the deliquescence calcium chloride as a reactional product, is markedly generated to frequently cause the clogging of the filter cloth, and so the period of dust blow-off is shortened based on the information on the charcoal fire buried in ash. Further, when the difference in pressure between the waste gas inlet side and the treated gas outlet side becomes a prescribed value or more, dust blow-off operation is additionally performed by making an interruption on the period of dust blow-off. Thus, an operating method by which dust collecting capacity is kept constant irrespective of the added quantity of the neutralizer can be provided.

Description

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

【0001】[0001]

【産業上の利用分野】本発明はろ過式集塵装置の運転方
法に係り、特にろ過式集塵装置に導入される排気ガス中
にアルカリ中和剤を添加し、ガス中に含まれる酸性ガス
を中和反応させてろ過式集塵装置のろ布で捕集するろ過
式集塵装置の運転方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for operating a filtration type dust collector, and more particularly to an acidic gas contained in a gas obtained by adding an alkali neutralizing agent to exhaust gas introduced into the filtration dust collector. The present invention relates to a method of operating a filtration type dust collecting apparatus, in which the water is neutralized and collected by a filter cloth of the filtration type dust collecting apparatus.

【0002】[0002]

【従来の技術】焼却炉から排出される排気ガス中には、
重金属やダイオキシン等が含まれているので、焼却炉の
後段にろ過式集塵装置を設け、このろ過式集塵装置によ
り前記重金属やダイオキシン等を捕集して前記排気ガス
を大気に放出している。しかし、前記ろ過式集塵装置か
ら放出される処理ガス中には、塩化水素(HCl)や硫
黄酸化物(SOX)等の酸性ガスが含まれており、これ
らの酸性ガスを直接大気に放出することはできない。
2. Description of the Related Art In exhaust gas discharged from an incinerator,
Since it contains heavy metals, dioxins, etc., a filtration type dust collector is installed in the latter stage of the incinerator, and the heavy metals, dioxins, etc. are collected by this filtration type dust collector and the exhaust gas is released to the atmosphere. There is. However, the processing gas released from the filtration type dust collector contains acidic gases such as hydrogen chloride (HCl) and sulfur oxides (SOX), and these acidic gases are directly released to the atmosphere. It is not possible.

【0003】そこで、ろ過式集塵装置に導入される排気
ガスに、水酸化カルシウム〔Ca(OH)2 〕等のアル
カリ中和剤を添加し、前記酸性ガスを中和反応させてろ
過式集塵装置のろ布に捕集するようにしている。前記ア
ルカリ中和剤の添加量は、ろ過式集塵装置から放出され
る処理ガス中の酸性ガス濃度に基づいて制御されてい
る。
Therefore, an alkaline neutralizing agent such as calcium hydroxide [Ca (OH) 2 ] is added to the exhaust gas introduced into the filtration type dust collector to neutralize the acid gas to carry out the filtration type collection. It collects on the filter cloth of the dust device. The addition amount of the alkali neutralizing agent is controlled based on the concentration of acidic gas in the processing gas discharged from the filtration dust collector.

【0004】しかし、塩化水素と水酸化カルシウムとの
化学反応で生成される塩化カルシウム(CaCl2
は、潮解性の高いものなので(特に、焼却炉の埋火時等
における温度低下時にその潮解性が著しく生じる)、潮
解した塩化カルシウムがろ布に付着して目詰まりを頻繁
に発生させる。そこで、従来から、ろ過式集塵装置は、
所定の周期で前記ろ布に圧縮エアーを吹き付けてろ布に
付着した塩化カルシウムを含むダストを払い落とすよう
にしている。
However, calcium chloride (CaCl 2 ) produced by the chemical reaction between hydrogen chloride and calcium hydroxide
Has a high deliquescent property (especially, the deliquescent property remarkably occurs when the temperature of the incinerator is lowered during a burial, etc.), so that deliquescent calcium chloride adheres to the filter cloth and frequently causes clogging. Therefore, conventionally, the filtration type dust collector is
Compressed air is blown to the filter cloth at a predetermined cycle to remove the dust containing calcium chloride attached to the filter cloth.

