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JPS6051533A - Dry removal method for harmful gases - Google Patents

Dry removal method for harmful gases

Info

Publication number
JPS6051533A
JPS6051533A JP58159978A JP15997883A JPS6051533A JP S6051533 A JPS6051533 A JP S6051533A JP 58159978 A JP58159978 A JP 58159978A JP 15997883 A JP15997883 A JP 15997883A JP S6051533 A JPS6051533 A JP S6051533A
Authority
JP
Japan
Prior art keywords
gas
exhaust gas
powder
blower
mixed
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
JP58159978A
Other languages
Japanese (ja)
Inventor
Koji Arita
有田 耕二
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.)
JFE Engineering Corp
Original Assignee
NKK Corp
Nippon Kokan 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 NKK Corp, Nippon Kokan Ltd filed Critical NKK Corp
Priority to JP58159978A priority Critical patent/JPS6051533A/en
Publication of JPS6051533A publication Critical patent/JPS6051533A/en
Pending legal-status Critical Current

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  • Treating Waste Gases (AREA)

Abstract

PURPOSE:To efficiently remove noxious gas in exhaust gas in a dry system, by simple operation such that an alkali powder is sprayed and mixed in exhaust gas to be reacted with noxious gas, and guiding the treated gas to a dust collector through a blower. CONSTITUTION:Exhaust gas containing noxious gas from a waste material incinerator is guided to a reaction chamber 11 and an alkali powder such as slaked lime is sprayed and mixed in the exhaust gas by compressed air to be reacted with noxious gas such as HCl. This powder mixed gas is guided to a blower 12 where the gas and the powder are again mixed under stirring and reacted. Thereafter, the exhaust gas is guided to a dust collecting apparatus 13 to perform dust collection while the purified gas is exhausted from a chimney 14. By this method, noxious gas can be removed with good efficiency by the reduced addition amount of the alkali powder.

Description

【発明の詳細な説明】 本発明は、廃棄物焼却炉等から発生する排ガス中の有害
ガスを乾式法により除去する方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for removing harmful gases from exhaust gas generated from a waste incinerator or the like by a dry method.

廃棄物焼却炉等の排ガス中には、I]C8+ SOx 
*NOx等の有害ガス成分が含まれている。これらの有
害ガスは、法律又は条例等で排出濃度の規制があり、近
年これらの規制値が強化されつつある。
In the exhaust gas from waste incinerators, etc., I]C8+ SOx
*Contains harmful gas components such as NOx. The emission concentrations of these harmful gases are regulated by laws or ordinances, and these regulatory values have been tightened in recent years.

有害ガス除去方法には、乾式、半乾式、湿式の3方式が
ある。乾式法は、半乾式法、湿式法に比べて設備費が安
く、操業、維持管理が容易である利点があるが、その反
面有害ガスの除去性能が悪い欠点がある。
There are three methods for removing harmful gases: dry, semi-dry, and wet. The dry method has the advantage of having lower equipment costs and easier operation and maintenance than the semi-dry method and the wet method, but has the disadvantage of poor performance in removing harmful gases.

[21Jち従来の乾式法は、焼却炉lからボイラ2を経
た排ガスを反応室3に導き、ここでアルカリ粉末(例え
ばCa(OH)z)を噴霧混合して有害ガスと反応させ
た後、集塵機4で集塵し、送風様5(吸引ファン]を経
て煙突6から排出している。しかし、この方法では、大
部分のダクト内部において排ガスの流れの中にアルカリ
粉末が同伴されており、排ガスとアルカリ粉末との相対
速度が低い。このためアルカリ粉末が排ガス中の有害ガ
スと遭遇する確率が低く、有害ガス除去率を高めるため
に過剰なアルカリ粉末を投入する必要がある。例えば除
去率50チの場合、モル比で約1.0のアルカリ剤を使
用しなければならない。又除去率70%の場合、モル比
で約2.0必要としている。
[21J] In the conventional dry method, the exhaust gas from the incinerator 1 is passed through the boiler 2 and is led to the reaction chamber 3, where an alkali powder (for example, Ca(OH)z) is spray-mixed and reacted with the harmful gas. The dust is collected by a dust collector 4 and discharged from a chimney 6 through a blower 5 (suction fan).However, in this method, alkaline powder is entrained in the flow of exhaust gas inside most of the ducts. The relative velocity between the exhaust gas and the alkali powder is low.Therefore, the probability that the alkali powder will encounter harmful gases in the exhaust gas is low, and it is necessary to input excess alkali powder to increase the removal rate of harmful gases.For example, the removal rate In the case of 50 inches, it is necessary to use an alkaline agent in a molar ratio of about 1.0.In addition, in the case of a removal rate of 70%, a molar ratio of about 2.0 is required.

