JP2004283644A - Method and apparatus for cleaning incinerator exhaust gas - Google Patents

Method and apparatus for cleaning incinerator exhaust gas Download PDF

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Publication number
JP2004283644A
JP2004283644A JP2003075602A JP2003075602A JP2004283644A JP 2004283644 A JP2004283644 A JP 2004283644A JP 2003075602 A JP2003075602 A JP 2003075602A JP 2003075602 A JP2003075602 A JP 2003075602A JP 2004283644 A JP2004283644 A JP 2004283644A
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Prior art keywords
exhaust gas
temperature
dust collector
incinerator
path
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JP2003075602A
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Japanese (ja)
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Taizo Nagaoka
泰三 長岡
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NE PROJECT KK
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NE PROJECT KK
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for cleaning an incinerator exhaust gas which easily adjusts a dry dust collector at a temperature to enough demonstrate its performance by cooling the high temperature exhaust gas, can remove an acidic gas, and miniaturizes an apparatus itself, and the apparatus for the method. <P>SOLUTION: In the method, the high temperature exhaust gas from the incinerator 2, after being cooled, is passed through the dry dust collector 3. The exhaust gas is discharged into two pathways 5 and 8. Most of the exhaust gas is passed through a wet dust collector 6 from one pathway to remove the acidic gas, and after being cooled adiabatically in the dust collector 6, is led to a mixing temperature control device 7. The residual exhaust gas is led from the other pathway to the temperature control device. In the control device, the low temperature exhaust gas discharged from the wet dust collector 6 is heated by the residual high temperature exhaust gas, and the heated exhaust gas is led to the dry dust collector 3. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

【0001】
【発明の属する技術分野】
本発明は焼却炉の排気ガスから酸性ガスとダイオキシンを除去して清浄化する方法および装置に関する。
【0002】
【従来の技術】
ダイオキシンを除去する従来の処理方法は、焼却路の二次側に減温塔を設け、減温塔では800℃程度の排気ガスに加圧高温水を噴霧して、排気ガスを200℃程度まで急激に冷却し、その後、乾式集塵機(バグフィルター)を通す方法であった(例えば、特許文献1参照。)。この方法は、加圧高温水が冷水よりも気化しやすことを利用している。
