JPS61197910A - Waste material combustion method removing hydrogen chloride and its device - Google Patents
Waste material combustion method removing hydrogen chloride and its deviceInfo
- Publication number
- JPS61197910A JPS61197910A JP4043385A JP4043385A JPS61197910A JP S61197910 A JPS61197910 A JP S61197910A JP 4043385 A JP4043385 A JP 4043385A JP 4043385 A JP4043385 A JP 4043385A JP S61197910 A JPS61197910 A JP S61197910A
- Authority
- JP
- Japan
- Prior art keywords
- gas
- hydrogen chloride
- ash
- chloride
- 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
Landscapes
- Chimneys And Flues (AREA)
- Gasification And Melting Of Waste (AREA)
Abstract
Description
【発明の詳細な説明】
(産業上の利用分野)
本発明は可燃性廃棄物を燃焼乾留してガスを生成し、あ
るいは焼却して排ガスを放出する際に、乾留ガス中の塩
化水素を除去して腐食性のない浄化したガスを取出すよ
うにし、あるいは焼却排ガスを無害として大気へ放出す
るようにした塩化水素除去燃焼に関するものである。Detailed Description of the Invention (Industrial Application Field) The present invention removes hydrogen chloride from the carbonization gas when combustible waste is burned and carbonized to produce gas or incinerated to release exhaust gas. The present invention relates to hydrogen chloride removal combustion in which purified non-corrosive gas is extracted, or incineration exhaust gas is released into the atmosphere as harmless.
(従来の技術)
都市塵芥や各種産業廃棄物は塩化ビニール、クロロブレ
ンゴム等、燃焼によって塩化水素を発生する物質を含む
場合が多く、乾留ガスとして熱源に使用する場合は各機
器を腐食し、また焼却するときは大気を汚染するという
障害が生ずる。(Conventional technology) Municipal dust and various industrial wastes often contain substances that generate hydrogen chloride when burned, such as vinyl chloride and chloroprene rubber, and when used as a heat source as carbonized gas, they corrode various equipment. Also, when incinerated, there is a problem in that it pollutes the atmosphere.
この塩化水素を除去する先行技術としては、特開昭54
−37378号公報、および特開昭54−150865
号公報に開示されているが、前者の特開昭54−373
78号公報では流動式焼却炉を採用し、炉上部空間に石
灰粉を導入して炉内で塩化水素と接触反応させ、上記塩
化水素は塩化カルシウムとして石灰粉表面に附着させ、
その後この塩化カルシウムの附着した石灰粉を炉外にお
いて電気集塵機やマルチサイクロンなどの集塵装置を用
いて除塵しており、後の特開昭54−150865号公
報では、廃棄物焼却炉内の廃棄物供給用ホッパー投入箇
所へ直接カルシウム化合物を供給して、廃棄物層から発
生する塩化水素と直ちに乾式反応させているが、この場
合も前述の先行技術と同様、高温雰囲気で反応の促進を
図っているものの、煙突に至るまでの煙道中に電気集塵
機などを設けており、何れも焼却炉の炉外において塩化
水素を分離除去するようになされていた。As a prior art for removing this hydrogen chloride, Japanese Patent Application Laid-open No. 54
-37378 publication, and JP-A-54-150865
Although it is disclosed in the Japanese Patent Application Publication No. 54-373 of the former
Publication No. 78 adopts a fluidized incinerator, introduces lime powder into the upper space of the furnace, causes a contact reaction with hydrogen chloride in the furnace, and causes the hydrogen chloride to adhere to the surface of the lime powder as calcium chloride.
The lime powder with calcium chloride attached is then removed outside the furnace using a dust collector such as an electrostatic precipitator or a multi-cyclone. Calcium compounds are supplied directly to the input point of the material supply hopper and immediately undergo a dry reaction with hydrogen chloride generated from the waste layer, but in this case as well, the reaction is accelerated in a high temperature atmosphere, similar to the prior art described above. However, electrostatic precipitators were installed in the flue leading to the chimney, and hydrogen chloride was separated and removed outside the incinerator.