【0005】[0005]

【発明が解決しようとする課題】しかしながら、従来の
ろ過式集塵装置は、ダスト払い落とし動作を一定の周期
で制御しているので、例えばアルカリ中和剤の添加量が
増加した場合、即ち塩化カルシウムのろ布への付着速度
が早くなった場合、ダスト払い落とし動作の前にろ布に
塩化カルシウムが十分に付着し、ダスト捕集能力がその
間低下するという欠点がある。
However, since the conventional filtration type dust collector controls the dust removal operation at a constant cycle, for example, when the addition amount of the alkali neutralizing agent is increased, that is, when the chloride neutralizing agent is added, If the rate of adhesion of calcium to the filter cloth becomes faster, there is a drawback that calcium chloride is sufficiently adhered to the filter cloth before the dust removing operation, and the dust collecting ability is reduced during that time.

【0006】本発明はこのような事情に鑑みてなされた
もので、アルカリ中和剤の添加量が変化してもダスト捕
集能力を一定に維持することができるろ過式集塵装置の
運転方法を提供することを目的とする。
The present invention has been made in view of the above circumstances, and a method of operating a filtration type dust collecting apparatus capable of maintaining a constant dust collecting ability even when the amount of alkali neutralizer added changes. The purpose is to provide.

【0007】[0007]

【課題を解決する為の手段】本発明は、前記目的を達成
する為に、焼却炉等から排出された排気ガスを処理して
大気に放出するろ過式集塵装置であって、このろ過式集
塵装置から放出される処理ガス中の酸性ガス濃度に基づ
いて、前記排気ガス中に添加するアルカリ中和剤の添加
量を制御するろ過式集塵装置の運転方法に於いて、前記
アルカリ中和剤の添加量に基づいて、前記ろ過式集塵装
置のダスト払い落とし周期を制御するようにしたことを
特徴としている。
In order to achieve the above-mentioned object, the present invention is a filter type dust collecting apparatus for treating exhaust gas discharged from an incinerator or the like and releasing it to the atmosphere. In a method for operating a filtration type dust collecting apparatus, which controls the addition amount of an alkali neutralizing agent added to the exhaust gas, based on the concentration of acid gas in the processing gas discharged from the dust collecting apparatus, It is characterized in that the dust removal cycle of the filtration type dust collecting apparatus is controlled based on the amount of addition of the solvating agent.

【0008】[0008]

【作用】本発明によれば、アルカリ中和剤の添加量に基
づいて、ろ過式集塵装置のダスト払い落とし周期を制御
する。即ち、添加量が多い場合には、ダスト払い落とし
周期を短くし、添加量が少ない場合にはダスト払い落と
し周期を長くする。これにより、アルカリ中和剤の添加
量が変化してもダスト捕集能力を一定に維持することが
できる。
According to the present invention, the dust removal cycle of the filtration dust collector is controlled based on the amount of the alkali neutralizing agent added. That is, when the addition amount is large, the dust removal period is shortened, and when the addition amount is small, the dust removal period is extended. Thereby, even if the amount of the alkali neutralizing agent added changes, the dust collecting ability can be maintained constant.

【0009】また、塩化水素(HCl)等の酸性ガス
と、水酸化カルシウム〔Ca(OH)2 〕等のアルカリ
中和剤との化学反応で生成される塩化カルシウム(Ca
Cl2)は、特に、焼却炉の埋火時等における温度低下
時にその潮解性が著しく生じるので、焼却炉等の埋火時
に、ダストの払い落とし周期を更に短く略間欠的に制御
する。
Calcium chloride (Ca) produced by a chemical reaction between an acidic gas such as hydrogen chloride (HCl) and an alkali neutralizing agent such as calcium hydroxide [Ca (OH) 2 ].
Cl 2 ) has a remarkable deliquescent property particularly when the temperature of the incinerator is lowered during the burial of the incinerator or the like. Therefore, when the burial of the incinerator or the like is performed, the dust removal cycle is controlled to be even shorter and substantially intermittent.

