JPS5855409B2 - Dry ash extraction device for municipal waste incineration equipment - Google Patents
Dry ash extraction device for municipal waste incineration equipmentInfo
- Publication number
- JPS5855409B2 JPS5855409B2 JP10820676A JP10820676A JPS5855409B2 JP S5855409 B2 JPS5855409 B2 JP S5855409B2 JP 10820676 A JP10820676 A JP 10820676A JP 10820676 A JP10820676 A JP 10820676A JP S5855409 B2 JPS5855409 B2 JP S5855409B2
- Authority
- JP
- Japan
- Prior art keywords
- ash
- incinerator
- municipal waste
- air
- blower
- 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
Links
Landscapes
- Refuse Collection And Transfer (AREA)
- Auxiliary Methods And Devices For Loading And Unloading (AREA)
- Gasification And Melting Of Waste (AREA)
- Incineration Of Waste (AREA)
Description
【発明の詳細な説明】
本発明は都市ごみ焼却設備の燃焼残渣を乾式により引出
し、外気との気密をシール機構を用いずに、炉内と外気
との差圧をなくすることによって遠戚させ、その目的に
用いた排気を利用することを特徴づけた都市ごみ焼却設
備の乾式灰引出し装置に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention extracts combustion residue from municipal waste incineration equipment using a dry method, and achieves airtightness with the outside air by eliminating the differential pressure between the inside of the furnace and the outside air without using a sealing mechanism. , relates to a dry ash extraction device for a municipal waste incineration facility, characterized in that the exhaust gas used for that purpose is utilized.
都市ごみ焼却設備の燃焼残渣は水を張った移送機(フラ
イトコンベア)による湿式引出し方式が殆んどである。In most cases, combustion residue from municipal waste incineration facilities is extracted using a wet method using a flight conveyor filled with water.
その理由は■焼却炉内と外気との気密が水封というもつ
とも簡単な方法でしかも完全に行なうことができる。The reason for this is: - The inside of the incinerator can be completely airtight with the outside air using water sealing, which is a very simple method.
■燃焼残渣の保有潜熱を水封水により冷却することがで
きる。■The latent heat of combustion residue can be cooled by water sealing.
■、■〜■と引出し灰の移送が同一フライトコンベア内
で同時に遠戚されるため設備費が安価であり、性能も安
定している。Since the transport of the drawn ash from ■, ■ to ■, is carried out at the same time within the same flight conveyor, the equipment cost is low and the performance is stable.
以上の通り、効果も優れ、価格も他の如何なる方法より
安く、都市ごみ燃焼残渣の引出し方式はこの湿式水封法
より優る方法はない。As mentioned above, there is no method superior to this wet water-sealing method for removing municipal waste combustion residue, as it has excellent effects and is cheaper than any other method.
しかし最近水を用いることによる幣害が生じてきた。However, recently, water damage has been occurring due to the use of water.
すなわち、(1)フライトコンベアから燃焼残渣と共に
持去られる浸出水は残渣貯蔵ピットから廃水処理設備に
送られ処理後放流されるが、残渣中に含まれる重金属類
を除去しなければならないため廃水処理設備が複雑かつ
高価になる。In other words, (1) The leachate taken away from the flight conveyor together with the combustion residue is sent from the residue storage pit to the wastewater treatment facility and discharged after treatment.However, the heavy metals contained in the residue must be removed, so wastewater treatment is required. Equipment becomes complex and expensive.
よしんば処理しても除去した沈殿汚泥はそのままの形で
投棄できず、何等かの安定化処置を講じなけれはならず
、その際、汚泥が高含水率であり、乾燥、焼結その他の
2次処理を行なうのに余分のエネルギを浪費しなければ
ならない。Even after Yoshiba treatment, the removed settled sludge cannot be dumped as is, and some kind of stabilization measures must be taken. Extra energy must be wasted to perform the processing.
(2)フライトコンベアの水封水は燃焼残渣の潜熱によ
り次第に温度が上昇し、湯気を発生する。(2) The temperature of the water seal on the flight conveyor gradually rises due to the latent heat of the combustion residue, generating steam.