(発明が解決しようとする問題点)
廃棄物の熱エネルギを乾留して回収する場合、従来の機
械式ストーカ−炉では、廃棄物の乾留によるガス化と発
生ガスの燃焼がほとんど同時に区別なく行われるため、
ガス化および燃焼がそれぞれ完全に行われず、排ガス中
に煤や未燃燐分が残存し好ましくない。従って廃棄物の
熱回収には乾留してガスを取得する工程と、該発生ガス
を別途に設けたバーナーで燃焼させる二段構への装置の
設置が推奨されている。(Problem to be Solved by the Invention) When recovering thermal energy from waste by carbonization, conventional mechanical stoker furnaces perform gasification by carbonization of waste and combustion of generated gas almost simultaneously and without distinction. In order to be exposed,
Gasification and combustion are not performed completely, and soot and unburned phosphorus remain in the exhaust gas, which is undesirable. Therefore, for heat recovery from waste, it is recommended to install a two-stage device in which the process involves carbonizing the waste to obtain gas, and then combusting the generated gas in a separately provided burner.
塩化ビニール、クロロブレンゴム等を含む可燃性廃棄物
を燃焼する際、例えば塩化ビニールは酸素存在下で燃焼
するとつぎのように反応して塩化水素を発生する。When burning combustible waste containing vinyl chloride, chloroprene rubber, etc., for example, when vinyl chloride is burned in the presence of oxygen, it reacts as follows to generate hydrogen chloride.
C!H2OHCl+丁02→HOJl’+2002+H
20このようにして発生した塩化水素の除去には、1)
水またはアルカリ液に吸収させる湿式法、2)アルカリ
液等と反応させ、かつ塩類を固体として回収する半乾式
法、3)アルカリ粉末と反応させ固体として回収する全
乾式法がある。これらのうち湿式法では水噴射によって
30〜40%、アルカリ液では低温で85〜95%除去
できるが、このためには燃焼炉と煙突との間に吸収塔な
どの湿式有害ガス除去装置、更には廃液処理設備などの
両帯施設を要し、建設費も嵩み、また廃熱回収装置に塩
化物や煤が耐着して伝熱効率を低下させ、かつ装置が腐
食するなどの問題があった。また半乾式法、全乾式法で
は燃焼炉より煙突に至るまでの煙道中に電気集塵機など
を設けて炉外部でガスの清浄化を行っており、この場合
も大規模な装置を必要とし問題があった。C! H2OHCl+D02→HOJl'+2002+H
20 To remove hydrogen chloride generated in this way, 1)
There are two methods: a wet method in which salts are absorbed in water or an alkaline solution, 2) a semi-dry method in which salts are reacted with an alkali solution and recovered as a solid, and 3) a completely dry method in which salts are reacted with an alkali powder and recovered as a solid. Of these, the wet method can remove 30 to 40% by water injection, and the alkaline solution can remove 85 to 95% at low temperatures. This requires dual facilities such as waste liquid treatment equipment, which increases construction costs, and there are also problems such as chlorides and soot adhering to the waste heat recovery equipment, reducing heat transfer efficiency and corroding the equipment. Ta. In addition, in the semi-dry method and fully dry method, gas is purified outside the furnace by installing an electrostatic precipitator in the flue from the combustion furnace to the chimney, but this also requires large-scale equipment and poses problems. there were.
(問題点を解決するための手段)
そこで本出願人は乾留炉あるいは焼却炉の上記問題点に
鑑み、これを解決するため、本発明は特に大規模な付帯
設備を設けることなく、簡単に塩化水素を塩化カルシウ
ムなどの塩化物として捕捉除去する方法および装置を提
供するためになされたものであり、その要旨とするとこ
ろは、可燃性葉物を燃焼して生成する塩化水素を含むガ
スにアルカリ剤を噴出してガス中に塩化物を生成させ、
該塩化物を同伴するガスは炉内で粒状残塊の灰層を通さ
せて塩化物を捕捉除去する方法と、上部にアルカリ剤噴
出口を備えた炉内に隔壁を設けて燃焼室とこれに連通ず
る反応室を形成し、炉下部に灰出し装置を設け、反応室
には粒状残塊の灰層を介してガス出口を開口するととも
に灰層ボックスに連絡した塩化水素除去廃棄物燃焼装置
である。(Means for Solving the Problems) Therefore, in view of the above-mentioned problems of carbonization furnaces or incinerators, in order to solve the problems, the present invention has been developed to easily chlorinate the This was developed to provide a method and device for capturing and removing hydrogen as chlorides such as calcium chloride. The agent is ejected to generate chloride in the gas,
The chloride-carrying gas is passed through the ash layer of granular residue in the furnace to capture and remove the chloride, and a partition wall is installed in the furnace with an alkali agent spout at the top to separate the combustion chamber and this. A reaction chamber is formed that communicates with the ash layer, and an ash extraction device is installed in the lower part of the furnace, and a gas outlet is opened in the reaction chamber through the ash layer of the granular residue, and a hydrogen chloride removal waste combustion device is connected to the ash layer box. It is.