一方、通常の経済的なアルカリ剤使用量の範囲では、除
去率の限界は80%であシ、アルカリ剤の量を増加して
も除去率はそれほど増加しない。
On the other hand, within the normal economical range of the amount of alkali agent used, the limit of the removal rate is 80%, and even if the amount of the alkali agent is increased, the removal rate will not increase much.

このため排ガスダクトの形状をU字状に反転させて混合
効果を高めるようにしているものもあるが、必ずしも十
分とはいえない。
For this reason, some systems have reversed the shape of the exhaust gas duct into a U-shape to enhance the mixing effect, but this is not necessarily sufficient.

また別の方法として、セラミックボールに薬剤としてC
a(OH)2スラリーを被覆して充填層を形成し、この
セラミックボールを循環させながら充填層に排ガスを通
し、薬剤と有害ガスを反応させる方法がある。この方法
によれば、充填層に排ガスを通すので薬剤と排ガスとの
相対速度が大きく、境界層へ新たな排ガスが供給されや
すい。このため反応効率が高く、例えdモル比2程度で
除去率90%以上、出口、P度で50ppm以下となる
。しかしこの方法を行なうための装置の構造が複雑でト
ラブルが多く、稼動率が低い問題がある。
Another method is to use C as a drug in a ceramic ball.
There is a method in which a packed layer is formed by coating a(OH)2 slurry, and exhaust gas is passed through the packed layer while circulating the ceramic balls to cause the chemical and harmful gas to react. According to this method, since the exhaust gas is passed through the packed bed, the relative velocity between the drug and the exhaust gas is high, and new exhaust gas is easily supplied to the boundary layer. Therefore, the reaction efficiency is high, and even if the d molar ratio is about 2, the removal rate is 90% or more, and the P degree at the outlet is 50 ppm or less. However, the structure of the equipment used to carry out this method is complicated and causes many troubles, and there are problems in that the operating rate is low.

更にCaQの充填層を形成し、充填層内のCaOを順次
入れ替えながら排ガスを通して排ガス中の有害ガスとC
aOとを反応させる方法がある。
Furthermore, a packed bed of CaQ is formed, and while the CaO in the packed bed is sequentially replaced, the exhaust gas is passed through to remove harmful gases and C from the exhaust gas.
There is a method of reacting with aO.

この方法でも、充填層に排ガスを通すので、CaOと排
ガスとの相対速度が大きく、又境界層へ新たな排ガスが
供給されやすい。このため反応効率が高く、例えばモル
比25で9096以上の除去率が得られている。しかし
この方法においても構造が複雑で稼動率が低い問題があ
る。
Also in this method, since the exhaust gas is passed through the packed bed, the relative velocity between CaO and the exhaust gas is high, and new exhaust gas is easily supplied to the boundary layer. Therefore, the reaction efficiency is high, and for example, a removal rate of 9096 or more is obtained at a molar ratio of 25. However, this method also has the problem of a complicated structure and a low operating rate.

本発明は、上記事情に鑑みてなされたもので、その目的
とするところは、送風機を利用してアルカリ粉末と有害
ガスとの相対速度を高めることによシ、少ないアルカリ
粉末で効率よく有害ガスを除去することができ、しかも
装置の構造が簡単な有害ガスの乾式除去方法を得んとす
るものである。
The present invention has been made in view of the above-mentioned circumstances, and its purpose is to efficiently remove harmful gases using a small amount of alkali powder by increasing the relative velocity between the alkali powder and the harmful gas using a blower. The object of the present invention is to provide a dry method for removing harmful gases that can remove harmful gases and has a simple device structure.