この湯気には特有の臭気と金属を腐食させる若干の亜硫
酸ガスおよび水蒸気があって付近の機器を腐食させるの
で、湯気が立たない温度まで下げる補給水を大量に必要
とし、この補給水量が灰の持去る吸収水量を大きく上廻
るため廃水処理設備の容量を増大させる。This steam has a characteristic odor and contains some sulfur dioxide gas and water vapor that corrode metals, which can corrode nearby equipment, so a large amount of make-up water is required to lower the temperature to a point where steam does not form. The capacity of wastewater treatment equipment will be increased to greatly exceed the amount of water absorbed.
(3)気密と燃焼残渣の急冷だけを目的とした所謂半湿
式タイプの灰引出し装置も外国の例には多いが、このタ
イプは燃焼残渣の温度が完全に冷却される時間を与えず
引出されるので、(2)と同様湯気と臭気および腐食の
好ましくない幣害を伴なう。(3) There are many examples of so-called semi-humid type ash extraction equipment in other countries, which are intended only for airtightness and rapid cooling of combustion residue, but this type does not allow time for the combustion residue to cool down completely. Therefore, like (2), it is accompanied by undesirable damage such as steam, odor, and corrosion.
これらの不都合事項が惹起するに及んで、従来余り採用
されていない乾式の灰引出し方式が要求されるようにな
った。As these inconveniences have arisen, a dry ash extraction system, which has not been widely used in the past, has become necessary.
湿式は炉とフライトコンベアとの接点である灰出しシュ
ートをコンベアの水封水につけるだけで炉の気密を保つ
ことができるのに対し、乾式は一10m/m水柱前後の
負圧をシールする機構が必要となり、構造上の困難さと
共に湿式より高価になることは避けられない。In the wet type, the furnace can be kept airtight simply by submerging the ash removal chute, which is the contact point between the furnace and the flight conveyor, in water sealing water on the conveyor, whereas in the dry type, the negative pressure of around 10 m/m of water is sealed. This requires a mechanism, which is difficult to construct and is inevitably more expensive than the wet method.
しかし、湿式は上記(1)、(2)の理由から廃水処理
設備に莫大な設備費と維持費とを必要とし、総括的にメ
リット、デメリットを比較した場合、乾式の持つ特徴を
生かす道が展けて来た。However, due to reasons (1) and (2) above, the wet method requires huge equipment costs and maintenance costs for wastewater treatment equipment, and when comparing the overall advantages and disadvantages, there is no way to take advantage of the characteristics of the dry method. It has opened.
ごみ焼却施設より公害を出さないための落し予約な性格
のものである。This facility is designed to be an afterthought in order to produce less pollution than a garbage incineration facility.
乾式灰引出し装置が用いられなかった陰の理由として気
密構造の困難さがあげられる。The reason why dry ash extraction equipment was not used was that it was difficult to create an airtight structure.
単なる外気との遮断だけならば問題はないが、燃焼残渣
は有機物が燃焼した残りの灰分にとどまらず、燃えのこ
りの未燃物や始めから混入する土砂、がれき、ガラス、
陶磁器、金属類等バラエティに富んだ無機物、特に缶詰
、石油缶等の嵩ものや番線、コード、ワイヤ、洋傘骨等
の長ものの存在が気密構造設計上の障害となっている。There is no problem if it is simply isolated from the outside air, but combustion residue is not only the ash left after burning organic matter, but also the unburned remains of the embers, dirt, debris, glass, etc. that are mixed in from the beginning.
The presence of a wide variety of inorganic materials such as ceramics and metals, especially bulky items such as canned goods and oil cans, and long items such as cords, cords, wires, and umbrella ribs, pose obstacles to the design of airtight structures.
そのため回転や摺動を必要とする複雑な機構は故障をま
ねく結果になって適当とは言えず、単純な機構例えば2
段ダンパの如き構造しか使用できない。For this reason, complex mechanisms that require rotation or sliding are not appropriate as they may lead to failures, and simple mechanisms such as 2
Only structures such as stage dampers can be used.
構造が簡単であれば、気密の程度は劣り、気密を保持さ
れると間欠的な使用方法となってクリンカ発生その細別
の幣害を生む結果となり兼ねない。If the structure is simple, the degree of airtightness is poor, and if airtightness is maintained, intermittent use may result in clinker generation and other damage.