【0003】
【特許文献1】
特開2001−132937号公報(第4頁、第1図)
【0004】
上述した方法以外には、排気ガスを熱交換方式で間接冷却してから乾式集塵機に通す方法もある。
【0005】
【発明が解決しようとする課題】
減温塔では、ダイオキシンの再合成を防ぐために排気ガスの温度を急激に低下させる役割だけでなく、乾式集塵機がその性能を充分に発揮できる温度である200℃程度よりも、排気ガスの温度を高くも低くもしないように調整する役割が求められている。
【0006】
しかし、減温塔での温度制御は、加圧高温水の噴霧量の調整によってのみ行われるものである。従って、その噴霧量が不適切な場合、例えば噴霧量が少ない場合には温度低下が不十分となる。一方、噴霧量が多い場合には温度が下がりすぎて、乾式集塵機が濡れ、排気ガスが通らなくなる恐れがある。それ故、温度制御は非常に重要であった。
【0007】
しかしながら、焼却炉から排出される排気ガスの温度は、燃焼するゴミの種類や量によって変動する。従って、常時変動する排気ガスの温度を、加圧高温水の噴霧量だけで所定の温度に冷却するのは困難である。熱交換方式の場合も同様のことが言える。つまり、間接冷却のため、被熱体(例えば水)の流量を制御しなければ温度制御できないが、被熱体の流量を大幅に変化させることは構造上できないので、排気ガスの温度変化に追従できない。
【0008】
また、加圧高温水を噴霧し、その気化熱を利用して冷却するという構造上、大きな気化領域を必要とし、減温塔が大型化する。熱交換方式の場合も、勿論、大型化する。
【0009】
さらに、乾式集塵機(バグフィルター)は、ダイオキシン等粒子を除去するものであり、酸性ガス(HclやSOx等)のガス体除去能力は低い。従って、乾式集塵機の二次側に酸性ガスの大半が排出され、環境上、好ましくない。なお、バグフィルターは、消石灰や活性炭の粉体を通常使用しているが、表面が酸性ガスと反応して別の化合物が生成し、ダイオキシン除去能力が低下する。
【0010】
本発明は以上に述べたような実情を考慮して創作されたもので、その解決課題は以下の通りである。第一に、高温排気ガスを冷却して乾式集塵機がその性能を充分に発揮できる温度に調整することが容易であること。第二に、酸性ガスを除去できること。第三に、装置自体を小型化できるようにすること。
【0011】
【課題を解決するための手段】
請求項1記載の発明は、焼却炉からの高温排気ガスを冷却後に乾式集塵機を通す焼却炉排気ガスの清浄化方法に関する。そして、焼却炉から高温排気ガスを二経路に排出し、高温排気ガスの大半を一方の経路から湿式集塵機に通して酸性ガスを除去しそこで断熱冷却した後に混合温度調整装置に導くと共に、高温排気ガスの残りを他方の経路から混合温度調整装置に導き、混合温度調整装置では、湿式集塵機から出される低温排気ガスを高温排気ガスの残りで昇温させ、その昇温させた排気ガスを乾式集塵機に導くことを特徴とする。
【0012】
高温排気ガスの大半を湿式集塵機に通過させることで、酸性ガスのガス体を除去し、断熱冷却によりダイオキシンの再合成しない温度まで急冷でき、混合温度調整装置でその低温排気ガスに高温排気ガスの残りを混合することによって、乾式集塵機がその性能を充分に発揮する使用可能温度にまで昇温できる。そして、乾式集塵機ではダイオキシンを吸着して除去する。また、乾式集塵機は、前述したように酸性ガスのガス体除去能力が低いが、高温排気ガスの大半を湿式集塵機に通して酸性ガスのガス体を除去しているので、その低い能力で高温排気ガスの残りに含まれる酸性ガスのガス体を除去すれば良く、全体的には酸性ガスのガス体の殆どが除去される。
【0013】
請求項2記載の発明の焼却炉排気ガスの清浄化装置は、焼却炉からの排気ガスを二経路に排出する分岐管と、分岐管の一方の経路に一次側を接続する湿式集塵機と、分岐管の他方の経路と湿式集塵機の二次側の双方に一次側を接続し且つ乾式集塵機に二次側を接続する混合温度調整装置と、混合温度調整装置から排出される排気ガスの温度を一定温度に保持するために焼却炉からの高温排気ガスを一方の経路と他方の経路に導く割合を自動的に調整する混合割合制御装置と、からなることを特徴とする。
【0014】
混合割合制御装置としては、分岐管の一方の経路と他方の経路にダンパーをそれぞれ開閉可能に設け、混合温度調整装置から出る排気ガスの温度を温度センサーで検知して、その検知結果が一定温度となるようにダンパーの開閉具合を自動的に調整するものが、一例として挙げられる。
【0015】
【発明の実施の形態】
図1及び図2に示すのが、本発明の焼却炉排気ガスの清浄化装置1を組み込んだゴミ焼却施設である。ゴミ焼却施設は、焼却炉2と、本発明の清浄化装置1と、乾式集塵機3、排気ファンFANから構成される。
【0016】
焼却炉2では、ゴミを800℃以上の高温で完全燃焼させ、ダイオキシンの発生を阻止する。焼却炉2を出た高温排気ガスは、本発明の清浄化装置1に送られる。
【0017】
