JPS59183817A - Removal of harmful component and dust in waste gas from waste incinerator - Google Patents
Removal of harmful component and dust in waste gas from waste incineratorInfo
- Publication number
- JPS59183817A JPS59183817A JP58057278A JP5727883A JPS59183817A JP S59183817 A JPS59183817 A JP S59183817A JP 58057278 A JP58057278 A JP 58057278A JP 5727883 A JP5727883 A JP 5727883A JP S59183817 A JPS59183817 A JP S59183817A
- Authority
- JP
- Japan
- Prior art keywords
- dust
- cao
- sand
- mixture
- furnace
- 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
Links
Classifications
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/30—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having a fluidised bed
Abstract
Description
【発明の詳細な説明】
本発明は、産業廃棄物焼却炉排ガス、都市こみ焼却炉排
ガスなど(以下、単に廃葉物焼却炉排ガスとhう)のよ
うにHC召、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ff1
g+するものである。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to exhaust gas containing HC, SOx, and dust, such as industrial waste incinerator exhaust gas, municipal waste incinerator exhaust gas, etc. (hereinafter simply referred to as waste incinerator exhaust gas). A method of processing ff1 efficiently and at low cost using limestone
g+.
一般r、廃棄物焼却炉排カス、たとえば都市こミ焼却炉
排カスvrtdHcIlが200〜100’Oppm、
SOxが10〜1ooppm含まれており、cノHC6
、SOx & CaCO5f用イテ化学反応すセCaC
4、Ca S O<として分離・除去する乾式法は従来
から良く知られている。この乾式法に、アルカリ水溶液
に有害カスを吸収、酵解させて排水として1余去する湿
式法f比へて、その排水を処理しなければならないi
ト(D 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、寸た熱ロスが多いなどの問題点かあうた。General r, waste incinerator waste, for example, municipal waste incinerator waste vrtdHcIl is 200 to 100'Oppm,
Contains 10 to 1 ooppm of SOx, cNOHC6
, SOx & CaCO5f Ite chemical reaction process CaC
4. A dry method for separating and removing Ca SO< has been well known. In addition to this dry method, the wastewater must be treated using a wet method in which harmful scum is absorbed in an aqueous alkaline solution, fermented, and left as wastewater.
(D) It has the advantage of being inexpensive because it is a simple method without any problems, but it has problems such as the utilization rate of CaCO3 is not so high and there is a large amount of heat loss.
本発明は上記の問題点を解決するためになされだもので
、廃棄物焼却流動床炉に石灰石(CaC03)を投入し
て排ガス中のHCβ、SOxを除去する方法において、
流動床炉内で活性化されたC、aO,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、反応化・載物、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こ、Ca
Oと排ガス中の含有HC(1,SOxとを反応させると
同時に排ガス中のタストを捕集した後、反応生成物およ
びり゛ストとCaCO3、CaOおよび流動媒体とに分
離し、CaCO5、CaOおよび流ylJ1媒体を1与
び流動床炉f供給して発生HC1,SOxの除去に再利
用することにより、低コストでHCn、 SOx、ダス
トを同時ニ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・ゲ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 HCβ and SOx from exhaust gas by introducing limestone (CaC03) into a waste incineration fluidized bed furnace.
After extracting the mixture of activated fluidized media such as C, aO, and silica sand, reaction products, noncombustibles, and dust from the bottom of the furnace and separating the reacted materials, noncombustibles, and dust,
CaO and a fluidized medium are introduced into a moving bed type harmful gas/dust removal device that falls between two supports at a low speed, and the exhaust gas from the fluidized bed furnace is passed through this moving bed.
After reacting O with HC (1, SOx) contained in the exhaust gas and collecting the tast in the exhaust gas, the reaction product and tast are separated into CaCO3, CaO and a fluidized medium, HCn, SOx, and dust can be removed at the same time at low cost by supplying fluidized bed furnace F and reusing it to remove generated HC1 and SOx. The purpose is to provide a method for removing harmful components and guests.
以下、未発明の構成を図面に基づいて説明する。Hereinafter, an uninvented configuration will be explained based on the drawings.
