JP2000140574A - Waste gas treatment apparatus and method - Google Patents

Waste gas treatment apparatus and method

Info

Publication number
JP2000140574A
JP2000140574A JP10322130A JP32213098A JP2000140574A JP 2000140574 A JP2000140574 A JP 2000140574A JP 10322130 A JP10322130 A JP 10322130A JP 32213098 A JP32213098 A JP 32213098A JP 2000140574 A JP2000140574 A JP 2000140574A
Authority
JP
Japan
Prior art keywords
exhaust gas
fluidized bed
alkali
waste gas
hydrogen chloride
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
JP10322130A
Other languages
Japanese (ja)
Inventor
Yasushi Yamamoto
泰史 山本
Hideji Michihashi
秀治 道端
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.)
Taiheiyo Cement Corp
Original Assignee
Taiheiyo Cement Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Taiheiyo Cement Corp filed Critical Taiheiyo Cement Corp
Priority to JP10322130A priority Critical patent/JP2000140574A/en
Publication of JP2000140574A publication Critical patent/JP2000140574A/en
Pending legal-status Critical Current

Links

Landscapes

  • Treating Waste Gases (AREA)
  • Gas Separation By Absorption (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

PROBLEM TO BE SOLVED: To efficiently remove acidic gases such as hydrogen chloride and sulfur oxides contained in a waste gas and lessen the consumption of an alkali. SOLUTION: A waste gas discharged out of a kiln 11 is cooled by a waste gas cooling tower 12 and then dust of the waste gas is removed and incinerator fly ashes are recovered by a dust removing apparatus 13 and further acidic gases such as hydrogen chloride, sulfur oxides, and the likes are removed from the resultant waste gas by reaction with an alkali forming a fluidized bed by passing the resultant waste gas through a fluidized bed filter 14. After that, the treated waste gas is released to atmosphere through a chimney 15.

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】この発明は、排ガス処理装置
及び方法に係り、特に塩化水素や硫黄酸化物等の酸性ガ
スが発生するような焼成工程が行われる燃焼炉からの排
ガスを消石灰等のアルカリを用いて処理する装置及び方
法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an exhaust gas treatment apparatus and method, and more particularly, to an exhaust gas from a combustion furnace in which a baking process is performed to generate an acidic gas such as hydrogen chloride or sulfur oxide. The present invention relates to an apparatus and a method for processing by using the method.

【0002】[0002]

【従来の技術】近年、都市ごみ等の廃棄物は著しく増加
し、これら廃棄物の有効利用、再資源化を図る目的で、
都市ごみ焼却灰等を原料の一部に用いる環境調和型セメ
ント(以下、エコセメントと称す)の製造が試みられて
いる。焼却灰に石灰石、粘土類等の天然原料を混合して
セメント調合原料とし、これをロータリーキルン等で焼
成することにより、エコセメントが製造される。
2. Description of the Related Art In recent years, the amount of waste such as municipal solid waste has increased remarkably, and for the purpose of effective use and recycling of such waste,
Attempts have been made to produce environmentally friendly cement (hereinafter referred to as ecocement) using incinerated ash from municipal solid waste as part of the raw material. Eco-cement is produced by mixing incinerated ash with natural raw materials such as limestone and clays to prepare a cement-mixed raw material and firing it in a rotary kiln or the like.