清浄化装置1では、取り込んだ高温排気ガスを分岐管4で二つの経路に排出し、高温排気ガスの大半を一方の経路5から湿式集塵機6、混合温度調整装置7に順番に送ると共に、高温排気ガスの残りを他方の経路8から混合温度調整装置7に直接送り込む。湿式集塵機6では、酸性ガスを除去しつつ800℃以上の高温排気ガスを0.5秒以下で80℃程度に断熱冷却して低温排気ガスとする。混合温度調整装置7では、80℃程度の低温排気ガスに高温排気ガスの残りを混ぜ合わせ、その混合割合を混合割合制御装置9で自動的に調整して排気ガスを200℃程度にする。そして、200℃程度の排気ガスを乾式集塵機(バグフィルター)3に通して、ダイオキシンを除去すると共に、残りの高温排気ガスに含まれる酸性ガスを除去し、排気ガスを清浄化する。その後、排気ガスは、排気ファンFANによって誘引されて大気に放出される。
【0018】
清浄化装置1を構成する機器類についてさらに詳述する。湿式集塵機6(スクラバ)は酸性ガスを除去する周知のいかなるものであっても良いが、高温排気ガスが洗浄液と触れた際に水滴となって排気ガスと同伴されるのを防止するためには、ミスト除去ユニットUを取り付けることが望ましい。湿式集塵機6の一例としては、塔10内上部のシャワーノズル11から洗浄液を散水し、その洗浄液で高温排気ガスを断熱冷却して排出する。また、高温排気ガスの酸性ガスが洗浄液で除去されて、塔10の底部に溜まる洗浄液のpHが変化するが、溜まった液のpHをセンサー(図示省略)で検知して、一定のpHに保つようにバルブ12の開閉具合を自動的に制御して、塔10内にアルカリを補給する。また、塔10内から出口用配管13を利用して定量づつ排液し洗浄液の塩濃度を一定に維持する。排液には有害物も含まれているので、焼却灰等と供に系外処理する。なお、排気ガスの排出や有害物の排出に伴って水分が失われるので、底部に溜まる液量をセンサー(図示省略)で検知して、一定のレベルを保つようにバルブ14を自動的に開閉して塔内に水を補給する。
【0019】
混合温度調整装置7は、筒状ケース15の一次側覆板16の中央部に内筒17を突入し、内筒17から低温排気ガスをケース15内に取り入れる。一方、残りの高温排気ガスを導入する取込み口18をケース15の筒板19の一次側にあけ、取込み口18から取り込んだ高温排気ガスが内筒17の外側を旋回し、その旋回流によって高温排気ガスと低温排気ガスを効率よく混合して昇温させ、出口20から排出する。また、飽和された状態の低温排気ガスが内筒17から入ってケース15に直に接触するとケース15が腐食するので、それを防ぐためにケース15の内側に沿って高温排気ガスの旋回流を発生させ、低温排気ガスを包み込むようにしてある。なお、ケース15の二次側(出口側)は先細り状になっており、旋回流を発生させやすくしてある。
【0020】
混合割合を自動的に調整する混合割合制御装置9は、混合温度調整装置7の出口側に有する温度センサー21と、分岐管4からの一方の経路5と他方の経路8に別々に有するダンパー22、23と、コントローラ24からなり、温度センサー21からの検知信号に基づいてコントローラ24が二つのダンパー22,23の開閉具合を自動的に調整して排気ガスの温度を200℃程度となるようにする。混合割合の目安としては、一方の経路5(湿式集塵機に向かう方)を通過する高温排気ガスが85%、他方の経路7(直に混合温度調整装置に向かう方)を通過する高温排気ガスが15%を基準とし、基準付近で混合割合を調整する。
【0021】
乾式集塵機3は、ダイオキシン除去のため消石灰や活性炭の粉体を用い、200℃程度がその性能を充分に発揮できる温度である。また、酸性ガスの除去能力は高くはないが少しはある。
【0022】
【発明の効果】
本発明によれば、湿式集塵機で酸性ガスのガス体を除去し、混合温度調整装置で排気ガスの温度調整をするという具合に、その役割が明確に分かれており、湿式集塵機では排気ガスの温度低下を気にすることなく酸性ガスのガス体除去に専念でき、一方、混合温度調整装置では排気ガスの温度調整に専念できるので、排気ガスの温度調整が容易に行える。また、湿式集塵機で冷却して低温となった排気ガスを、高温排気ガスの残りで昇温させるという巧みな手法を用いることで、熱を有効利用している。さらに、高温排気ガスに含まれる酸性ガスは、そのガス体の大部分を湿式集塵機で除去し、残りの分だけ乾式集塵機で除去すれば良いので、ガス体の除去能力が低い乾式集塵機での負荷が小さくなり、その結果、乾式集塵機から排出される排気ガスは、ガス体が殆ど除去される。その上、乾式集塵機ではダイオキシンをも除去しているので、排出される排気ガスは清浄なものとなる。また、乾式集塵機に付着する酸性物の量を激減でき、乾式集塵機がその性能を発揮できる期間が長くなる。
【0023】
高温排気ガスを湿式集塵機で断熱冷却することで、混合温度調整装置に投入する排気ガスの量を減らすことができ、装置自体を小型化できる。
【図面の簡単な説明】
【図1】焼却炉排気ガスの清浄化装置を組み込んだゴミ焼却施設のブロック図である。
【図2】焼却炉排気ガスの清浄化装置を組み込んだゴミ焼却施設の説明図である。
【符号の説明】
2 焼却炉
3 乾式集塵機
4 分岐管
5 一方の経路
6 湿式集塵機
7 混合温度調整装置
8 他方の経路
9 混合割合制御装置
[0001]
TECHNICAL FIELD OF THE INVENTION
The present invention relates to a method and an apparatus for removing acid gas and dioxin from exhaust gas of an incinerator for purification.