【0010】これにより、焼却炉の次回の運転開始時に
おけるダスト捕集能力を低下させない。更に、ろ過式集
塵装置の排気ガス入口側と処理ガス出口側との差圧を測
定し、この差圧が所定値以上になった時に、前記ダスト
払い落とし周期に割り込ませてダスト払い落とし動作を
行う。
As a result, the dust collecting capability at the start of the next operation of the incinerator is not reduced. Furthermore, the differential pressure between the exhaust gas inlet side and the treated gas outlet side of the filtration type dust collector is measured, and when this differential pressure exceeds a predetermined value, it is interrupted in the dust sweep cycle to perform the dust sweep operation. I do.

【0011】これにより、アルカリ中和剤の添加量に影
響されず、ダスト捕集能力を一定に維持することができ
る。
As a result, the dust collecting ability can be maintained constant without being affected by the amount of the alkali neutralizing agent added.

【0012】[0012]

【実施例】以下添付図面に従って本発明に係るろ過式集
塵装置の運転方法の好ましい実施例について説明する。
図1には、本発明に係るろ過式集塵装置の運転方法が適
用された焼却炉排気ガスの処理系統を示す。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENT A preferred embodiment of a method for operating a filtration type dust collecting apparatus according to the present invention will be described below with reference to the accompanying drawings.
FIG. 1 shows a treatment system for incinerator exhaust gas to which the method for operating a filtration dust collector according to the present invention is applied.

【0013】焼却炉10から発生した燃焼排気ガスは、
吸気ファン12に吸引されることにより、煙道14、ろ
過式集塵装置16、及び煙道18を介して、煙突20か
ら大気に放出される。前記ろ過式集塵装置16の入口側
煙道14には、吹込部22が設けられる。この吹込部2
2には、前記排気ガス中に含まれる塩化水素等の酸性ガ
スを中和反応させるアルカリ中和剤、例えば水酸化カル
シウムが供給される。これにより、排気ガスには水酸化
カルシウムが添加され、そして添加されて生成される塩
化カルシウムが前記ろ過式集塵装置16のろ布24A、
24B、24Cに付着して潮解する。
The combustion exhaust gas generated from the incinerator 10 is
By being sucked by the intake fan 12, the air is discharged from the chimney 20 to the atmosphere through the flue 14, the filtration dust collector 16, and the flue 18. The inlet side flue 14 of the filtration type dust collector 16 is provided with a blowing part 22. This blowing part 2
An alkaline neutralizing agent for neutralizing an acidic gas such as hydrogen chloride contained in the exhaust gas, for example, calcium hydroxide, is supplied to 2. As a result, calcium hydroxide is added to the exhaust gas, and calcium chloride produced by the addition is added to the filter cloth 24A of the filtration dust collector 16,
It adheres to 24B and 24C and deliquesces.

