Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JPS6345852B2 - - Google Patents
[go: Go Back, main page]

JPS6345852B2 - - Google Patents

Info

Publication number
JPS6345852B2
JPS6345852B2 JP58057278A JP5727883A JPS6345852B2 JP S6345852 B2 JPS6345852 B2 JP S6345852B2 JP 58057278 A JP58057278 A JP 58057278A JP 5727883 A JP5727883 A JP 5727883A JP S6345852 B2 JPS6345852 B2 JP S6345852B2
Authority
JP
Japan
Prior art keywords
dust
cao
exhaust gas
caco
sox
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.)
Expired
Application number
JP58057278A
Other languages
Japanese (ja)
Other versions
JPS59183817A (en
Inventor
Katsuji Nagahara
Hiroshi Fujama
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.)
Kawasaki Heavy Industries Ltd
Original Assignee
Kawasaki Heavy Industries 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 Kawasaki Heavy Industries Ltd filed Critical Kawasaki Heavy Industries Ltd
Priority to JP58057278A priority Critical patent/JPS59183817A/en
Publication of JPS59183817A publication Critical patent/JPS59183817A/en
Publication of JPS6345852B2 publication Critical patent/JPS6345852B2/ja
Granted legal-status Critical Current

Links

Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/30Incineration of waste; Incinerator constructions; Details, accessories or control therefor having a fluidised bed

Landscapes

  • Engineering & Computer Science (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Treating Waste Gases (AREA)
  • Fluidized-Bed Combustion And Resonant Combustion (AREA)
  • Chimneys And Flues (AREA)

Description

【発明の詳細な説明】 本発明は、産業廃棄物焼却炉排ガス、都市ごみ
焼却炉排ガスなど(以下、単に廃棄物焼却炉排ガ
スという)のようにHCl、SOxおよびダストを含
む排ガスを、石灰石を用いて効率よくかつ低コス
トで処理する方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention aims to convert waste gas containing HCl, SOx, and dust, such as industrial waste incinerator exhaust gas and municipal waste incinerator exhaust gas (hereinafter simply referred to as waste incinerator exhaust gas), to limestone. The present invention relates to a method for processing efficiently and at low cost.

一般に、廃棄物焼却炉排ガス、たとえば都市ご
み焼却炉排ガスにはHClが200〜1000ppm、SOx
が10〜100ppm含まれており、このHCl、SOxを
CaCO3を用いて化学反応させCaCO2、CaSO4
して分離・除去する乾式法は従来から良く知られ
ている。この乾式法は、アルカリ水溶液に有害ガ
スを吸収、溶解させて排水として除去する湿式法
に比べて、その排水を処理しなければならないな
どの問題がなく簡易な方法であるので安価となる
という利点を有しているが、CaCO3の利用率が
それ程高くなく、また熱ロスが多いほどの問題点
があつた。
Generally, waste incinerator exhaust gas, such as municipal waste incinerator exhaust gas, contains 200 to 1000 ppm of HCl and SOx.
Contains 10 to 100 ppm, and this HCl, SOx
The dry method of chemically reacting CaCO 3 and separating and removing it as CaCO 2 and CaSO 4 has been well known. Compared to the wet method, which absorbs and dissolves harmful gases in an alkaline aqueous solution and removes them as wastewater, this dry method has the advantage that it is a simple method that does not require treatment of the wastewater and is therefore inexpensive. However, there were problems in that the utilization rate of CaCO 3 was not very high and there was a lot of heat loss.