[0002]
[Prior art]
In the conventional treatment method for removing dioxin, a cooling tower is provided on the secondary side of the incineration path, and in the cooling tower, exhaust gas at about 800 ° C is sprayed with pressurized high-temperature water to reduce the exhaust gas to about 200 ° C. It was a method of rapidly cooling and then passing through a dry dust collector (bag filter) (for example, see Patent Document 1). This method utilizes the fact that pressurized high-temperature water vaporizes more than cold water.
[0003]
[Patent Document 1]
JP 2001-132937 A (page 4, FIG. 1)
[0004]
In addition to the method described above, there is a method in which the exhaust gas is indirectly cooled by a heat exchange method and then passed through a dry dust collector.
[0005]
[Problems to be solved by the invention]
The cooling tower not only plays a role in rapidly reducing the temperature of the exhaust gas to prevent re-synthesis of dioxin, but also reduces the temperature of the exhaust gas from about 200 ° C, which is the temperature at which the dry dust collector can sufficiently exhibit its performance. There is a need for a role to adjust so that it is not too high or too low.
[0006]
However, temperature control in the cooling tower is performed only by adjusting the spray amount of pressurized high-temperature water. Therefore, when the spray amount is inappropriate, for example, when the spray amount is small, the temperature drop is insufficient. On the other hand, when the spray amount is large, the temperature may be too low, the dry dust collector may get wet, and exhaust gas may not pass. Therefore, temperature control was very important.
[0007]
However, the temperature of the exhaust gas discharged from the incinerator varies depending on the type and amount of refuse to be burned. Therefore, it is difficult to cool the constantly changing exhaust gas temperature to a predetermined temperature only by the spray amount of pressurized high-temperature water. The same can be said for the heat exchange method. In other words, the temperature cannot be controlled without controlling the flow rate of the heat target (for example, water) because of indirect cooling, but the flow rate of the heat target cannot be changed drastically structurally. Can not.
[0008]
Further, a structure in which pressurized high-temperature water is sprayed and cooled by utilizing the heat of vaporization requires a large vaporization region, and the size of the cooling tower increases. In the case of the heat exchange method, of course, the size is increased.
[0009]
Furthermore, the dry dust collector (bag filter) is for removing particles such as dioxin, and has a low ability to remove acidic gases (Hcl, SOx, etc.). Therefore, most of the acid gas is discharged to the secondary side of the dry dust collector, which is not preferable from an environmental point of view. In addition, although powder of slaked lime or activated carbon is usually used for the bag filter, the surface reacts with the acidic gas to generate another compound, and the dioxin removal ability is reduced.
[0010]
The present invention has been created in consideration of the above-described circumstances, and the problems to be solved are as follows. First, it is easy to cool the high-temperature exhaust gas and adjust it to a temperature at which the dry dust collector can sufficiently exhibit its performance. Second, the ability to remove acid gases. Third, the device itself can be miniaturized.
[0011]
[Means for Solving the Problems]
The invention according to claim 1 relates to a method for purifying incinerator exhaust gas by passing a high-temperature exhaust gas from an incinerator through a dry dust collector after cooling. Then, the high-temperature exhaust gas is discharged from the incinerator into two paths, most of the high-temperature exhaust gas is passed from one path through a wet dust collector to remove the acid gas, and then adiabatically cooled. The rest of the gas is led from the other path to the mixing temperature controller, where the temperature of the low-temperature exhaust gas discharged from the wet dust collector is raised by the rest of the high-temperature exhaust gas, and the heated exhaust gas is dried by the dry dust collector. It is characterized by leading to.