【0003】原料の一部に都市ごみ焼却灰等を用いるこ
とから、ロータリーキルンで発生する排ガスには塩化水
素や硫黄酸化物等の酸性ガスが含まれる惧れがあり、従
来は、図4に示されるような排ガス処理装置で処理して
いた。すなわち、キルン1から排出された排ガスは排ガ
ス冷却塔2で冷却された後、除塵機3に入る。除塵機3
内には濾布の表面上に消石灰等のアルカリの濾過層が形
成されたダスト捕集機構が設けられており、このダスト
捕集機構により排ガス中の焼却飛灰が捕集されると共に
排ガス中に含まれている塩化水素や硫黄酸化物等の酸性
ガスが濾過層のアルカリと反応し除去される。除塵機3
を出た排ガスは煙突4から大気中へ放出される。
[0003] Since municipal solid waste incineration ash and the like are used as part of the raw materials, there is a concern that the exhaust gas generated from the rotary kiln may contain acidic gases such as hydrogen chloride and sulfur oxides. The waste gas was treated with an exhaust gas treatment device as described below. That is, the exhaust gas discharged from the kiln 1 is cooled in the exhaust gas cooling tower 2 and then enters the dust remover 3. Dust remover 3
There is a dust collection mechanism in which an alkali filtration layer such as slaked lime is formed on the surface of the filter cloth. This dust collection mechanism collects incineration fly ash in the exhaust gas, Acid gas such as hydrogen chloride or sulfur oxide contained in the filter reacts with the alkali in the filtration layer and is removed. Dust remover 3
Is discharged from the chimney 4 into the atmosphere.

【0004】[0004]

【発明が解決しようとする課題】しかしながら、除塵機
3のダスト捕集機構では、濾布の表面上に形成されるア
ルカリの濾過層が薄いことから塩化水素や硫黄酸化物等
の酸性ガスとアルカリとの十分な反応時間がとれず、ま
た濾過層内に焼却飛灰も含まれるため、塩化水素や硫黄
酸化物等の酸性ガスの除去効率が低く、アルカリが多量
に必要になるという問題点があった。
However, in the dust collecting mechanism of the dust remover 3, since an alkaline filter layer formed on the surface of the filter cloth is thin, an acidic gas such as hydrogen chloride or sulfur oxide is mixed with an alkaline gas. And the filtration layer contains incinerated fly ash, which reduces the efficiency of removing acidic gases such as hydrogen chloride and sulfur oxides, and requires a large amount of alkali. there were.

【0005】この発明はこのような問題点を解消するた
めになされたもので、排ガス中に含まれる塩化水素や硫
黄酸化物等の酸性ガスを効率よく除去することができ、
アルカリの使用量を低減することができる排ガス処理装
置及び方法を提供することを目的としている。
The present invention has been made to solve such a problem, and can efficiently remove acidic gases such as hydrogen chloride and sulfur oxide contained in exhaust gas.
It is an object of the present invention to provide an exhaust gas treatment device and method capable of reducing the amount of alkali used.

【0006】[0006]

【課題を解決するための手段】この発明に係る排ガス処
理装置は、燃焼炉で発生した排ガスから焼却飛灰を回収
する除塵機と、除塵機で焼却飛灰が回収された排ガスを
流通させることにより排ガスに含まれる塩化水素や硫黄
酸化物等の酸性ガスを除去するアルカリの流動床フィル
ターとを備えたものである。なお、流動床フィルターと
して、アルカリと活性炭との混合物からなる流動床を有
するフィルターを用いることもできる。また、燃焼炉と
しては、セメント製造等に用いられるロータリーキルン
を使用することができる。
An exhaust gas treatment apparatus according to the present invention comprises a dust remover for collecting incinerated fly ash from exhaust gas generated in a combustion furnace, and an exhaust gas from which the incinerated fly ash is collected by the dust remover. And an alkaline fluidized bed filter for removing acidic gases such as hydrogen chloride and sulfur oxides contained in the exhaust gas. In addition, a filter having a fluidized bed made of a mixture of an alkali and activated carbon can be used as the fluidized bed filter. In addition, a rotary kiln used for cement production or the like can be used as the combustion furnace.