すなわち本発明方法は有害ガスを含む排ガス中にアルカ
リ粉末を噴肪混入し、該粉末混入排ガスを送風機に導き
、次いで集pノ≦機で集塵後大気放出することを特徴と
する。
That is, the method of the present invention is characterized in that alkali powder is injected into the exhaust gas containing harmful gases, the powder-containing exhaust gas is introduced to a blower, and then the dust is collected by a collector and then released into the atmosphere.

以下本発明を図示する実施例を参照して説明する。まず
第2図に示すように廃棄物焼却炉等から発生した排ガス
を反応室11に導き、ここで消石灰等のアルカリ粉末を
加圧空気表蒸気等で噴霧して混合し、アルカリ粉末をf
l(JU等の有害ガスと反応させる。更にアルカリ粉末
と混合した有害ガスを送風機12に導く。この送風機1
2によシ有害ガスとアルカリ粉末とを再度攪拌、混合し
、アルカリ粉末を有害ガスと反応させる。
The present invention will be described below with reference to illustrative embodiments. First, as shown in Fig. 2, exhaust gas generated from a waste incinerator, etc. is led to the reaction chamber 11, where an alkali powder such as slaked lime is sprayed and mixed with pressurized air steam, etc.
1 (reacts with a harmful gas such as JU).The harmful gas mixed with the alkali powder is further guided to the blower 12.
2. The harmful gas and the alkali powder are stirred and mixed again, and the alkali powder is reacted with the harmful gas.

この後排ガスを集塵機13に導いて乗座し、煙突14か
ら排出する。
Thereafter, the exhaust gas is guided to a dust collector 13 and discharged from a chimney 14.

この場合、送風Ft12の型式としてC1、遠心式、軸
流式のいずれでもよいが、設置の容易さを考慮すれば遠
心式のものが好ましい。また遠心式の場合、送風イ゛ジ
12の羽根をラジアルチップ型(鋼板製の曲線羽根12
〜30枚を半径方向に取付けだ羽根車形式の羽根」又は
直線型(鋼板製の直線羽根6〜12枚を半径方向に取付
けた羽根車形式の羽根ンとして、ダスト量の多い排ガス
に対凧するのが好ましい。
In this case, the type of air blower Ft12 may be C1, centrifugal type, or axial flow type, but the centrifugal type is preferable in consideration of ease of installation. In addition, in the case of a centrifugal type, the blades of the blower 12 are of the radial tip type (curved blades 12 made of steel plate).
It can be used as an impeller-type blade with ~30 straight blades attached in the radial direction or as a straight type (impeller-type blade with 6 to 12 straight steel plate blades installed in the radial direction) to prevent exhaust gas with a large amount of dust. It is preferable to do so.

また送風機12の羽根にダストが付着する場合予備のフ
ァンを設けて切替運転をおこなうようにしてもよい。
Further, if dust adheres to the blades of the blower 12, a spare fan may be provided to perform switching operation.

なお送風機12の静圧は70〜100 ruAF程度で
よく、又このような静圧では摩耗について考慮する必要
はとくにない。
Note that the static pressure of the blower 12 may be about 70 to 100 ruAF, and at such a static pressure there is no particular need to consider wear.

またこの24J2図に示す方法では、反応室11と送に
ζl!12との間1(44塵機を設置しない。
In addition, in the method shown in Fig. 24J2, ζl! Between 12 and 1 (44 dust machine will not be installed.

しかしてこの発明によれば送風機12内部で遠心力によ
りアルカリ粒末と排ガス中の有害ガスとが十分に攪拌さ
れ、アルカリ粉末と有害ガスとの相対速度を上昇する。
However, according to the present invention, the alkali powder and the harmful gas in the exhaust gas are sufficiently stirred by the centrifugal force inside the blower 12, and the relative velocity between the alkali powder and the harmful gas is increased.