本発明は上記の問題点を解決するためになされ
たもので、廃棄物焼却流動床炉に石灰石
(CaCO3)を投入して排ガス中のHCl、SOxを除
去する方法において、流動床炉内で活性化された
CaO、珪砂などの流動媒体、反応生成物、不燃
物、ダストの混合物を炉底から抜き出し、反応生
成物、不燃物、ダストを分離した後、CaOおよび
流動媒体を2枚の支持体間を低速度で落下させる
移動層式有害ガス・ダスト除去装置に投入して流
動床炉からの排ガスをこの移動層内に通過させ
て、CaOと排ガス中の含有HCl、SOxとを反応さ
せると同時に排ガス中のダストを捕集した後、反
応生成物およびダストとCaCO3、CaOおよび流
動媒体とに分離し、CaCO3、CaOおよび流動媒
体を再び流動床炉に供給して発生HCl、SOxの除
去に再利用することにより、低コストでHCl、
SOx、ダストを同時に除去することができる廃棄
物焼却炉排ガス中の有害成分・ダスト除去方法を
提供せんとするものである。
The present invention was made to solve the above problems, and is a method for removing HCl and SOx from exhaust gas by introducing limestone (CaCO 3 ) into a waste incineration fluidized bed furnace. activated
A mixture of CaO, a fluid medium such as silica sand, reaction products, noncombustibles, and dust is extracted from the furnace bottom, and after separating the reaction products, noncombustibles, and dust, CaO and the fluid medium are passed between two supports. The exhaust gas from the fluidized bed furnace is fed into a moving bed type harmful gas/dust removal device that drops at a high speed, and the exhaust gas from the fluidized bed furnace is passed through this moving bed to react with CaO and HCl and SOx contained in the exhaust gas. After collecting the dust of By using HCl at low cost,
The purpose of this invention is to provide a method for removing harmful components and dust from waste incinerator exhaust gas that can simultaneously remove SOx and dust.

以下、本発明の構成を図面に基づいて説明す
る。1は流動床炉で、珪砂などの流動媒体(以
下、砂という)が用いられる。流動床炉1に脱
塩・脱硫剤として一定粒径のCaCO3を投入する
と、大部分はCaOまで熱解離して活性化し、発生
HCl、SOxガスと反応し脱塩、脱硫が行なわれ
る。この反応は、CaO粒子の表面で起こり、
CaCl2や、CaSO4のような反応生成物になるが、
砂などの撹拌作用により、反応生成物ははがされ
て殆ど粉体の状態で排ガスに同伴されて流動床炉
1の上部から排出される。流動床炉1内ではつぎ
の反応が行なわれる。
Hereinafter, the configuration of the present invention will be explained based on the drawings. 1 is a fluidized bed furnace in which a fluidized medium such as silica sand (hereinafter referred to as sand) is used. When CaCO 3 of a certain particle size is introduced into the fluidized bed furnace 1 as a desalination/desulfurization agent, most of it is thermally dissociated to CaO, activated, and generated.
Reacts with HCl and SOx gas to perform desalination and desulfurization. This reaction occurs on the surface of CaO particles,
Reaction products such as CaCl 2 and CaSO 4 are produced,
Due to the stirring action of sand or the like, the reaction product is peeled off and is discharged from the upper part of the fluidized bed furnace 1 in a mostly powdered state along with the exhaust gas. The following reaction takes place in the fluidized bed furnace 1.

CaCO3→CaO+CO2 CaO+2HCl→CaCl2+H2O CaCO3+2HCl→CaCl2+H2O+CO2 CaO+SO2→CaSO3 CaSO3+1/202→CaSO4 一方、活性化されたCaO(1部反応したCaCO2
を含む)と砂との混合物は流動床炉1の炉底から
抜き出され、3段形振動ふるいなどの分離装置2
で不燃物、ダスト、反応生成物(CaCl2
CaSO4)を分離除去し、CaOおよび砂は移動層式
有害ガス・ダスト除去装置3へ搬送される。4は
流動媒体排出装置、5は中間ホツパ、6は余剰
CaO・砂抜出管である。
CaCO 3 →CaO+CO 2 CaO+2HCl→CaCl 2 +H 2 O CaCO 3 +2HCl→CaCl 2 +H 2 O+CO 2 CaO+SO 2 →CaSO 3 CaSO 3 +1/20 2 →CaSO 4 On the other hand, activated CaO (partially reacted CaCO 2
) and sand is extracted from the bottom of the fluidized bed furnace 1 and passed through a separation device 2 such as a three-stage vibrating screen.
Incombustibles, dust, reaction products (CaCl 2 ,
CaSO 4 ) is separated and removed, and CaO and sand are transported to a moving bed type harmful gas/dust removal device 3. 4 is a fluidized medium discharge device, 5 is an intermediate hopper, and 6 is a surplus
This is a CaO/sand extraction pipe.