【0007】この発明に係る排ガス処理方法は、燃焼炉
で発生した排ガスから焼却飛灰を回収し、焼却飛灰が回
収された排ガスをアルカリの流動床に流通させることに
より排ガスに含まれる塩化水素や硫黄酸化物等の酸性ガ
スを除去する方法である。なお、流動床としてアルカリ
と活性炭との混合物からなる流動床を用い、焼却飛灰が
回収された排ガスをこの流動床に流通させることにより
塩化水素や硫黄酸化物等の酸性ガスの除去と共に排ガス
に含まれるダイオキシンを除去することもできる。
[0007] The exhaust gas treatment method according to the present invention recovers incinerated fly ash from exhaust gas generated in a combustion furnace, and flows the exhaust gas from which the incinerated fly ash has been recovered through a fluidized bed of alkali to remove hydrogen chloride contained in the exhaust gas. This is a method for removing acidic gases such as sulfur and sulfur oxides. In addition, by using a fluidized bed made of a mixture of alkali and activated carbon as a fluidized bed, the exhaust gas from which the incinerated fly ash was collected was passed through the fluidized bed to remove acidic gases such as hydrogen chloride and sulfur oxides, and to form the exhaust gas. The contained dioxin can also be removed.

【0008】[0008]

【発明の実施の形態】以下、この発明の実施の形態を添
付図面に基づいて説明する。図1にこの発明の一実施の
形態に係る排ガス処理装置の構成を示す。セメント製造
に用いられるロータリーキルン等のキルン11に排ガス
冷却塔12が接続され、排ガス冷却塔12に除塵機13
が接続されている。さらに、除塵機13に流動床フィル
ター14が接続され、流動床フィルター14の出口側に
煙突15が接続されている。
Embodiments of the present invention will be described below with reference to the accompanying drawings. FIG. 1 shows a configuration of an exhaust gas treatment apparatus according to one embodiment of the present invention. An exhaust gas cooling tower 12 is connected to a kiln 11 such as a rotary kiln used for cement production.
Is connected. Further, a fluidized bed filter 14 is connected to the dust remover 13, and a chimney 15 is connected to an outlet side of the fluidized bed filter 14.

【0009】次に、この実施の形態に係る排ガス処理装
置の動作について説明する。まず、セメント原料の焼成
を行うキルン11から排出された排ガスは、排ガス冷却
塔12において、除塵機13に流通し得る程度の温度に
まで冷却された後に除塵機13に入り、ここで除塵され
て焼却飛灰が回収される。この除塵機13は、図4に示
した除塵機3のようなアルカリの濾過層を備えておら
ず、焼却飛灰の捕集のみを目的とするため、電気集塵機
等の各種の除塵機を用いることができる。
Next, the operation of the exhaust gas processing apparatus according to this embodiment will be described. First, the exhaust gas discharged from the kiln 11 for sintering the cement raw material is cooled in the exhaust gas cooling tower 12 to a temperature at which the exhaust gas can be circulated to the dust remover 13, and then enters the dust remover 13, where the dust is removed. Incinerated fly ash is collected. This dust remover 13 does not have an alkali filtration layer like the dust remover 3 shown in FIG. 4 and is used only for collecting incinerated fly ash. Therefore, various dust removers such as an electric dust collector are used. be able to.

【0010】次に、除塵機13を出た排ガスは、図2及
び3に示されるような流動床フィルター14に入る。流
動床フィルター14は二つの密閉室21を備えており、
各密閉室内には消石灰等のアルカリ22の流動床がその
底部に形成されると共に排ガス透過性且つアルカリ不透
過性の濾過手段23が上部に配置されている。除塵機1
3からの排ガスは、入口ダクト24からパイプ25へ、
そしてガス分散器26を経て二つの密閉室21内に導入
される。排ガスの導入速度は、装置の規模や形状等に依
存するものではあるが、例えば0.1〜2m/秒程度と
することができる。
Next, the exhaust gas leaving the dust remover 13 enters a fluidized bed filter 14 as shown in FIGS. The fluidized bed filter 14 has two closed chambers 21,
In each closed chamber, a fluidized bed of alkali 22 such as slaked lime is formed at the bottom, and an exhaust gas permeable and alkali impermeable filtering means 23 is disposed at the top. Dust remover 1
3 from the inlet duct 24 to the pipe 25,
Then, the gas is introduced into the two closed chambers 21 through the gas distributor 26. Although the introduction speed of the exhaust gas depends on the scale and shape of the apparatus, it can be, for example, about 0.1 to 2 m / sec.