(発明の作用)
本発明においては廃棄物の乾留あるいは燃焼に際し、発
生する塩化水素はアルカリ粉末、例えば消石灰と次式の
ように反応する。(Operation of the Invention) In the present invention, hydrogen chloride generated during carbonization or combustion of waste reacts with an alkali powder, such as slaked lime, as shown in the following equation.
2HOJ?+0a(OH)r”oaO12+2H20生
成した塩化カルシウムは炉内の粒状残塊の灰層を通過さ
せることによって捕捉し、灰分とともに排出させて、先
行技術の電気集塵機、マルチサイクロン等の付帯設備を
不要とするものである。2HOJ? +0a(OH)r”oaO12+2H20 The produced calcium chloride is captured by passing through the ash layer of the granular residue in the furnace and discharged together with the ash, eliminating the need for ancillary equipment such as electrostatic precipitators and multi-cyclones of the prior art. It is something to do.
即ち、燃焼炉上方にガス通路を有し、下方は粒状残塊灰
層の移送を許す隔壁によって、大容量の燃焼室と小容量
の反応室に区画し、消石灰などのアルカリ粉末を炉上部
から噴出して塩化水素と反応させ、生成落下する塩化カ
ルシウム等の塩化物を同伴したガスは、スクリューコン
ベアまたはプッシャー等の灰出し装置によって燃焼室か
ら移送され、細目の灰層支持用フィルター上に滞留した
粒状残塊の灰層を通過し、この残塊粒子間が有効濾過流
路となって粉状の塩化カルシウム等の塩化物はIP別捕
捉され、乾留の場合は浄化ガスのみ後段の燃焼炉(図示
せず)に導き、焼却の場合は大気へ放出するものであり
、隔壁は実施例で示すように燃焼室に面するため高温と
なって反応室を高温に維持し、反応は促進できる。粒状
残塊の灰層にて捕捉された塩化カルシウム等の塩化物は
灰分とともに灰出しボックスより排出される。In other words, there is a gas passage above the combustion furnace, and the lower part is divided into a large-capacity combustion chamber and a small-capacity reaction chamber by a partition wall that allows the transfer of the granular residual ash layer. Gas accompanied by chlorides such as calcium chloride that ejects and reacts with hydrogen chloride and falls is transferred from the combustion chamber by an ash removal device such as a screw conveyor or pusher, and is retained on a fine ash layer support filter. It passes through the ash layer of the granular residual agglomerates, and the space between the residual agglomerates becomes an effective filtration flow path, and chlorides such as powdered calcium chloride are captured by IP.In the case of carbonization, only the purified gas is passed through the combustion furnace in the latter stage. (not shown), and in the case of incineration, it is released into the atmosphere.As shown in the example, the partition wall faces the combustion chamber, so the temperature becomes high, maintaining the reaction chamber at a high temperature, and promoting the reaction. . Chlorides such as calcium chloride captured in the ash layer of the granular residue are discharged from the ash removal box together with the ash content.
(実施例)
図は可燃性廃棄物を乾留燃焼して乾留ガスを取得する場
合の本発明の一実施例を示す断面説明図であって、乾留
炉Iは例えば角形に形成し、垂直の隔壁2で大容量の乾
留室3と小容量の反応室4に区画し、画室は上方をガス
通路5で、下方は天道出通路6で連通しており、炉の上
部にはダンパー7を備えた廃棄物投入装置8が設けられ
、乾留室の下部は全面にロスドル9を敷き詰め、その下
方には燃焼用の空気分散パイプ10を適宜数配置し、そ
の上方に任意の間隔をおいてスクリューコンベヤまたは
プッシャー等の灰出し装置11が反応室側壁12に達す
るまで配置されている。(Embodiment) The figure is a cross-sectional explanatory diagram showing an embodiment of the present invention in which carbonization gas is obtained by carbonization combustion of combustible waste. 2 into a large-capacity carbonization chamber 3 and a small-capacity reaction chamber 4, and the chambers are communicated with a gas passage 5 at the top and a top outlet passage 6 at the bottom, and a damper 7 is provided at the top of the furnace. A waste input device 8 is provided, and the entire lower part of the carbonization chamber is covered with Rosdol 9. An appropriate number of air dispersion pipes 10 for combustion are placed below it, and a screw conveyor or An ash removal device 11 such as a pusher is arranged until it reaches the side wall 12 of the reaction chamber.