移動層式有害ガス・ダスト除去装置3内には、
ルーバ、孔明板、金網などからなる2枚の支持体
7が対設されており、この支持体7,7間にCaO
および砂を充填し低速度で落下する移動層8とな
るように構成されている。搬送されてきたCaOと
砂との混合物は、支持体7,7間を自重落下しつ
つ排ガスと接触し、排ガス中に含まれるHCl、
SOxガスを反応吸収すると同時に、排ガス中のダ
ストもCaOと砂との混合物の層で捕集される。な
お10は廃熱ボイラ、ガス冷却塔、熱交換器など
の排ガス冷却装置である。移動層式有害ガス・ダ
スト除去装置3内での反応はつぎの通りである。
Inside the moving bed type harmful gas/dust removal device 3,
Two supports 7 made of louvers, perforated plates, wire mesh, etc. are placed opposite each other, and between these supports 7, CaO
The moving layer 8 is filled with sand and falls at a low speed. The conveyed mixture of CaO and sand falls between the supports 7 and 7 under its own weight and comes into contact with the exhaust gas, and the HCl contained in the exhaust gas,
At the same time as SOx gas is reacted and absorbed, dust in the exhaust gas is also collected in a layer of CaO and sand mixture. Note that 10 is an exhaust gas cooling device such as a waste heat boiler, a gas cooling tower, and a heat exchanger. The reaction within the moving bed type harmful gas/dust removal device 3 is as follows.

CaO+2HCl→CaCl2+H2O CaO+SO3→CaSO3 CaSO3+1/202→CaSO4 CaO+CO2→CaCO3 移動層式有害ガス・ダスト除去装置3から排出
される混合物には、ダスト、反応生成物
(CaCl2、CaSO4)が含まれているので、これを
振動ふるいなどの分離装置11により除去し、
CaCO3、CaOおよび砂の混合物を流動床炉1に
投入し再利用する。12は送風機、13はサイク
ロン、14は空気分散板、15は風箱である。
CaO+2HCl→CaCl 2 +H 2 O CaO+SO 3 →CaSO 3 CaSO 3 +1/20 2 →CaSO 4 CaO+CO 2 →CaCO 3 The mixture discharged from the moving bed harmful gas/dust removal device 3 includes dust, reaction products ( CaCl 2 , CaSO 4 ) is included, so this is removed using a separator 11 such as a vibrating sieve.
A mixture of CaCO 3 , CaO and sand is put into the fluidized bed furnace 1 and reused. 12 is a blower, 13 is a cyclone, 14 is an air distribution plate, and 15 is a wind box.

CaOと砂との混合物は炉底から抜き出された
後、移動層式有害ガス・ダスト除去装置に至るま
での間に放熱により冷却されるが、移動層式有害
ガス・ダスト除去装置3において、排ガスの顕熱
が与えられ再度加熱されるので、熱ロスを小さく
するという利点がある。なお循環して使用する流
動媒体は、Ca系と砂との混合物に限ることなく、
Ca系単独でも可能である。
After the mixture of CaO and sand is extracted from the furnace bottom, it is cooled by heat radiation before reaching the moving bed type harmful gas and dust removal device 3. Since the sensible heat of the exhaust gas is given and heated again, it has the advantage of reducing heat loss. The fluid medium to be circulated and used is not limited to a mixture of Ca-based and sand.
It is also possible to use Ca alone.