【0014】前記水酸化カルシウムはサイロ26に蓄え
られており、演算部28でその開閉量がインバータ制御
された供給器30によって、開閉量に基づいた必要量が
サイロ26から切り出される。切り出された前記水酸化
カルシウムは、供給器30の後段に設置された輸送ブロ
ア32によって前記吹込部22に空気輸送される。前記
演算部28は、出口側煙道18に接続された塩化水素濃
度計34、及び硫黄酸化物濃度計36からの濃度を示す
情報に基づいて、これらの濃度をゼロに近づける為の水
酸化カルシウムの添加量を演算する。そして、演算部2
8は、演算して求めた添加量を切り出す為の駆動信号を
前記供給器30に出力する。これにより、水酸化カルシ
ウムの添加量は、ろ過式集塵装置16からの処理ガス中
に含まれる酸性ガス濃度に基づいて自動制御される。
The calcium hydroxide is stored in the silo 26, and a necessary amount based on the opening / closing amount is cut out from the silo 26 by a feeder 30 whose opening / closing amount is inverter-controlled by a computing unit 28. The cut out calcium hydroxide is pneumatically transported to the blow-in unit 22 by a transportation blower 32 installed at a subsequent stage of the feeder 30. Based on the information indicating the concentrations from the hydrogen chloride densitometer 34 and the sulfur oxide densitometer 36 connected to the outlet side flue 18, the computing unit 28 uses calcium hydroxide to bring these concentrations close to zero. Calculate the addition amount of. And the calculation unit 2
Reference numeral 8 outputs a drive signal to the supply device 30 for cutting out the addition amount calculated and calculated. As a result, the amount of calcium hydroxide added is automatically controlled based on the concentration of acidic gas contained in the process gas from the filtration dust collector 16.

【0015】一方、前記供給器30による水酸化カルシ
ウムの切り出し量は、コントローラ38に出力される。
このコントローラ38は、前記切り出し量に基づいて、
エアーバルブ40A、40B、40Cの開閉周期を演算
する。そして、コントローラ38は、演算して求めた開
閉周期で各エアーバルブ40A、40B、40Cを開閉
させる為の駆動信号を各エアーバルブ40A、40B、
40Cに出力する。これにより、エアーバルブ40A、
40B、40Cは、その開閉動作がコントローラ38に
よって制御される。
On the other hand, the amount of calcium hydroxide cut out by the feeder 30 is output to the controller 38.
The controller 38, based on the cutout amount,
The open / close cycle of the air valves 40A, 40B, 40C is calculated. Then, the controller 38 outputs drive signals for opening and closing the air valves 40A, 40B, 40C at the calculated open / close cycle to the air valves 40A, 40B,
Output to 40C. As a result, the air valve 40A,
The opening and closing operations of 40B and 40C are controlled by the controller 38.

【0016】前記エアーバルブ40A、40B、40C
にはエアー源42が接続される。エアー源42からの圧
縮エアは、開放されたエアーバルブ40A、40B、4
0Cを介してろ布24A、24B、24C内に供給され
る。これにより、ろ布24A、24B、24Cに付着し
たダストが払い落とされる。また、コントローラ38
は、前記焼却炉10の埋火を示す埋火信号44が入力さ
れると、エアーバルブ40A、40B、40Cを短い周
期で間欠的に開放させる為の駆動信号をエアーバルブ4
0A、40B、40Cに出力することができる。
The air valves 40A, 40B, 40C
An air source 42 is connected to. Compressed air from the air source 42 is released by the air valves 40A, 40B, 4
It is supplied into the filter cloths 24A, 24B, and 24C via 0C. As a result, the dust attached to the filter cloths 24A, 24B, 24C is removed. In addition, the controller 38
When the burial signal 44 indicating the burial of the incinerator 10 is input, the air valve 4 outputs a drive signal for intermittently opening the air valves 40A, 40B and 40C in a short cycle.
It can be output to 0A, 40B, and 40C.

【0017】更に、前記コントローラ38には、差圧器
46から煙道14と煙道18の差圧を示す情報が逐次出
力されている。この差圧が所定値(ろ布24A、24
B、24Cの捕集能力が低下したことを示す値)以上に
なった時に前記エアーバルブ40A、40B、40Cを
開放させる駆動信号をエアーバルブ40A、40B、4
0Cに出力することができる。
Further, information indicating the differential pressure between the flue 14 and the flue 18 is sequentially output from the pressure differencer 46 to the controller 38. This differential pressure is a predetermined value (filter cloth 24A, 24
B, 24C is a value indicating that the trapping ability has deteriorated) or more), a drive signal for opening the air valves 40A, 40B, 40C is supplied to the air valves 40A, 40B, 4
Can be output to 0C.