【0011】ガス分散器26から密閉室21内に導入さ
れた排ガスはアルカリ22と接触し、このとき流動床で
あるアルカリ22は、排ガスにより密閉室21内で吹き
上げられ、排ガスとアルカリ22との充分な接触がなさ
れ、排ガスに含まれる塩化水素や硫黄酸化物等の酸性ガ
スが効率的に除去される。密閉室21内への排ガスの導
入速度が高い場合、アルカリ22は勢いよく吹き上げら
れて噴流状態になるが、この状態でも塩化水素や硫黄酸
化物等の酸性ガスの効率的な除去が達成される。ここで
密閉室21内に、導入される排ガスの乱流を生じさせる
手段、例えば邪魔板27を配置すれば、排ガスとアルカ
リ22との接触が一層良好となり好ましい。
The exhaust gas introduced into the closed chamber 21 from the gas distributor 26 comes into contact with the alkali 22, and at this time, the alkali 22 as a fluidized bed is blown up in the closed chamber 21 by the exhaust gas, and Sufficient contact is made, and acid gases such as hydrogen chloride and sulfur oxides contained in the exhaust gas are efficiently removed. When the introduction speed of the exhaust gas into the closed chamber 21 is high, the alkali 22 is vigorously blown up to be in a jet state, but also in this state, the efficient removal of the acidic gas such as hydrogen chloride and sulfur oxide is achieved. . Here, it is preferable to arrange a means for generating a turbulent flow of the exhaust gas to be introduced, for example, a baffle plate 27 in the closed chamber 21 because the contact between the exhaust gas and the alkali 22 is further improved.

【0012】アルカリ22と接触した排ガスは、下流方
向で排ガス透過性且つ活性炭不透過性の濾過手段23を
通過する。濾過手段23は、その目的が達せられればよ
く、その具体的な形態はとくに制限されないが、例えば
ろ布を用いた濾過手段が簡便で低コストであり好まし
い。ろ布としては、例えば従来のバグフィルタと同様の
ものを用いることができる。また、排ガス及びアルカリ
22との接触表面積が大きくなるように、例えばろ布を
適当な支持体上に巻き付けて円筒状とし、これを多数本
設置しておくのが好適である。このような濾過手段23
により、アルカリ22は密閉室21内に保持され、排ガ
スのみが濾過手段23を通過し、出口ダクト39を通じ
て密閉室21の外部に放出される。
The exhaust gas which has come into contact with the alkali 22 passes through a filtering means 23 which is permeable to the exhaust gas and impermeable to activated carbon in the downstream direction. As long as the purpose of the filtering means 23 is achieved, its specific form is not particularly limited. For example, a filtering means using a filter cloth is preferable because it is simple and low-cost. As the filter cloth, for example, the same cloth as a conventional bag filter can be used. Further, it is preferable that a filter cloth is wound around a suitable support to form a cylindrical shape, and a large number of the filter cloths are provided so that the contact surface area with the exhaust gas and the alkali 22 is increased. Such a filtering means 23
Accordingly, the alkali 22 is held in the closed chamber 21, and only the exhaust gas passes through the filtering means 23 and is discharged to the outside of the closed chamber 21 through the outlet duct 39.

【0013】密閉室21内の圧力は、密閉室21の形
状、濾過手段23の形態、処理速度等に依存するもので
はあるが、例えば60〜1000mmHOとすること
ができる。
The pressure in the closed chamber 21 depends on the shape of the closed chamber 21, the form of the filtering means 23, the processing speed and the like, but may be, for example, 60 to 1000 mmH 2 O.