以上説明したように、本発明の方法は廃棄物焼
却流動床炉に脱塩・脱硫剤としてCaCO3を投入
し、炉内で活性化されたCaOと砂との混合物を移
動層式有害ガス・ダクト除去装置の反応剤兼ろ過
材として用い、排ガスに含まれるHCl、SOxを反
応吸収し、かつダストも同時に捕集した後、ダス
トおよび反応生成物を分離除去した高温のCaO、
CaCO3と砂との混合物を流動床炉に投入して再
利用するものであるから、安価なCaCO3が利用
できる上に、CaCO3の利用率がきわめて高くな
り、このためランニングコストが安くなり、また
循環して使用するCaCO3と砂との混合物を排ガ
スで加熱して流動床炉に投入するため、熱ロスが
小さくなる、などの効果を有している。
As explained above, the method of the present invention involves introducing CaCO 3 as a desalination/desulfurization agent into a waste incineration fluidized bed furnace, and converting the activated CaO and sand mixture in the furnace into a moving bed type harmful gas. High-temperature CaO is used as a reactant and filter material in duct removal equipment to react and absorb HCl and SOx contained in exhaust gas, and also collect dust at the same time, after which dust and reaction products are separated and removed.
Since the mixture of CaCO 3 and sand is put into a fluidized bed furnace and reused, not only can cheap CaCO 3 be used, but the utilization rate of CaCO 3 is extremely high, which reduces running costs. Furthermore, since the mixture of CaCO 3 and sand that is used in circulation is heated with exhaust gas and then fed into the fluidized bed furnace, it has the effect of reducing heat loss.

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

図面は本発明の方法を実施する装置の一例を示
す系統的説明図である。 1……流動床炉、2……分離装置、3……移動
層式有害ガス・ダスト除去装置、4……流動媒体
排出装置、5……中間ホツパ、6……余剰CaO・
砂抜出管、7……支持体、8……移動層、10…
…冷却装置、11……分離装置、12……送風
機、13……サイクロン、14……空気分散板、
15……風箱。
The drawing is a systematic explanatory diagram showing an example of an apparatus for carrying out the method of the present invention. 1... Fluidized bed furnace, 2... Separation device, 3... Moving bed harmful gas/dust removal device, 4... Fluidized medium discharge device, 5... Intermediate hopper, 6... Excess CaO.
Sand extraction pipe, 7... Support, 8... Moving layer, 10...
...cooling device, 11 ... separation device, 12 ... blower, 13 ... cyclone, 14 ... air distribution plate,
15...Wind box.

Claims (1)

【特許請求の範囲】[Claims] 1 廃棄物焼却流動床炉に石灰石を投入して排ガ
ス中のHCl、SOxを除去する方法において、流動
床炉内で活性化されたCaO、流動媒体、反応生成
物、不燃物、ダストの混合物を炉底から抜き出
し、反応生成物、不燃物、ダストを分離した後、
CaOおよび流動媒体を移動層式有害ガス・ダスト
除去装置に投入して2枚の支持体間を低速度で落
下させつつ、流動床炉からの排ガスを移動層内に
通過させて、CaOと排ガス中の含有HCl、SOxと
を反応させると同時に排ガス中のダストを捕集し
た後、反応生成物およびダストと、CaCO3
CaOおよび流動媒体とに分離し、CaCO3、CaO
および流動媒体を流動床炉に供給して発生HCl、
SOxの除去に再利用することを特徴とする廃棄物
焼却炉排ガス中の有害成分・ダスト除去方法。
1 In a method of removing HCl and SOx from exhaust gas by introducing limestone into a waste incineration fluidized bed furnace, a mixture of activated CaO, fluidized medium, reaction products, incombustibles, and dust is After extracting from the bottom of the furnace and separating reaction products, incombustibles, and dust,
CaO and a fluidized medium are introduced into a moving bed type noxious gas/dust removal device and are allowed to fall between two supports at low speed, while the exhaust gas from the fluidized bed furnace is passed through the moving bed. After collecting the dust in the exhaust gas at the same time as reacting the HCl and SOx contained in it, the reaction products and dust, CaCO 3 ,
Separates into CaO and fluid medium, CaCO 3 , CaO
and HCl generated by supplying the fluidized medium to the fluidized bed furnace,
A method for removing harmful components and dust from waste incinerator exhaust gas, which is characterized by reuse for removing SOx.
JP58057278A 1983-03-31 1983-03-31 Removal of harmful component and dust in waste gas from waste incinerator Granted JPS59183817A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58057278A JPS59183817A (en) 1983-03-31 1983-03-31 Removal of harmful component and dust in waste gas from waste incinerator