【0018】次に、前記コントローラ38によるろ過式
集塵装置16の運転制御方法について図2を参照しなが
ら説明する。先ず、焼却炉10、及びろ過式集塵装置1
6の運転を開始する。そして、煙道18を通過する処理
ガス中の塩化水素濃度、硫黄酸化物濃度を、それぞれ塩
化水素濃度計34、及び硫黄酸化物濃度計36で測定
し、この濃度に基づいて求められた添加量の水酸化カル
シウムをサイロ26から吹込部22に供給する。
Next, a method of controlling the operation of the filtration type dust collector 16 by the controller 38 will be described with reference to FIG. First, the incinerator 10 and the filtration dust collector 1
Operation of 6 is started. Then, the hydrogen chloride concentration and the sulfur oxide concentration in the treated gas passing through the flue 18 are measured by the hydrogen chloride concentration meter 34 and the sulfur oxide concentration meter 36, respectively, and the addition amount obtained based on these concentrations Of calcium hydroxide is supplied from the silo 26 to the blowing section 22.

【0019】初期運転期間中における塩化水素濃度、硫
黄酸化物濃度は、定常運転期間中の各濃度よりも高い場
合があるので、前記水酸化カルシウムの添加量は演算部
28によって多めに制御制御される。これにより、コン
トローラ38は図2に示すように、定常運転期間中のダ
スト払い落とし周期T2 よりも短い周期T1 でエアーバ
ルブ40A、40B、40Cを開閉制御する。
Since the hydrogen chloride concentration and the sulfur oxide concentration during the initial operation period may be higher than the respective concentrations during the steady operation period, the addition amount of the calcium hydroxide is controlled and controlled by the arithmetic unit 28 in a large amount. It Thus, as shown in FIG. 2, the controller 38 controls the opening and closing of the air valves 40A, 40B, 40C at a cycle T 1 shorter than the dust removal cycle T 2 during the steady operation period.

【0020】これにより、潮解した塩化カルシウムが各
ろ布24A、24B、24Cに十分に付着する前に、塩
化カルシウムや他のダストをろ布24A、24B、24
Cから払い落とすことができる。従って、水酸化カルシ
ウムの添加量が増えてもダスト捕集能力を一定に維持す
ることができる。次に、コントローラ38は、定常運転
期間中には前述したように、T2 の周期でエアーバルブ
40A、40B、40Cを開閉制御してダストの払い落
としを行う。
Thus, before the deliquescent calcium chloride is sufficiently adhered to each of the filter cloths 24A, 24B and 24C, calcium chloride and other dusts are removed from the filter cloths 24A, 24B and 24C.
Can be paid off from C. Therefore, even if the amount of calcium hydroxide added is increased, the dust collecting ability can be maintained constant. Next, during the steady operation period, the controller 38 controls the opening / closing of the air valves 40A, 40B, 40C at the cycle of T 2 to wipe off the dust, as described above.

【0021】定常運転期間中に、図1に示した差圧器4
6で測定された差圧が所定値以上になった時、これと略
同時にコントローラ38は、前記周期T2 に割り込ませ
てエアーバルブ40A、40B、40Cを開放制御す
る。これにより、水酸化カルシウムの添加量に影響され
ず、ろ過式集塵装置16のダスト捕集能力を一定に維持
することができる。また、定常運転期間中の周期T
2 は、コントローラ38に予めメモリされた最長周期よ
りも超えることはない。
During the steady operation period, the differential pressure device 4 shown in FIG.
When the differential pressure measured in 6 exceeds a predetermined value, the controller 38 causes the air valves 40A, 40B and 40C to open at substantially the same time as it interrupts the cycle T 2 . This makes it possible to maintain the dust collecting capability of the filtration dust collector 16 constant without being affected by the amount of calcium hydroxide added. In addition, the cycle T during the steady operation period
2 is no longer than the longest period previously stored in controller 38.