反応室上部には適宜複数個のアルカリ剤噴出口13を開
口し、下部には前記ロスドル9の間隔より狭い灰層支持
用フィルター14を敷き詰め、その下方はガス出口15
に連通ずるとともに、側壁12にはダンパー16を介し
て傾斜側壁17を有する灰出しボックス18を設け、該
ボックス1Bに設けたダンパー19は外気を遮断する。In the upper part of the reaction chamber, a plurality of alkali agent jet ports 13 are opened as appropriate, and in the lower part, an ash layer supporting filter 14, which is narrower than the spacing between the Rosdol 9, is spread, and below that, a gas outlet 15 is opened.
An ash removal box 18 having an inclined side wall 17 is provided on the side wall 12 via a damper 16, and a damper 19 provided on the box 1B blocks outside air.
アルカリ剤噴出口は目詰り対策を施せば乾留室に設けて
もよい。The alkaline agent spout may be provided in the carbonization chamber if measures are taken to prevent clogging.
上記の構成を有する乾留炉1において、投入された塩化
ビニール、クロロプレンゴム等の塩化物を含有する廃棄
物20が炉内に堆積し、着火後、空気分散パイプ10よ
り供給されロスドル9を通過した空気により約500〜
600℃で乾留され、廃棄物は熱分解によって塩化水素
を発生し、これを含む乾留ガスはガス通路5を経て反応
室4に入り、例えば消石灰粉末がアルカリ剤噴出口13
より噴出し、塩化水素と反応して塩化カルシウムを生成
し、ガスに同伴されて下降する。In the carbonization furnace 1 having the above configuration, the input waste 20 containing chlorides such as vinyl chloride and chloroprene rubber was deposited in the furnace, and after being ignited, it was supplied from the air distribution pipe 10 and passed through the Rosdol 9. Approximately 500~ depending on the air
The waste is carbonized at 600°C, and hydrogen chloride is generated by thermal decomposition, and the carbonized gas containing this enters the reaction chamber 4 through the gas passage 5. For example, slaked lime powder is passed through the alkali agent spout 13.
It ejects from the water, reacts with hydrogen chloride to produce calcium chloride, and descends along with the gas.
一方、乾留後の粒状残塊の灰層21はスクリューコンベ
ヤー11で反応室側へ移送され、ここで反応室4を下降
する乾留ガスは粒状残塊の灰層21’およびこれを支持
する細目の灰層支持用フィルター14を通過し、出口1
5より後続の燃焼室(図示せず)へ送出されるが、乾留
ガスが同伴した塩化カルシウムおよび煤等は粒状残塊の
灰層21′を通過する際にが別され、これらを捕捉した
粒状残塊の灰層は灰出しボックス18に落下し、ダンパ
ー16を開いて外部に排出される。細目の灰層支持用フ
ィルタ14の存在は常時灰層の確保に効果があり、塩化
物同伴ガスが煙道に素通りすることはない。On the other hand, the ash layer 21 of the granular residual mass after carbonization is transferred to the reaction chamber side by the screw conveyor 11, and here the carbonization gas descending through the reaction chamber 4 is transferred to the ash layer 21' of the granular residual mass and the fine particles supporting this. Passes through the ash layer support filter 14 and exits at the outlet 1
5 to the subsequent combustion chamber (not shown), but the calcium chloride and soot entrained by the carbonized gas are separated as they pass through the ash layer 21' of the granular residue, and the captured granules The remaining ash layer falls into the ash removal box 18, and is discharged to the outside by opening the damper 16. The presence of the fine ash layer supporting filter 14 is effective in ensuring an ash layer at all times, and chloride-entrained gas does not pass through the flue.