【0014】なお、塩化水素や硫黄酸化物等の酸性ガス
とアルカリとの反応により流動床内で生成された生成物
は、排ガスの入り口である流動床の下部に溜まるため、
アルカリ22の流動床は適宜交換する必要がある。この
場合、排ガス入口ダンパ31および排ガス出口ダンパ3
2を閉じて密閉室21内のガスの出入りを遮断し、アル
カリ22をバルブ33を介して排出器34及び輸送機3
5に運ぶ。このとき、ろ布差圧計36により、ろ布に付
着しているアルカリ量が多い場合には、例えばエアー供
給手段37によりエアーを吹付けてアルカリをろ布から
除去することができる。一方、新たなアルカリは、輸送
機28からダンパ29を経てアルカリホッパー30に供
給され、排ガス入口ダンパ31及び排ガス出口ダンパ3
2を閉じた状態で、アルカリホッパー30から密閉室2
1内にバルブ40で供給量が調節されながら導入され
る。図2及び3に示される流動床フィルター14では、
密閉室21が二つ設けられているため、アルカリの交換
はそれぞれ交互に行うことができ、排ガス処理操作を完
全に停止させることがなく有利である。
The product produced in the fluidized bed by the reaction of an acidic gas such as hydrogen chloride or sulfur oxide with an alkali accumulates in the lower part of the fluidized bed, which is the entrance of the exhaust gas.
The fluidized bed of the alkali 22 needs to be appropriately replaced. In this case, the exhaust gas inlet damper 31 and the exhaust gas outlet damper 3
2 is closed to shut off gas from flowing into and out of the sealed chamber 21, and the alkali 22 is discharged from the discharger 34 and the transporter 3 via the valve 33.
Carry to 5. At this time, when the amount of alkali adhering to the filter cloth is large by the filter cloth differential pressure gauge 36, the alkali can be removed from the filter cloth by, for example, blowing air by the air supply means 37. On the other hand, fresh alkali is supplied from the transporting machine 28 to the alkali hopper 30 via the damper 29, and the exhaust gas inlet damper 31 and the exhaust gas outlet damper 3 are supplied.
2 is closed, and the sealed chamber 2 is
The gas is introduced into the fuel cell 1 while the supply amount is adjusted by the valve 40. In the fluidized bed filter 14 shown in FIGS.
Since the two closed chambers 21 are provided, the exchange of alkalis can be performed alternately, which is advantageous without completely stopping the exhaust gas treatment operation.

【0015】流動床フィルター14の運転中に、アルカ
リ流動床差圧計38により、流動床の差圧が低いことが
判明した場合には、アルカリを補充し、差圧が高い場合
には、逆にアルカリをフィルター外部に排出し、流動床
フィルター14内の圧力を適切に保つことが望ましい。
また、排ガス量が多い場合には、上記のような流動床フ
ィルターを並列に連結するとよい。さらに、排ガス中に
塩化水素や硫黄酸化物等の酸性ガスが多量に含まれるこ
とが想定される場合には、複数の流動床フィルターを直
列に連結し、排ガスの処理操作を数回繰り返すことが好
ましい。流動床を形成するアルカリとしては、消石灰の
他、CaO、CaCO、NaOH、KOH等の種々の
アルカリを用いることができる。
If the pressure difference of the fluidized bed is found to be low by the alkali fluidized bed pressure gauge 38 during the operation of the fluidized bed filter 14, the alkali is replenished. It is desirable to discharge the alkali to the outside of the filter and maintain the pressure inside the fluidized bed filter 14 appropriately.
When the amount of exhaust gas is large, the fluidized bed filters described above may be connected in parallel. Further, when it is assumed that the exhaust gas contains a large amount of an acidic gas such as hydrogen chloride or sulfur oxide, a plurality of fluidized bed filters may be connected in series, and the exhaust gas treatment operation may be repeated several times. preferable. As the alkali forming the fluidized bed, various alkalis such as CaO, CaCO 3 , NaOH, and KOH can be used in addition to slaked lime.