[0012]
By passing most of the high-temperature exhaust gas through a wet dust collector, the gaseous acid gas can be removed, and adiabatic cooling allows rapid cooling to a temperature at which dioxin is not resynthesized. By mixing the remainder, the temperature can be raised to a usable temperature at which the dry dust collector sufficiently exhibits its performance. The dry dust collector adsorbs and removes dioxin. As described above, dry dust collectors have a low ability to remove acidic gases, but most of the high-temperature exhaust gases pass through wet dust collectors to remove the acidic gases. What is necessary is just to remove the gaseous substance of the acidic gas contained in the rest of the gas, and almost all of the gaseous substance of the acidic gas is removed.
[0013]
An incinerator exhaust gas purifying apparatus according to claim 2 includes a branch pipe for discharging exhaust gas from the incinerator to two paths, a wet dust collector for connecting a primary side to one path of the branch pipe, and a branch pipe. A mixing temperature controller that connects the primary side to both the other path of the pipe and the secondary side of the wet type dust collector and connects the secondary side to the dry type dust collector, and keeps the temperature of the exhaust gas discharged from the mixing temperature regulator constant. A mixing ratio control device for automatically adjusting a ratio of high-temperature exhaust gas from the incinerator to one path and the other path to maintain the temperature.
[0014]
As the mixing ratio control device, dampers are provided in one path and the other path of the branch pipe so as to be openable and closable, and the temperature of exhaust gas emitted from the mixing temperature control device is detected by a temperature sensor, and the detection result is a constant temperature. One that automatically adjusts the opening / closing state of the damper so that
[0015]
BEST MODE FOR CARRYING OUT THE INVENTION
FIG. 1 and FIG. 2 show a refuse incineration facility incorporating an incinerator exhaust gas cleaning apparatus 1 of the present invention. The refuse incineration facility includes an incinerator 2, the cleaning device 1 of the present invention, a dry dust collector 3, and an exhaust fan FAN.
[0016]
In the incinerator 2, the refuse is completely burned at a high temperature of 800 ° C. or more to prevent the generation of dioxin. The high-temperature exhaust gas leaving the incinerator 2 is sent to the cleaning device 1 of the present invention.
[0017]
In the cleaning device 1, the taken high-temperature exhaust gas is discharged to two paths through the branch pipe 4, and most of the high-temperature exhaust gas is sequentially sent from one path 5 to the wet dust collector 6 and the mixing temperature adjusting device 7. The remainder of the exhaust gas is sent directly from the other path 8 to the mixing temperature controller 7. In the wet dust collector 6, high-temperature exhaust gas of 800 ° C. or more is adiabatically cooled to about 80 ° C. in 0.5 seconds or less while removing acidic gas to produce low-temperature exhaust gas. The mixing temperature adjusting device 7 mixes the rest of the high-temperature exhaust gas with the low-temperature exhaust gas of approximately 80 ° C., and automatically adjusts the mixing ratio by the mixing ratio control device 9 to reduce the exhaust gas to approximately 200 ° C. Then, the exhaust gas of about 200 ° C. is passed through a dry dust collector (bag filter) 3 to remove dioxin and remove the acidic gas contained in the remaining high-temperature exhaust gas, thereby purifying the exhaust gas. Thereafter, the exhaust gas is attracted by the exhaust fan FAN and released to the atmosphere.