しかも送風機12内部では、アルカリ粉末が#、壊され
、新しいアルカリ粉末の反応表面が作られることが期待
される。このため第1図のものに比べて反応効率を著し
く上昇することができ、循環する充f1層に排ガスを通
す方法と同等の反応効率をイIIることかできる。
Moreover, inside the blower 12, it is expected that the alkaline powder will be destroyed and a new reaction surface of the alkaline powder will be created. Therefore, the reaction efficiency can be significantly increased compared to the one shown in FIG. 1, and the reaction efficiency can be equivalent to the method of passing the exhaust gas through the circulating packed F1 layer.

また、送風機12で攪拌、混合するので、充填層による
ものに比べて構造が簡庁になシ、トラブルも少なく、稼
動率も高い。
In addition, since the blower 12 is used to stir and mix the mixture, the structure is simpler and less troublesome, and the operating rate is higher than that using a packed bed.

なお本発明は、アルカリ粉末の噴霧ケ所を送風機12の
前段に限らず送KjQ1:zの内部に設けてもよい。
In the present invention, the alkali powder spraying location is not limited to the front stage of the blower 12, but may be provided inside the blower KjQ1:z.

以上説明したように本発明によれば、ファンにより攪拌
してアルカリ粉末と排ガスとの相対速度を高めるので、
反応効率を著しく向上し、少ないアルカリ粉末の添加量
で効率よく有害ガスを除去でき、しかも送風機と集塵機
との配置を替えるという簡単な構成で本発明方法を実施
でき、操業が容易で稼動率が高いなど顕著な効果を奏す
る。
As explained above, according to the present invention, since the relative velocity between the alkali powder and the exhaust gas is increased by stirring with the fan,
The reaction efficiency is significantly improved, harmful gases can be removed efficiently with a small amount of alkali powder added, and the method of the present invention can be carried out with a simple configuration of changing the arrangement of the blower and dust collector, making it easy to operate and improve the operating rate. It has remarkable effects such as high

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は従来の有害ガスの乾式除去方法を示す説明図、
第2図は本発明の一実Ai[i例を示す有害ガスの乾式
除去方法の陸明図である。 11・・・反応室、12・・・送F@、枦、13・・・
集塵機、14・・・煙突。
Figure 1 is an explanatory diagram showing a conventional dry removal method for harmful gases;
FIG. 2 is a diagram of a dry method for removing harmful gases showing an example of the present invention. 11... Reaction chamber, 12... Feed F@, 枦, 13...
Dust collector, 14...chimney.

Claims (1)

【特許請求の範囲】[Claims] 有害ガスを含む排ガス中にアルカリ粉末を噴霧混入し、
該粉末を混入した排ガスを送風機に導き、次いで集塵機
で集塵機大気放出することを特徴とする有害ガスの乾式
除去方法。
Alkaline powder is sprayed into the exhaust gas containing harmful gases,
A dry method for removing harmful gases, characterized in that the exhaust gas mixed with the powder is introduced into a blower, and then discharged into the atmosphere by a dust collector.
JP58159978A 1983-08-31 1983-08-31 Dry removal method for harmful gases Pending JPS6051533A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58159978A JPS6051533A (en) 1983-08-31 1983-08-31 Dry removal method for harmful gases

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58159978A JPS6051533A (en) 1983-08-31 1983-08-31 Dry removal method for harmful gases

Publications (1)

Publication Number Publication Date
JPS6051533A true JPS6051533A (en) 1985-03-23

Family

ID=15705325

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58159978A Pending JPS6051533A (en) 1983-08-31 1983-08-31 Dry removal method for harmful gases

Country Status (1)

Country Link
JP (1) JPS6051533A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61254285A (en) * 1985-05-03 1986-11-12 エスケ−エフ ステイ−ル エンジニアリング アクテイエボラ−グ Waste decomposition treatment method

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61254285A (en) * 1985-05-03 1986-11-12 エスケ−エフ ステイ−ル エンジニアリング アクテイエボラ−グ Waste decomposition treatment method

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