【0022】次いで、コントローラ38は、埋火信号4
4が入力されると、埋火運転期間中周期T3 でエアーバ
ルブ40A、40B、40Cを開閉制御してダストの払
い落としを行う。これは、焼却炉10の埋火時における
温度低下期間中に塩化カルシウムの潮解性が著しく生じ
るので、ダストの払い落とし周期を前記T1 、T2 周期
よりも更に短く略間欠的に制御し、潮解した塩化カルシ
ウムを効率良く払い落とすようにした。
Next, the controller 38 controls the flash signal 4
When 4 is input, the air valve 40A in Umahi operation period in the period T 3, 40B, 40C closing control to the brushing dust performed. This is because the deliquescent property of calcium chloride occurs remarkably during the temperature decrease period during the burial of the incinerator 10, so that the dust removal cycle is controlled to be substantially shorter and shorter than the T 1 and T 2 cycles, The deliquescent calcium chloride was efficiently removed.

【0023】これにより、焼却炉10の次回の運転開始
時におけるダスト捕集能力を低下させない。
As a result, the dust collecting capability at the time of starting the next operation of the incinerator 10 is not lowered.

【0024】[0024]

【発明の効果】以上説明したように本発明に係るろ過式
集塵装置の運転方法によれば、アルカリ中和剤の添加量
に基づいて、ろ過式集塵装置のダスト払い落とし周期を
制御したので、アルカリ中和剤の添加量が変化してもダ
スト捕集能力を一定に維持することができる。
As described above, according to the method of operating the filtration type dust collecting apparatus of the present invention, the dust removing cycle of the filtration type dust collecting apparatus is controlled based on the addition amount of the alkali neutralizing agent. Therefore, even if the addition amount of the alkali neutralizing agent changes, the dust collecting ability can be maintained constant.

【0025】また、酸性ガスとアルカリ中和剤との化学
反応で生成される塩化カルシウム等は、特に、焼却炉の
埋火時等における温度低下時にその潮解性が著しく生じ
るので、焼却炉等の埋火時に、前記ダストの払い落とし
周期を更に短く略間欠的に制御する。これにより、焼却
炉の次回の運転開始時におけるダスト捕集能力を低下さ
せない。
Calcium chloride and the like produced by a chemical reaction between an acid gas and an alkali neutralizing agent have a remarkable deliquescent property particularly when the temperature of the incinerator is lowered during the burial of the incinerator. At the time of burial, the dust removal cycle is controlled to be shorter and substantially intermittently. As a result, the dust collection capability at the start of the next operation of the incinerator is not reduced.

【0026】更に、ろ過式集塵装置の排気ガス入口側と
処理ガス出口側との差圧を測定し、この差圧が所定値以
上になった時に、前記ダスト払い落とし周期に割り込ま
せてダスト払い落とし動作を行うようにしたので、アル
カリ中和剤の添加量に影響されず、ダスト捕集能力を一
定に維持することができる。
Further, the differential pressure between the exhaust gas inlet side and the treated gas outlet side of the filtration type dust collector is measured, and when the differential pressure exceeds a predetermined value, the dust is removed by interrupting the dust sweeping cycle. Since the removal operation is performed, the dust collecting ability can be maintained constant without being affected by the addition amount of the alkali neutralizing agent.

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

【図1】本発明に係るろ過式集塵装置の運転方法の処理
系統図
FIG. 1 is a processing system diagram of a method for operating a filtration dust collector according to the present invention.

【図2】本発明に係るろ過式集塵装置の運転方法のダス
ト払い落とし周期を示す図
FIG. 2 is a diagram showing a dust removal cycle of the operation method of the filtration dust collector according to the present invention.