[0018]
The equipment constituting the cleaning device 1 will be described in further detail. The wet dust collector 6 (scrubber) may be any known one that removes acid gas. However, in order to prevent hot exhaust gas from becoming water droplets and being entrained with the exhaust gas when it comes into contact with the cleaning liquid. It is desirable to attach a mist removal unit U. As an example of the wet dust collector 6, the cleaning liquid is sprinkled from the shower nozzle 11 at the upper part of the tower 10, and the high-temperature exhaust gas is adiabatically cooled and discharged with the cleaning liquid. Further, the acidic gas of the high-temperature exhaust gas is removed by the cleaning liquid, and the pH of the cleaning liquid accumulated at the bottom of the tower 10 changes. However, the pH of the accumulated liquid is detected by a sensor (not shown) and maintained at a constant pH. The opening and closing of the valve 12 is automatically controlled as described above, and alkali is supplied into the tower 10. Further, the solution is drained from the inside of the tower 10 using the outlet pipe 13 at a constant rate, and the salt concentration of the washing solution is kept constant. Since the wastewater contains harmful substances, it is treated outside the system together with incineration ash. Since water is lost due to exhaust gas emission and harmful substance emission, the amount of liquid accumulated at the bottom is detected by a sensor (not shown), and the valve 14 is automatically opened and closed so as to maintain a constant level. And refill the tower with water.
[0019]
The mixing temperature adjusting device 7 projects the inner cylinder 17 into the center of the primary side cover plate 16 of the cylindrical case 15, and takes in low-temperature exhaust gas from the inner cylinder 17 into the case 15. On the other hand, the intake port 18 for introducing the remaining high-temperature exhaust gas is opened on the primary side of the cylindrical plate 19 of the case 15, and the high-temperature exhaust gas taken in from the intake port 18 turns around the outer side of the inner cylinder 17. Exhaust gas and low-temperature exhaust gas are efficiently mixed and heated to be discharged from the outlet 20. If saturated low-temperature exhaust gas enters through the inner cylinder 17 and comes into direct contact with the case 15, the case 15 is corroded. To prevent this, a swirling flow of the high-temperature exhaust gas is generated along the inside of the case 15. And wraps the low temperature exhaust gas. Note that the secondary side (outlet side) of the case 15 is tapered so that a swirling flow is easily generated.
[0020]
The mixing ratio control device 9 for automatically adjusting the mixing ratio includes a temperature sensor 21 provided on the outlet side of the mixing temperature control device 7 and a damper 22 provided separately on one path 5 and the other path 8 from the branch pipe 4. , 23, and a controller 24. The controller 24 automatically adjusts the opening / closing state of the two dampers 22, 23 based on the detection signal from the temperature sensor 21 so that the temperature of the exhaust gas becomes about 200 ° C. I do. As a guide of the mixing ratio, 85% of the high-temperature exhaust gas passing through one path 5 (toward the wet-type dust collector) and 85% of the high-temperature exhaust gas passing through the other path 7 (toward the mixing temperature controller). The mixing ratio is adjusted near 15% with reference to 15%.
[0021]
The dry dust collector 3 uses slaked lime or activated carbon powder to remove dioxins, and a temperature of about 200 ° C. is a temperature at which its performance can be sufficiently exhibited. In addition, the ability to remove acidic gas is not high, but there is a little.
[0022]
【The invention's effect】
According to the present invention, the role of removing the gaseous acid gas with a wet dust collector and controlling the temperature of the exhaust gas with a mixing temperature controller is clearly divided, and the temperature of the exhaust gas is reduced in the wet dust collector. It is possible to concentrate on removing the acid gas from the gas without worrying about the decrease. On the other hand, the mixing temperature controller can concentrate on the temperature control of the exhaust gas, so that the temperature control of the exhaust gas can be easily performed. Further, the heat is effectively used by using a skillful method of raising the temperature of the exhaust gas cooled to a low temperature by the wet dust collector with the remainder of the high-temperature exhaust gas. Furthermore, since most of the acidic gas contained in the high-temperature exhaust gas can be removed by the wet dust collector and the remaining gas can be removed by the dry dust collector, the load on the dry dust collector, which has a low gas removing ability, can be reduced. As a result, the exhaust gas discharged from the dry dust collector is almost completely free of gas. In addition, since the dry dust collector also removes dioxin, the exhaust gas discharged is clean. Further, the amount of acidic substances adhering to the dry dust collector can be drastically reduced, and the period during which the dry dust collector can exhibit its performance becomes longer.
[0023]
By adiabatically cooling the high-temperature exhaust gas with a wet dust collector, the amount of exhaust gas to be supplied to the mixing temperature adjusting device can be reduced, and the device itself can be downsized.
[Brief description of the drawings]
FIG. 1 is a block diagram of a refuse incineration facility incorporating an incinerator exhaust gas cleaning device.