1は流■1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CaC0aを投入すると、大部分子rica−
0まで熱解離して活性化し、発生HC6、SOxガスと
反応し脱塩、脱硫が行なわれる。この反応&:t−Ca
O粒子の表面で起こり、CaC4や、Ca 504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η1−ガスに同
伴されて流動床炉】の上部から排出される。流動床炉1
内ではつきの反応が行なわれる。1 is a one-bed furnace, in which a fluid medium such as silica sand (hereinafter referred to as sand) is used. When CaC0a of a certain particle size is introduced into the fluidized bed furnace 1 as a desalination/desulfurization agent, most of the molecules rica-
It is activated by thermal dissociation to zero and reacts with generated HC6 and SOx gas to perform desalination and desulfurization. This reaction &:t-Ca
This occurs on the surface of O particles, resulting in reaction products such as CaC4 and Ca504, but due to the stirring action of sand, the reaction products are peeled off and are entrained in the η1-gas in almost a powder state. It is discharged from the top of the fluidized bed furnace. Fluidized bed furnace 1
Inside, a reaction takes place.
CaCO3→CaO+CO2
CaO+ 2HC1→CaC4+H2OCaC0a
+ 2HCj? −+ CaC4+ Iイ2 0
+ CO2CaO+S02→Ca5O3
Ca 503 + 1/ 202 →Ca 504
一方、活性化されたCaO(一部反応したC a (−
1j 2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Jヒ振W1ふるいなどの分離g置2
で不燃物、り゛スト、反応生成物(CaC4、Ca5O
4)を分離除去し、CaOおよび#は拶催1層式有害ガ
ス・ダスト除去装置3へ搬送される。4け流u1媒体排
出装置、5は中量1ホッパ、6は余剰CaO・砂抜出管
である。CaCO3→CaO+CO2 CaO+ 2HC1→CaC4+H2OCaC0a
+2HCj? -+ CaC4+ Ii2 0
+ CO2CaO+S02 → Ca5O3 Ca 503 + 1/ 202 → Ca 504
On the other hand, activated CaO (partially reacted Ca (-
A mixture of sand and sand is extracted from the bottom of the fluidized bed furnace 1, and passed through a separation device 2 such as a 3-stage J Hi-Shin W1 sieve.
Incombustibles, lysts, reaction products (CaC4, Ca5O
4) is separated and removed, and CaO and # are conveyed to the single-layer noxious gas/dust removal device 3. 4 is a flow u1 medium discharge device, 5 is a medium capacity 1 hopper, and 6 is an excess CaO/sand extraction pipe.
$勅層式有害ガス・タスト除去装置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聞πCaOおよび砂を充填し低
速度で落下する!8動層8となるように構成されている
。搬送されてきだCaOと砂との混合物に1、支持体7
.7間を自重落下1一つつ排ガスと接触し、排ガス中π
含捷れるHCβ、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lOは1ノロ熱ボイラ、ガス冷却塔、熱交換
器などの排ガス冷却装置−である。#側層式有害ガス・
り゛スト除去装W 3内での反応につぎの11]りであ
る。Inside the $ layer type harmful gas/tast removal device 3, there are louvers,
Two supports 7 made of perforated plates, wire mesh, etc. are placed opposite each other, and these supports 7.7 are filled with πCaO and sand and fall at a low speed! It is configured to have eight dynamic layers. The conveyed mixture of CaO and sand has 1 and support 7
.. One by one, the dead weight falls between 7 and π in the exhaust gas.
At the same time as reacting and absorbing HCβ and SOx gas,
Dust in the exhaust gas is also collected in a layer of CaO and sand mixture. Note that IO is an exhaust gas cooling device such as a one-norm heat boiler, a gas cooling tower, or a heat exchanger. #Side layer type harmful gas・
The following 11] describes the reaction inside the strike removal device W3.