上記ではアルカリ剤は消石灰で説明したが、生石灰、水
酸化マグネシウム、ソーダ灰等も使用できることは勿論
である。なお灰出し作業は炉内の塵芥物が減少してから
行い、その灰層の移送によって反応室内の灰層が高くな
り過ぎ、ガスの通過抵抗が大となれば、ダンパー16を
開いて灰出しボックス18へ落下させ、灰層が減少すれ
ばダンパー16は閉じて灰層を適宜の高さまで化成させ
、このように灰出し作業は調節できる。In the above explanation, slaked lime was used as the alkaline agent, but it goes without saying that quicklime, magnesium hydroxide, soda ash, etc. can also be used. The ash removal work should be carried out after the amount of dust in the furnace has decreased. If the ash layer in the reaction chamber becomes too high due to the transfer of the ash layer and the gas passage resistance becomes large, open the damper 16 and remove the ash. The ash is dropped into the box 18, and when the ash layer decreases, the damper 16 closes to convert the ash layer to an appropriate height, and the ash removal operation can be adjusted in this way.
(効果)
本発明は塩化水素を含む高温の燃焼ガスにアルカリ剤を
噴出してガス中に塩化カルシウム等の塩化物を生成させ
、該塩化物を同伴する燃焼ガスは炉内における粒状残塊
の灰層を通して該塩化物を捕捉除去する塩化水素除去廃
棄物燃焼方法、及び炉を隔壁で区画して反応室を形成し
た装置であるから、反応室は高温燃焼室の隔壁を一側面
とするため、高温に維持されるとともに、従来のアルカ
リ剤を噴出した焼却炉から直ちにガスを取出す場合に比
べてこの反応室の存在によってガス流路は延長されてガ
ス滞留時間は長く保たれ、反応時間も長くなって塩化水
素除去反応は一層促進される効果がある。(Effects) The present invention injects an alkali agent into high-temperature combustion gas containing hydrogen chloride to generate chlorides such as calcium chloride in the gas, and the combustion gas accompanied by the chlorides is used to remove granular residual agglomerates in the furnace. This is a hydrogen chloride removal waste combustion method that captures and removes the chlorides through an ash layer, and an apparatus in which a reaction chamber is formed by dividing the furnace with a partition wall, so the reaction chamber has one side that is the partition wall of the high-temperature combustion chamber. In addition to being maintained at a high temperature, the existence of this reaction chamber lengthens the gas flow path and keeps the gas residence time longer than in the case of taking gas immediately from a conventional incinerator that spews out an alkaline agent. The longer the reaction time, the more the hydrogen chloride removal reaction is promoted.
またアルカリ剤噴出口を反応室上方に設ければ、アルカ
リ剤の噴出はガス流と並流となるから噴出抵抗は減じ噴
出圧も低くでき、目詰まりも防止でき、また図示のよう
に灰出し装置、空気分散パイプ等は灰層に埋設させれば
火炎に直接炎らず長期間の使用に耐える。In addition, if the alkali agent spout is installed above the reaction chamber, the alkali agent will be ejected in parallel with the gas flow, reducing the ejection resistance and lowering the ejection pressure, preventing clogging. If equipment, air dispersion pipes, etc. are buried in the ash layer, they will not be directly exposed to flames and can withstand long-term use.
更には燃焼ガスは粒状残塊の灰層を通過するから、同伴
した塩化カルシウム等の塩化物および煤などがこの粒状
残塊灰層によって消削捕捉され、従来のように電気集塵
機のごとき大規模な集塵装置は不要となり、また燃焼ガ
スは塩化水素を含まないので後段に熱回収廃熱ボイラ等
を設けても塩化水素による腐食は防止でき、また従来の
湿式の場合のように吸収液の後処理設備なども不用とな
るので、装置も簡単になって設備費が安価になると共に
メンテナンスも容易となりその効果は多大である。Furthermore, since the combustion gas passes through the ash layer of the granular residue, the entrained chlorides such as calcium chloride and soot are eliminated and captured by the granular residue ash layer, making it possible to use large-scale equipment such as conventional electrostatic precipitators. Furthermore, since the combustion gas does not contain hydrogen chloride, corrosion due to hydrogen chloride can be prevented even if a heat recovery waste heat boiler is installed in the latter stage. Since post-processing equipment and the like are not required, the equipment becomes simpler, the equipment cost becomes cheaper, and maintenance becomes easier, which has great effects.