FIG. 2 is an explanatory diagram of a refuse incineration facility in which an incinerator exhaust gas cleaning device is incorporated.
[Explanation of symbols]
2 incinerator 3 dry dust collector 4 branch pipe 5 one path 6 wet dust collector 7 mixing temperature regulator 8 other path 9 mixing ratio controller

Claims (2)

焼却炉(2)からの高温排気ガスを冷却後に乾式集塵機(3)を通す焼却炉排気ガスの清浄化方法において、
焼却炉(2)から高温排気ガスを二経路(5,8)に排出し、高温排気ガスの大半を一方の経路(5)から湿式集塵機(6)に通して酸性ガスを除去しそこで断熱冷却した後に混合温度調整装置(7)に導くと共に、高温排気ガスの残りを他方の経路(8)から混合温度調整装置(7)に導き、
混合温度調整装置(7)では、湿式集塵機(6)から出される低温排気ガスを高温排気ガスの残りで昇温させ、その昇温させた排気ガスを乾式集塵機(3)に導くことを特徴とする焼却炉排気ガスの清浄化方法。
In a method for purifying incinerator exhaust gas, the high-temperature exhaust gas from the incinerator (2) is cooled and then passed through a dry dust collector (3).
High-temperature exhaust gas is discharged from the incinerator (2) to two paths (5, 8), and most of the high-temperature exhaust gas is passed from one path (5) to the wet dust collector (6) to remove acid gas, and then adiabatically cooled. After that, the mixture is led to the mixing temperature controller (7), and the rest of the high-temperature exhaust gas is led from the other path (8) to the mixing temperature controller (7).
In the mixing temperature adjusting device (7), the low-temperature exhaust gas discharged from the wet dust collector (6) is heated with the remainder of the high-temperature exhaust gas, and the heated exhaust gas is guided to the dry dust collector (3). To clean incinerator exhaust gas.
焼却炉(2)からの排気ガスを二経路(5,8)に排出する分岐管(4)と、分岐管(4)の一方の経路(5)に一次側を接続する湿式集塵機(6)と、分岐管(4)の他方の経路(8)と湿式集塵機(6)の二次側の双方に一次側を接続し且つ乾式集塵機(3)に二次側を接続する混合温度調整装置(7)と、混合温度調整装置(7)から排出される排気ガスの温度を一定温度に保持するために焼却炉(2)からの高温排気ガスを一方の経路(5)と他方の経路(8)に導く割合を自動的に調整する混合割合制御装置(9)と、からなることを特徴とする焼却炉排気ガスの清浄化装置。A branch pipe (4) for discharging exhaust gas from the incinerator (2) to two paths (5, 8), and a wet dust collector (6) for connecting the primary side to one path (5) of the branch pipe (4) A mixing temperature control device (1) that connects the primary side to both the other path (8) of the branch pipe (4) and the secondary side of the wet dust collector (6) and connects the secondary side to the dry dust collector (3) ( 7) and the high-temperature exhaust gas from the incinerator (2) in order to maintain the temperature of the exhaust gas discharged from the mixing temperature adjusting device (7) at a constant temperature in one path (5) and the other path (8). And a mixing ratio control device (9) for automatically adjusting the ratio leading to (1).
JP2003075602A 2003-03-19 2003-03-19 Method and apparatus for cleaning incinerator exhaust gas Pending JP2004283644A (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20210143407A (en) * 2020-05-20 2021-11-29 주식회사 페스텍 Fire saftety exhaust system
CN116006979A (en) * 2022-12-07 2023-04-25 灌南新苏国丰新能源有限公司 Flue gas recovery monitoring system for garbage incineration power generation

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20210143407A (en) * 2020-05-20 2021-11-29 주식회사 페스텍 Fire saftety exhaust system
KR102483291B1 (en) * 2020-05-20 2023-01-02 주식회사 페스텍 Fire saftety exhaust system
CN116006979A (en) * 2022-12-07 2023-04-25 灌南新苏国丰新能源有限公司 Flue gas recovery monitoring system for garbage incineration power generation
CN116006979B (en) * 2022-12-07 2023-09-22 灌南新苏国丰新能源有限公司 Flue gas recovery monitoring system for garbage incineration power generation

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