それ故、機械的機構で満足すべき構造を設計することは
難事である。Therefore, it is difficult to design a satisfactory structure with a mechanical mechanism.
従来の都市ごみ焼却設備の沢山装置は図1−A及び図1
−Bに示すように、燃焼残渣は灰出しシュート5を経て
フライトコンベア6で冷却し移送される。Many conventional municipal waste incineration facilities are shown in Figure 1-A and Figure 1.
As shown in -B, the combustion residue is cooled and transferred by the flight conveyor 6 through the ash removal chute 5.
灰出しシュートは図1−Bのようにフライトコンベア6
の水槽38に水封されて外気との気密が保たれている。The ash removal chute is connected to the flight conveyor 6 as shown in Figure 1-B.
The water tank 38 is sealed with water to maintain airtightness from the outside air.
フライトコンベアには燃焼ストーカ3(乾燥ヌトーカを
含む)および3′(後燃焼ストーカを含む)のロスドル
よりこほれ落ちた灰および未燃焼物を空気箱兼落じんホ
ッパ4゜4′テ受は落しんシュー)40.40’を通り
接続させ、灰出しシュート同様水封されている。On the flight conveyor, there is an air box and dust hopper 4゜4' for dropping the ash and unburned materials that have fallen from the combustion stoker 3 (including dried nutoka) and 3' (including the post-combustion stoker). It is connected through the shoe) 40.40' and is sealed with water like the ash removal chute.
フライトコンベア6より移送された燃焼残渣および落じ
んは、この様に水の中に完全浸漬されているので、過飽
和に水を含み灰貯蔵ピット7に落され貯蔵すると余剰汚
水が灰貯蔵ピットに相当量たまるので、図1−Aの様に
集水ピット7aを設けてあり、ここから灰ピツト汚水を
ポンプアップし廃水処理設備7bに送られ処理される。The combustion residue and dust transferred from the flight conveyor 6 are completely immersed in water in this way, so when they are supersaturated with water and are dropped into the ash storage pit 7 and stored, the excess wastewater is stored in the ash storage pit. Since the wastewater accumulates in a large amount, a water collection pit 7a is provided as shown in FIG. 1-A, from which the wastewater from the ash pit is pumped up and sent to a wastewater treatment facility 7b for treatment.
しかしこの灰ピツト汚水は廃水処理設備7bで処理され
る全体のプラント汚水からすれば量的に少ないが、燃焼
残渣中の有機物未燃分によるBOD性分高く、また、灰
処理汚水になるが故にSS値も高い。However, although this ash pit sewage is small in quantity compared to the entire plant sewage treated in the wastewater treatment facility 7b, it has a high BOD content due to unburned organic matter in the combustion residue, and because it becomes ash treatment sewage. SS value is also high.
それよりもましているいろな重金属類が溶出して含有さ
れている場合が多く、廃水処理設備の装置を大きくした
り複雑化する欠点がある。In many cases, various heavy metals are eluted and contained, which has the disadvantage of making wastewater treatment equipment larger and more complex.
この欠点をなくするには、灰ピツト汚水、ひいてはフラ
イトコンベアからの持去水を無くすることが必要であり
、そのためには乾式で灰処理を行なうことが条件になる
。In order to eliminate this drawback, it is necessary to eliminate wastewater from the ash pit and, by extension, water removed from the flight conveyor, and to this end, it is necessary to perform ash treatment in a dry manner.
乾式にすると焼却炉との気密を保たせる機構の設計は容
易でない。If it is a dry type, it is not easy to design a mechanism to maintain airtightness with the incinerator.
本発明は困難な機械的機構を設けることなく、気密を保
つようにしたものであり、その上気密手段として用いら
れる流体(空気と燃焼ガスとの混合物)を他の目的のた
めに活用する複合効果を兼ねさせるために開発されたも
のである。The present invention maintains airtightness without providing a difficult mechanical mechanism, and furthermore, it is a composite system that utilizes the fluid (mixture of air and combustion gas) used as the airtightness means for other purposes. It was developed to have both effects.
以下図面により詳細説明する。A detailed explanation will be given below with reference to the drawings.