【0016】このようにして塩化水素や硫黄酸化物等の
酸性ガスが除去された排ガスは、煙突15から大気中へ
放出される。
The exhaust gas from which the acidic gases such as hydrogen chloride and sulfur oxide have been removed is discharged from the chimney 15 into the atmosphere.

【0017】なお、流動床フィルター14として、アル
カリと活性炭との混合物からなる流動床を有するフィル
ターを用い、この流動床フィルター14に焼却飛灰が回
収された排ガスを流通させれば、排ガスに含まれるダイ
オキシンが流動床内の活性炭に吸着されるため、排ガス
中の塩化水素や硫黄酸化物等の酸性ガスの除去と同時に
ダイオキシンの除去が可能となる。
If a filter having a fluidized bed made of a mixture of alkali and activated carbon is used as the fluidized bed filter 14 and the exhaust gas from which the incinerated fly ash is collected is passed through the fluidized bed filter 14, it is contained in the exhaust gas. Since dioxin is adsorbed on activated carbon in the fluidized bed, dioxin can be removed simultaneously with the removal of acidic gases such as hydrogen chloride and sulfur oxides in exhaust gas.

【0018】この発明は、上述したようなセメント原料
の焼成の他、ごみの焼却やプラスチック類の燃焼装置
等、塩化水素や硫黄酸化物等の酸性ガスの発生を伴うキ
ルンからの排ガスの処理に適している。
The present invention is applicable not only to the above-described firing of cement raw materials, but also to the treatment of exhaust gas from kilns accompanied by generation of acid gas such as hydrogen chloride and sulfur oxides, such as incineration of refuse and combustion of plastics. Are suitable.

【0019】[0019]

【発明の効果】以上説明したように、この発明によれ
ば、排ガスから焼却飛灰を回収した後、アルカリの流動
床フィルターに排ガスを流通させることにより、排ガス
に含まれる塩化水素や硫黄酸化物等の酸性ガスを除去す
るので、塩化水素や硫黄酸化物等の酸性ガスを効率よく
除去することができ、アルカリの使用量を低減すること
が可能となる。また、流動床としてアルカリと活性炭と
の混合物からなる流動床を用いれば、焼却飛灰が回収さ
れた排ガスをこの流動床に流通させることにより塩化水
素や硫黄酸化物等の酸性ガスの除去と共に排ガスに含ま
れるダイオキシンを除去することも可能である。
As described above, according to the present invention, after incineration fly ash is recovered from the exhaust gas, the exhaust gas is passed through an alkali fluidized bed filter, whereby hydrogen chloride and sulfur oxides contained in the exhaust gas are removed. Since acidic gases such as hydrogen chloride and sulfur oxides can be efficiently removed, it is possible to reduce the amount of alkali used. In addition, if a fluidized bed made of a mixture of alkali and activated carbon is used as the fluidized bed, the exhaust gas from which the incinerated fly ash is collected is passed through the fluidized bed to remove acid gases such as hydrogen chloride and sulfur oxides and to remove the exhaust gas. It is also possible to remove dioxins contained in.

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

【図1】この発明の一実施の形態に係る排ガス処理装置
を示すブロック図である。
FIG. 1 is a block diagram showing an exhaust gas treatment apparatus according to one embodiment of the present invention.

【図2】実施の形態で用いられた流動床フィルターを示
す側面断面図である。
FIG. 2 is a side sectional view showing a fluidized bed filter used in the embodiment.

【図3】実施の形態で用いられた流動床フィルターを示
す平面図である。
FIG. 3 is a plan view showing a fluidized bed filter used in the embodiment.