【符号の説明】[Explanation of symbols]

10…焼却炉 12…吸気ファン 14、18…煙道 16…ろ過式集塵装置 22…吹込部 24A、24B、24C…ろ布 26…サイロ 28…演算部 30…供給器 34…塩化水素濃度計 36…硫黄酸化物濃度計 38…コントローラ 40A、40B、40C…エアーバルブ 44…埋火信号 46…差圧器 10 ... Incinerator 12 ... Intake fan 14, 18 ... Flue 16 ... Filtration type dust collector 22 ... Blowing part 24A, 24B, 24C ... Filter cloth 26 ... Silo 28 ... Calculation part 30 ... Feeder 34 ... Hydrogen chloride concentration meter 36 ... Sulfur oxide concentration meter 38 ... Controller 40A, 40B, 40C ... Air valve 44 ... Burst signal 46 ... Differential pressure device

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 焼却炉等から排出された排気ガスを処理
して大気に放出するろ過式集塵装置であって、このろ過
式集塵装置から放出される処理ガス中の酸性ガス濃度に
基づいて、前記排気ガス中に添加するアルカリ中和剤の
添加量を制御するろ過式集塵装置の運転方法に於いて、 前記アルカリ中和剤の添加量に基づいて、前記ろ過式集
塵装置のダスト払い落とし周期を制御するようにしたこ
とを特徴とするろ過式集塵装置の運転方法。
1. A filter-type dust collector that treats exhaust gas discharged from an incinerator or the like and discharges it to the atmosphere, based on the concentration of acidic gas in the process gas discharged from this filter-type dust collector. In the operating method of the filtration type dust collector controlling the addition amount of the alkali neutralizing agent added to the exhaust gas, based on the addition amount of the alkali neutralizing agent, A method for operating a filter-type dust collector, which is characterized in that a cycle for removing dust is controlled.
【請求項2】 前記焼却炉等の埋火を示す情報に基づい
て、前記ダストの払い落とし周期を制御するようにした
ことを特徴とする請求項1記載のろ過式集塵装置の運転
方法。
2. The method of operating a filtration type dust collecting apparatus according to claim 1, wherein the dust removal cycle is controlled based on information indicating a buried fire in the incinerator or the like.
【請求項3】 前記ろ過式集塵装置の排気ガス入口側と
処理ガス出口側との差圧を測定し、この差圧が所定値以
上になった時に、前記ダスト払い落とし周期に割り込ま
せてダスト払い落とし動作を行うように制御したことを
特徴とする請求項1記載のろ過式集塵装置の運転方法。
3. The differential pressure between the exhaust gas inlet side and the treated gas outlet side of the filtration type dust collector is measured, and when the differential pressure exceeds a predetermined value, it is interrupted in the dust sweep cycle. The method for operating a filtration type dust collecting apparatus according to claim 1, wherein the dust removing operation is controlled.
JP05019660A 1993-01-12 1993-01-12 Operation method of filtration type dust collector Expired - Fee Related JP3092373B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP05019660A JP3092373B2 (en) 1993-01-12 1993-01-12 Operation method of filtration type dust collector

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP05019660A JP3092373B2 (en) 1993-01-12 1993-01-12 Operation method of filtration type dust collector

Publications (2)

Publication Number Publication Date
JPH06205918A true JPH06205918A (en) 1994-07-26
JP3092373B2 JP3092373B2 (en) 2000-09-25

Family

ID=12005407

Family Applications (1)

Application Number Title Priority Date Filing Date
JP05019660A Expired - Fee Related JP3092373B2 (en) 1993-01-12 1993-01-12 Operation method of filtration type dust collector

Country Status (1)

Country Link
JP (1) JP3092373B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH09248418A (en) * 1996-03-15 1997-09-22 Nittetsu Mining Co Ltd Waste gas treatment method and apparatus

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH09248418A (en) * 1996-03-15 1997-09-22 Nittetsu Mining Co Ltd Waste gas treatment method and apparatus

Also Published As

Publication number Publication date
JP3092373B2 (en) 2000-09-25

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