図2に於て、図示していないごみ供給クレーンにより供
給されたごみはホッパおよびシュート1を通り供給フィ
ーダ2で定量が乾燥および燃焼ストーカ3に供給され燃
焼し、燃焼および後燃焼ストーカ3′で完全に灰化し、
灰出シュート5からフライトコンベア6に落ちる。In Fig. 2, garbage supplied by a garbage supply crane (not shown) passes through a hopper and a chute 1, and a fixed amount is supplied to a drying and combustion stoker 3 by a supply feeder 2, where it is combusted, and then a combustion and post-combustion stoker 3'. completely ashed,
It falls from the Ashide chute 5 onto the flight conveyor 6.
燃焼ガスはガス冷却ボイラの放射ゾーン11および11
′、接触ゾーン11“で冷却されガスダクト43を経て
電気集じん装置13で除じんし、ガスダクト14、吸出
送風機15を通り、図に示していない煙突に排ガスを放
出する通常の焼却設備形式である。The combustion gases are in the radiant zones 11 and 11 of the gas-cooled boiler.
It is a normal incineration facility type in which the exhaust gas is cooled in the contact zone 11'', passes through a gas duct 43, is removed by an electrostatic precipitator 13, passes through a gas duct 14 and a suction blower 15, and is released into a chimney not shown in the figure. .
この焼却炉形体において本発明は灰出しシュート5に普
通この部分でのマイナス10m/m水柱程度の炉内圧と
外気との気密を保たせる機械的構造を設けず、しかもフ
ライトコンベア6は水封することなく燃焼残渣は湿らさ
ずに落される。In this incinerator configuration, the present invention does not provide the ash removal chute 5 with a mechanical structure that normally maintains airtightness between the furnace internal pressure of about -10 m/m water column in this part and the outside air, and the flight conveyor 6 is water-sealed. Combustion residue is removed without getting wet.
このまま燃焼残渣がフライトコンベアにより移送され、
灰貯蔵ピット7に落下すれば、前述の気密機構がないの
で炉内と外気との気密が保たれず、大量の冷空気が焼却
炉に進入して燃焼継続は出来なくなると共に灰貯蔵ピッ
ト7は粉じんが立ち込め、作業環境ははなはだ不都合な
結果になることは目に見えている。The combustion residue is transferred as it is by a flight conveyor,
If it falls into the ash storage pit 7, the airtightness between the inside of the furnace and the outside air will not be maintained as there is no airtight mechanism as described above, and a large amount of cold air will enter the incinerator, making it impossible to continue combustion and the ash storage pit 7 It is clear that the dust buildup will result in a very inconvenient working environment.
そこで本発明の詳細な説明する上に図3を用意した。Therefore, FIG. 3 was prepared for detailed explanation of the present invention.
図3−Aはフライトコンベア6の隔室を部分的に示した
ものである。FIG. 3-A partially shows a compartment of the flight conveyor 6.
すなわち燃焼残渣は灰出しシュート5からフライトコン
ベア6の最初の隔室に入る。That is, the combustion residue enters the first compartment of the flight conveyor 6 from the ash removal chute 5.
隔室を構成する境界は耐熱可撓性材料よりなるカーテン
17が上蓋39より吊下げられることにより区分けされ
ている。The boundaries of the compartments are separated by a curtain 17 made of a heat-resistant flexible material suspended from an upper lid 39.
このカーテン17は図3−Bの断面図の斜線で示した部
分であってカーテン17のすそはコンベア槽38の底部
にとどく長さを持っている。This curtain 17 is the part shown by diagonal lines in the sectional view of FIG. 3-B, and the hem of the curtain 17 has a length that reaches the bottom of the conveyor tank 38.
コンベアには残渣を掻き寄せ移送するフライト35が駆
動チェーン36によす移動しているので完全に気密とス
ルことは出来ないが、炉内の負圧により進入しようとす
る外気に通気抵抗を与えられればそれでよい。The conveyor has a flight 35 that scrapes up and transfers the residue moving along the drive chain 36, so it cannot be completely airtight, but the negative pressure inside the furnace creates ventilation resistance for outside air that tries to enter. If you can, that's fine.