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58057278A JPS59183817A (en) 1983-03-31 1983-03-31 Removal of harmful component and dust in waste gas from waste incinerator

Publications (2)

Publication Number Publication Date
JPS59183817A JPS59183817A (en) 1984-10-19
JPS6345852B2 true JPS6345852B2 (en) 1988-09-12

Family

ID=13051066

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58057278A Granted JPS59183817A (en) 1983-03-31 1983-03-31 Removal of harmful component and dust in waste gas from waste incinerator

Country Status (1)

Country Link
JP (1) JPS59183817A (en)

Families Citing this family (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0611376B2 (en) * 1984-07-25 1994-02-16 バブコツク日立株式会社 Method for removing sulfur compounds and halogen compounds in exhaust gas
JPS62142907A (en) * 1985-12-18 1987-06-26 Mitsubishi Heavy Ind Ltd Pulverized coal burner of slag tap type
JPS6330729U (en) * 1986-08-06 1988-02-29
US5379705A (en) * 1992-11-11 1995-01-10 Kawasaki Jukogyo Kabushiki Kaisha Fluidized-bed incinerator
JP2977743B2 (en) * 1995-07-28 1999-11-15 川崎重工業株式会社 Plastic waste gasification gas treatment method
JP2004108688A (en) * 2002-09-19 2004-04-08 Hitachi Zosen Corp Method and apparatus for burning waste mainly composed of organic phosphorus compounds
JP4543629B2 (en) * 2003-07-09 2010-09-15 株式会社Inax Exhaust gas treatment apparatus, calcium fluoride recovery method, and fluorine recovery method
JP6339360B2 (en) * 2013-12-19 2018-06-06 川崎重工業株式会社 BOILER WITH CORROSION CONTROL DEVICE AND BOILER CORROSION CONTROL METHOD
CN110180493B (en) * 2019-04-17 2022-04-19 中节能(合肥)可再生能源有限公司 Active filter material for removing calcium ions, and preparation method and application thereof

Also Published As

Publication number Publication date
JPS59183817A (en) 1984-10-19

Similar Documents

Publication Publication Date Title
CN110560019A (en) efficient, energy-saving and environment-friendly waste activated carbon regeneration method
AU692014B2 (en) Method for separating gaseous pollutants from hot process gases
JPH10216476A (en) Exhaust gas treatment method and apparatus
JPH07299328A (en) Method of purifying exhaust gas
EP0170355B1 (en) Emission control process for combustion flue gases
JPS6345852B2 (en)
CA1296865C (en) Method and system for purifying exhaust gas
JP2000140627A (en) Dioxin removing material, dioxin removing method and regenerating method of dioxin removing material
JPH0376963B2 (en)
JPS5466380A (en) Treating apparatus for exhaust gas containing hydrogen chloride
JPS61259747A (en) Multistage jet stream bed gas-solid contact apparatus
JPS6025531A (en) Dry purification method for exhaust gas
JPH06170157A (en) Treatment of exhaust gas
JPH05228330A (en) Dry treatment of waste gas
JPS6053804B2 (en) Effective use of sludge melting slag
JP3306748B2 (en) Method and apparatus for treating limestone in response to circulating fluidized bed combustion requirements
CN107376613B (en) Device and method for drying carbide slag and removing dust from flue gas desulfurization
JPS6230803B2 (en)
JPS6134024Y2 (en)
JP3059152U (en) Exhaust gas treatment equipment
JPS6271518A (en) Method for removing harmful component and dust in waste gas from rubbish incinerator
JP2739258B2 (en) Method for removing hydrogen chloride and / or sulfur oxide in incinerator
JPS6119779Y2 (en)
JPS6216169Y2 (en)
JPS6133216A (en) Removing method of sulfur compound and halogen compound in waste gas