CaO+ 2HCn−+CaC4+ H20CaO+
SO3−> Ca5O,+
Ca 503 + 1/ 202 →Ca 504Ca
O+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πは、タスト、反応生成物(CaC4、Ca504
)が含捷れているので、これを振動ふるいなどの分離装
置t、 11 Kより除去し、CaCO3、CaOおよ
び砂の混合物を流動床炉lK投入し再利用する。12は
送風機−1:l−11−イクUン、14は空気分散板、
15は風箱である。CaO+ 2HCn-+CaC4+ H20CaO+
SO3->Ca5O, + Ca 503 + 1/202 → Ca 504Ca
O+CO2→CaCO3 The mixture π discharged from the moving bed type harmful gas/dust removal device 3 contains Tast, reaction products (CaC4, Ca504
), it is removed from a separator such as a vibrating sieve, and a mixture of CaCO3, CaO and sand is put into a fluidized bed furnace and reused. 12 is a blower-1:l-11-Ikuun, 14 is an air distribution plate,
15 is a wind box.
CaOと4(Jンとの混合物は炉底から抜き出された後
、移動層式自害ガス・ダスト除去装置に至るまでの11
)1に放熱により冷却されるが一* 1J(J1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
λられ再度加熱されるので、熱LJスを小さくするとい
う利点がある。なお循環して便用する流動媒体は、Ca
系と4沙との混合物に限ることなく−Ca系屯独でも可
能である。After the mixture of CaO and 4 (J) is extracted from the bottom of the furnace, it is transported to a moving bed type self-harming gas and dust removal device.
) 1 is cooled by heat radiation, but 1 * 1J (J) In the 1-layer noxious gas/dust removal device 3, the sensible heat of the exhaust gas is given to it and heated again, which has the advantage of reducing the heat LJ. The fluid medium that is circulated for use is Ca
It is not limited to a mixture of a Ca-based compound and a 4-silicon compound, and a -Ca-based compound is also possible.
以上説り1したように、未発E!1.1の方法にb6棄
物焼却流肋床炉に脱塩・脱硫剤としrcacO3を投入
し、炉内で7古性化されたCaOと砂との混合物を移動
層式有害ガス・タスト除去装置行の反応剤兼ろ過材とし
て用い、排ガスf含まれるHC(J、SOxを反応吸収
し、かつタストも同時f捕集した後、タストおよび反b
U生成物を分離除去した高温のCaO、CaCO5と砂
との混合物を流動床炉f投入して再利用するものである
から、安価fxCaCO3が利用できる上に、CaCO
7の利用率がきわめて1団くなり、このだめランニング
コストが安くなり、捷だ循環して使用するCaCO5と
砂との混合物を排ガスで加熱して流動床炉π投入するだ
め、熱ロスが小さくなるーなどの効果を有している。As I explained above, unreleased E! In the method of 1.1, rcacO3 is added as a desalination/desulfurization agent to a B6 waste incineration cost-bed furnace, and the mixture of aged CaO and sand is removed in a moving bed using a moving bed method. It is used as a reactant and filtration material in the equipment line, and after reacting and absorbing HC (J, SOx) contained in the exhaust gas and simultaneously collecting Tast,
Since the mixture of high-temperature CaO, CaCO5 and sand from which U products have been separated and removed is fed into the fluidized bed furnace f and reused, cheap fxCaCO3 can be used, and CaCO
The utilization rate of 7 is extremely low, the running cost is low, and the heat loss is small because the mixture of CaCO5 and sand, which is used by circulation, is heated with exhaust gas and then input into the fluidized bed furnace. It has the effect of becoming.
図面は本発明の方法f/実施する装置の一例を示寸系統
的h)a明図である。
1・・・流動床炉、2・・・分離装置、3・・・移動層
式有害ガス・ゲス1−除去装置、4・・・流動媒体排出
装置、5・・・中間ホラ・べ、6・・・余剰CaO・砂
抜出管、7・・・支持一体、8・・・移亜1層、10・
・・冷却装置、11・・・分i!1ff(、装置d 、
l 2− 送JtL 機、13 ・i−イク[J ン
、14・・・窄気分散板、15・・・風箱The drawings are schematic diagrams illustrating an example of an apparatus for implementing the method f/of the invention. DESCRIPTION OF SYMBOLS 1...Fluidized bed furnace, 2...Separation device, 3...Moving bed type noxious gas/gas 1-removal device, 4...Fluidized medium discharge device, 5...Intermediate hollow container, 6 ...Excess CaO/sand extraction pipe, 7...Support integrated, 8...Movement 1 layer, 10.