このようなカーテンがいくつかたれ下り、必要数の隔室
を構成させている。Several such curtains hang down to form the required number of compartments.
第2室は(図3−A)本発明のもつとも特長のある部分
であるこの第2室上蓋には逆錐状の吸気室18および内
気を吸弓する吸気ブロワ20(図2)に連結された吸引
ダクト19が設けてあり、炉内圧と第2室とが同圧にな
るようダンパ42により自動コントロール41されてい
る。The second chamber (FIG. 3-A) is the most distinctive part of the present invention. The upper lid of the second chamber is connected to an inverted conical intake chamber 18 and an intake blower 20 (FIG. 2) that sucks inside air. A suction duct 19 is provided, and automatic control 41 is performed by a damper 42 so that the pressure inside the furnace and the second chamber become the same pressure.
それ故第2室の内圧は炉内圧子カーテン17の通気抵抗
外の負圧になっている。Therefore, the internal pressure of the second chamber is a negative pressure outside the ventilation resistance of the indenter curtain 17 in the furnace.
外気は正圧であり最終室→・・・・・・→第4室→第3
室とカーテン抵抗外だけ次第に負圧になり、第3室では
ほぼ第1室と同圧あるいは若干高目の内圧となる。The outside air has positive pressure, and the final chamber→・・・・・・→4th chamber→3rd chamber
The pressure in the chamber and outside the curtain resistance gradually becomes negative, and the internal pressure in the third chamber becomes approximately the same as that in the first chamber or slightly higher.
それ故第2室で吸引される吸気は大部分の外気に若干第
1室を経過する炉内の燃焼ガスの混合気体である。Therefore, the intake air sucked into the second chamber is a mixture of mostly outside air and some combustion gas inside the furnace passing through the first chamber.
第2室には空気吹出しノズル28が設けである。The second chamber is provided with an air blowing nozzle 28.
ここには図2に示したコンプレッサ29により少量で圧
力の強い空気が導管30を経て吹出され、移送中の燃焼
残渣に直接吹付けられる。Here, a compressor 29 shown in FIG. 2 blows a small amount of high-pressure air through a conduit 30 and directly onto the combustion residue being transferred.
そして燃焼残渣中の軽い灰分を舞上らせこの粉じんをも
吸気ブロワ20で吸引させ、サイクロンセパレーク21
で捕集せしめる。Then, the light ash in the combustion residue is stirred up and this dust is also sucked by the intake blower 20, and the cyclone separator 21
I will have it collected.
この目的は灰貯蔵ピットでの粉じんトラブルを防ぐため
でもあるが、外気がフライトコンベア内のカーテンのす
き間を通過する時にかなりの風速になり、フライトコン
ベア内での粉じんは防ぎ切れない。The purpose of this is to prevent dust problems in the ash storage pit, but when the outside air passes through the gaps in the curtains inside the flight conveyor, the wind speed becomes quite high, making it impossible to prevent dust inside the flight conveyor.
これを防ぐよりも強制的に粉じんを立てて別に取除くこ
との方が確実であり取除いた軽い灰を別処理するか、中
和剤として利用することができれば一石二鳥の方法であ
る。Rather than preventing this, it is more reliable to forcibly raise dust and remove it separately, and if the removed light ash can be disposed of separately or used as a neutralizing agent, it is a way to kill two birds with one stone.
図3−A−に戻って、第3室、第4室に噴射ノズル39
の設けであるのは灰貯蔵ピットでの粉じん防止のために
仕上げの目的から冷却水をヌプレするものであるが、移
送中の残渣に直接スプレして湿灰とするような使用方法
をするのではなく雰囲気温度を下げ残渣を冷却する、す
でに知られているクエンチングクーラの使用方法を行な
うものである。Returning to FIG. 3-A-, the injection nozzle 39 is installed in the third and fourth chambers.
The reason for this is to spray cooling water into the ash storage pit for finishing purposes to prevent dust. Instead, it uses a known method of using a quenching cooler, which lowers the ambient temperature and cools the residue.