図は本発明の一実施例における断面説明図であって、第
1図は縦断面説明図、第2図は部分的に切欠いて内部構
造を示した平面図である。
】・・・乾留炉、 2・・・隔壁、3・・・乾
留室、 4・・・反応室、5・・・ガス通路、
6・・・天道出通路、8・・・廃棄物投入装置、9
・・・ロスドル、10・・・空気分散パイプ、11・・
・灰出し装置、13・・・アルカリ剤噴出口、
14・・・灰出支持用フィルタ、
15・・・ガス出口、 18・・・灰出しボックス
、20・・・廃棄物、
21.21′・・・粒状残塊の灰層。The drawings are explanatory cross-sectional views of one embodiment of the present invention, in which FIG. 1 is an explanatory longitudinal cross-sectional view, and FIG. 2 is a partially cutaway plan view showing the internal structure. ]... Carbonization furnace, 2... Partition wall, 3... Carbonization chamber, 4... Reaction chamber, 5... Gas passage,
6...Tendo outlet passage, 8...Waste input device, 9
...Rosdol, 10...Air distribution pipe, 11...
- Ash extraction device, 13... Alkaline agent spout, 14... Ash extraction support filter, 15... Gas outlet, 18... Ash extraction box, 20... Waste, 21.21' ...Ash layer of granular residual mass.
Claims (2)
ガスにアルカリ剤を噴出してガス中に塩化物を生成させ
、該塩化物を同伴するガスは炉内で粒状残塊の灰層を通
して塩化物を捕捉除去する塩化水素除去廃棄物燃焼方法
。(1) An alkali agent is injected into the gas containing hydrogen chloride generated by burning combustible waste to generate chloride in the gas, and the gas accompanied by the chloride is removed from the ash of granular residue in the furnace. Hydrogen chloride removal waste combustion method that captures and removes chloride through a layer.
けて燃焼室とこれに連通する反応室を形成し、炉下部に
灰出し装置を設け、反応室には粒状残塊の灰層を介して
ガス出口を開口するとともに灰出ボックスに連絡した塩
化水素除去廃棄物燃焼装置。(2) A partition wall is provided in the furnace equipped with an alkaline agent spout at the top to form a combustion chamber and a reaction chamber communicating with the combustion chamber.An ash removal device is installed at the bottom of the furnace, and the reaction chamber is filled with ash of granular residue. A hydrogen chloride removal waste combustion device with a gas outlet opening through the bed and communicating with the ash removal box.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP4043385A JPS61197910A (en) | 1985-02-28 | 1985-02-28 | Waste material combustion method removing hydrogen chloride and its device |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP4043385A JPS61197910A (en) | 1985-02-28 | 1985-02-28 | Waste material combustion method removing hydrogen chloride and its device |
Publications (2)
Publication Number | Publication Date |
---|---|
JPS61197910A true JPS61197910A (en) | 1986-09-02 |
JPH0468532B2 JPH0468532B2 (en) | 1992-11-02 |
Family
ID=12580504
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP4043385A Granted JPS61197910A (en) | 1985-02-28 | 1985-02-28 | Waste material combustion method removing hydrogen chloride and its device |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS61197910A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH01163511A (en) * | 1987-05-22 | 1989-06-27 | Evs Energ Versorgungssyst Gmbh | Method and device for coupling salt-forming element with solid substance when fossil fuel, dust, etc. are burnt |
Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5433273A (en) * | 1977-08-19 | 1979-03-10 | Mitsubishi Heavy Ind Ltd | Treating method for exhaust gas |
-
1985
- 1985-02-28 JP JP4043385A patent/JPS61197910A/en active Granted
Patent Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5433273A (en) * | 1977-08-19 | 1979-03-10 | Mitsubishi Heavy Ind Ltd | Treating method for exhaust gas |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH01163511A (en) * | 1987-05-22 | 1989-06-27 | Evs Energ Versorgungssyst Gmbh | Method and device for coupling salt-forming element with solid substance when fossil fuel, dust, etc. are burnt |
Also Published As
Publication number | Publication date |
---|---|
JPH0468532B2 (en) | 1992-11-02 |
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