...Cooling device, 11...minutes i! 1ff(, device d,
l 2- sending JtL machine, 13 ・i-ik [J n, 14... constriction air dispersion plate, 15... wind box
Claims (1)
HC(1,SOxを1余去する方法において、流動床炉
内で活性化されたCaα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一反応生成物、不
燃物、ゲストを分離した後、CaOおよび流動媒体を移
ω1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゛り、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H
Cβ、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、Ca
Oおよび流U、+媒体を流動床炉に供給して発生HCI
、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・ゲスト除去方法。1 In the method of charging limestone into a waste incineration fluidized bed furnace to remove HC (1, SOx) from the exhaust gas, activated Caα fluidized medium, reaction products, incombustibles, dust in the fluidized bed furnace After extracting the mixture from the bottom of the furnace and separating the reaction products, incombustibles, and guests, the CaO and fluidized medium are transferred to a one-layer noxious gas/dust removal device and passed between two supports at low speed. While dropping, the exhaust gas from the fluidized bed furnace is passed through the moving bed to remove CaO and H contained in the exhaust gas.
After collecting dust in the exhaust gas at the same time as reacting Cβ and SOx, the reaction products and dust are combined with CaCO3
, CaO and a fluid medium, CaCO3, Ca
O and stream U, + medium are fed to a fluidized bed furnace to generate HCI
, a method for removing harmful components and guests from waste incinerator exhaust gas, which is characterized in that it is reused for removing SOx.
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 true JPS59183817A (en) | 1984-10-19 |
JPS6345852B2 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) |
Cited By (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS6133216A (en) * | 1984-07-25 | 1986-02-17 | Babcock Hitachi Kk | Removing method of sulfur compound and halogen compound in waste 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 | ||
EP0597458A1 (en) * | 1992-11-11 | 1994-05-18 | Kawasaki Jukogyo Kabushiki Kaisha | Fluidized-bed incinerator |
JPH0938462A (en) * | 1995-07-28 | 1997-02-10 | Kawasaki Heavy Ind Ltd | Treating method of gas produced by gasification of plastic waste |
JP2004108688A (en) * | 2002-09-19 | 2004-04-08 | Hitachi Zosen Corp | Combustion method for waste containing organic phosphorus compound as main substance and its device |
JP2005028241A (en) * | 2003-07-09 | 2005-02-03 | Inax Corp | Exhaust gas treatment apparatus, method for recovering calcium fluoride and method for recovering fluorine |
JP2015117910A (en) * | 2013-12-19 | 2015-06-25 | 川崎重工業株式会社 | Boiler with corrosion suppression device and boiler corrosion suppression method |
CN110180493A (en) * | 2019-04-17 | 2019-08-30 | 中节能(合肥)可再生能源有限公司 | A kind of active filter and its preparation method and application for removing calcium ion |
-
1983
- 1983-03-31 JP JP58057278A patent/JPS59183817A/en active Granted
Cited By (11)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS6133216A (en) * | 1984-07-25 | 1986-02-17 | Babcock Hitachi Kk | Removing method of sulfur compound and halogen compound in waste 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 | ||
EP0597458A1 (en) * | 1992-11-11 | 1994-05-18 | Kawasaki Jukogyo Kabushiki Kaisha | Fluidized-bed incinerator |
JPH0938462A (en) * | 1995-07-28 | 1997-02-10 | Kawasaki Heavy Ind Ltd | Treating method of gas produced by gasification of plastic waste |
JP2004108688A (en) * | 2002-09-19 | 2004-04-08 | Hitachi Zosen Corp | Combustion method for waste containing organic phosphorus compound as main substance and its device |
JP2005028241A (en) * | 2003-07-09 | 2005-02-03 | Inax Corp | Exhaust gas treatment apparatus, method for recovering calcium fluoride and method for recovering fluorine |
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 |
JP2015117910A (en) * | 2013-12-19 | 2015-06-25 | 川崎重工業株式会社 | Boiler with corrosion suppression device and boiler corrosion suppression method |
CN110180493A (en) * | 2019-04-17 | 2019-08-30 | 中节能(合肥)可再生能源有限公司 | A kind of active filter and its preparation method and application for removing calcium ion |
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 |
---|---|
JPS6345852B2 (en) | 1988-09-12 |
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