【図4】従来の排ガス処理装置を示すブロック図であ
る。
FIG. 4 is a block diagram showing a conventional exhaust gas treatment device.

【符号の説明】[Explanation of symbols]

11 キルン 12 排ガス冷却塔 13 除塵機 14 流動床フィルター 15 煙突 22 アルカリ 11 Kiln 12 Exhaust gas cooling tower 13 Dust remover 14 Fluid bed filter 15 Chimney 22 Alkaline

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) B01D 53/70 B01D 53/34 134A B01J 20/20 134E Fターム(参考) 4D002 AA02 AA19 AA21 AC05 BA03 BA04 BA13 BA14 CA07 CA09 DA01 DA04 DA06 DA11 DA12 DA16 DA41 EA02 GA02 GB01 GB04 GB06 HA01 HA10 4D020 AA06 AA08 AA10 BA01 BA02 BA30 BB01 CA07 CC05 CC06 CD02 4G066 AA05B AA13B AA17B AA43B AE02B BA42 CA07 CA23 CA31 CA33 DA02 ──────────────────────────────────────────────────の Continued on the front page (51) Int.Cl. 7 Identification code FI Theme coat ゛ (Reference) B01D 53/70 B01D 53/34 134A B01J 20/20 134E F-term (Reference) 4D002 AA02 AA19 AA21 AC05 BA03 BA04 BA13 BA14 CA07 CA09 DA01 DA04 DA06 DA11 DA12 DA16 DA41 EA02 GA02 GB01 GB04 GB06 HA01 HA10 4D020 AA06 AA08 AA10 BA01 BA02 BA30 BB01 CA07 CC05 CC06 CD02 4G066 AA05B AA13B AA17B AA43B AE02B BA42 CA07 CA23 CA31

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 燃焼炉で発生した排ガスから焼却飛灰を
回収する除塵機と、 前記除塵機で焼却飛灰が回収された排ガスを流通させる
ことにより排ガスに含まれる塩化水素や硫黄酸化物等の
酸性ガスを除去するアルカリの流動床フィルターとを備
えたことを特徴とする排ガス処理装置。
1. A dust remover for recovering incinerated fly ash from exhaust gas generated in a combustion furnace, and an exhaust gas from which the incinerated fly ash is recovered by the dust remover is used to circulate hydrogen chloride, sulfur oxide, etc. contained in the exhaust gas. An exhaust gas treatment device comprising: an alkaline fluidized bed filter for removing acidic gas.
【請求項2】 前記流動床フィルターは、アルカリと活
性炭との混合物からなる流動床を有することを特徴とす
る請求項1に記載の排ガス処理装置。
2. The exhaust gas treatment apparatus according to claim 1, wherein the fluidized bed filter has a fluidized bed made of a mixture of alkali and activated carbon.
【請求項3】 前記燃焼炉はロータリーキルンである請
求項1または2に記載の排ガス処理装置。
3. The exhaust gas treatment device according to claim 1, wherein the combustion furnace is a rotary kiln.
【請求項4】 燃焼炉で発生した排ガスから焼却飛灰を
回収し、 焼却飛灰が回収された排ガスをアルカリの流動床に流通
させることにより排ガスに含まれる塩化水素や硫黄酸化
物等の酸性ガスを除去することを特徴とする排ガス処理
方法。
4. An incineration fly ash is recovered from an exhaust gas generated in a combustion furnace, and the exhaust gas from which the incineration fly ash is recovered is passed through a fluidized bed of an alkali, so that acidic gases such as hydrogen chloride and sulfur oxide contained in the exhaust gas are recovered. An exhaust gas treatment method comprising removing gas.
【請求項5】 焼却飛灰が回収された排ガスをアルカリ
と活性炭との混合物からなる流動床に流通させることに
より塩化水素や硫黄酸化物等の酸性ガスの除去と共に排
ガスに含まれるダイオキシンを除去することを特徴とす
る請求項4に記載の排ガス処理方法。
5. An exhaust gas from which incinerated fly ash has been collected is passed through a fluidized bed made of a mixture of alkali and activated carbon to remove acidic gases such as hydrogen chloride and sulfur oxides and to remove dioxins contained in the exhaust gas. The exhaust gas treatment method according to claim 4, wherein:
JP10322130A 1998-11-12 1998-11-12 Waste gas treatment apparatus and method Pending JP2000140574A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10322130A JP2000140574A (en) 1998-11-12 1998-11-12 Waste gas treatment apparatus and method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10322130A JP2000140574A (en) 1998-11-12 1998-11-12 Waste gas treatment apparatus and method

Publications (1)

Publication Number Publication Date
JP2000140574A true JP2000140574A (en) 2000-05-23

Family

ID=18140275

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10322130A Pending JP2000140574A (en) 1998-11-12 1998-11-12 Waste gas treatment apparatus and method

Country Status (1)

Country Link
JP (1) JP2000140574A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005125234A (en) * 2003-10-23 2005-05-19 Sumitomo Osaka Cement Co Ltd Dust collecting apparatus and dust collecting method of cement production facility
CN116531933A (en) * 2023-07-04 2023-08-04 生态环境部华南环境科学研究所(生态环境部生态环境应急研究所) Wet multi-pollutant absorbent for flue gas of brick kiln and preparation method thereof

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005125234A (en) * 2003-10-23 2005-05-19 Sumitomo Osaka Cement Co Ltd Dust collecting apparatus and dust collecting method of cement production facility
CN116531933A (en) * 2023-07-04 2023-08-04 生态环境部华南环境科学研究所(生态环境部生态环境应急研究所) Wet multi-pollutant absorbent for flue gas of brick kiln and preparation method thereof
CN116531933B (en) * 2023-07-04 2023-11-07 生态环境部华南环境科学研究所(生态环境部生态环境应急研究所) Wet multi-pollutant absorbent for flue gas of brick kiln and preparation method thereof

Similar Documents

Publication Publication Date Title
JP2006096615A (en) Method of treating exhaust gas from cement kiln
CN107583449B (en) Industrial garbage cracking incineration tail gas treatment method
EP0170355B1 (en) Emission control process for combustion flue gases
CN100361899C (en) Production of TiCl from high titanium slag4Closed deslagging method in process
JP2001065840A (en) Combustion gas processing method in refuse incinerator equipment
JPH05329316A (en) Waste gas treatment device
JP2000140627A (en) Dioxin removing material, dioxin removing method and regenerating method of dioxin removing material
JP2000140574A (en) Waste gas treatment apparatus and method
JPS59183817A (en) Removal of harmful component and dust in waste gas from waste incinerator
JP3905716B2 (en) Method for controlling ground improvement material manufacturing apparatus
JP4033420B2 (en) Method and apparatus for dry removal of hydrogen chloride in exhaust gas
JP2001248827A (en) Equipment for treatment of incineration waste gas for obtaining clean incineration fly ash
KR100373589B1 (en) Method for spraying and treating chemicals in a precoated-type bag filter
JP2001017833A (en) Method and device for dry treatment of exhaust gas
JP2010194530A (en) Method and apparatus for removing co2
US4764348A (en) Emission control apparatus
JP2000042362A (en) Waste gas treating device and method
JPH0376963B2 (en)
JP2000126550A (en) Combustion device and method for treating exhaust gas therefrom, ash cooling device therefor
JPH10165765A (en) Process and device for treating exhaust gas
JP2000354736A (en) Device for treating exhaust gas and its operation
CN201346444Y (en) Desulfurization device
JPH08332343A (en) Rdf-incinerating, exhaust gas treatment apparatus
JPS5535870A (en) Waste incinerating method
JP2001079340A (en) Method for removing sulfur oxide and hydrogen chloride contained in waste gas at incineration facility