図3−Bはフライトコンベアのa−a′線に沿う断面図
であり、図3Cはフライトコンベア形式の移送機ではな
く、エプロンコンベア37やパケットコンベア形式の移
送機であっても本発明に適用できることを示している。FIG. 3-B is a cross-sectional view of the flight conveyor taken along line a-a', and FIG. 3C is a sectional view of the flight conveyor, and the present invention is applicable to an apron conveyor 37 or a packet conveyor-type transfer device, rather than a flight conveyor-type transfer device. It shows what can be done.
図2に於て各ストーカ3,3′から下部の空気箱兼落じ
んホッパ4,4′に落ちた灰と未燃物はシュートを通り
通常は図1−Aの如くフライトコンベアに導ひかれるこ
とは前述の通りであるが、この未燃物をもう一度炉内に
戻し焼却残渣全体の熱灼減量を少なくする。In Figure 2, the ash and unburnt materials that fall from each stoker 3, 3' into the lower air box/dust hopper 4, 4' pass through a chute and are normally led to a flight conveyor as shown in Figure 1-A. As mentioned above, this unburned material is returned to the furnace once again to reduce the amount of heat loss of the entire incineration residue.
通称リドリング還元方式を空気輸送を用いることは一般
に石炭焚ボイラなどに用いられる方法であるが、本発明
ではフライトコンベア内の粉じんを捕集し終えた排気を
用いて空気輸送させるところに特徴を持っている。Using pneumatic transport, commonly known as the riddling reduction method, is a method generally used in coal-fired boilers, etc., but the present invention is characterized by using air transport after collecting dust in the flight conveyor. ing.
すなわち、捕集用サイクロン21からの排気は導管22
で排気されるが、この導管に灰および未燃物(リドリン
グ)はシュート9.9’が接続される。That is, the exhaust from the collection cyclone 21 is carried out through the conduit 22.
A chute 9.9' is connected to this conduit for ash and unburnt material (ridling).
このシュートには気密と定量供給の目的を持つロータリ
バルブ10,10′または図にないフラップダンパなど
が設けられる。This chute is provided with rotary valves 10, 10' or a flap damper (not shown) for the purpose of airtightness and quantitative supply.
導管22内のりドリングはりドリング吸引ブロワ25に
より搬ばれるが、この導管の途中にサイクロンセパレー
タ23、およびバグフイタ24が設けられて捕集され、
直接にまたは図示の様なケースコンベア27やフローコ
ンベアなどの輸送機を用いて導管44から焼起炉に戻し
完全燃焼させる。The liquid in the conduit 22 is carried by the suction blower 25, but a cyclone separator 23 and a bag filter 24 are installed in the middle of the conduit to collect it.
It is returned to the incinerator through the conduit 44 for complete combustion, either directly or using a transport device such as the case conveyor 27 or flow conveyor as shown.
リドリング吸引プロワ25からの排気は電気集じん装置
13の入口に接続し、微細な粉じんまで捕集させる。The exhaust gas from the ridling suction blower 25 is connected to the inlet of the electrostatic precipitator 13 to collect even the finest dust.
この様に構成された本発明によれば都市ごみ焼却炉燃焼
残渣を乾式で処理することにより、従来の湿式処理法に
比べ、湿式による余剰汚水の分だけ廃水処理装置が簡単
化すると同時に、灰貯蔵ピットから水分を過分に含んだ
残渣を運搬トラックに荷積みし、街路上に汚水を点滴せ
しめる公害を無くすることが可能である。According to the present invention configured in this way, by dry processing the combustion residue of municipal waste incinerators, compared to the conventional wet processing method, the wastewater treatment equipment is simplified by the amount of excess sewage produced by the wet method, and at the same time, the ash It is possible to load overly moist residue from storage pits onto transport trucks, eliminating the pollution caused by dripping sewage onto the streets.
そしてこの装置を適用したシステム中で乾燥灰分を捕集
し、説明を加えなかったが重金属を多く含んだ電気集じ
ん装置捕集灰と共に別処理すれば全体のpHを上げるこ
とが可能であり、処理上好都合である。Then, if the dried ash is collected in a system using this device and treated separately with the ash collected by the electrostatic precipitator, which contains a lot of heavy metals, although I did not explain this, it is possible to raise the overall pH. It is convenient for processing.
また、灰分の利用を計る省資源形公害防止設備をも計画
に組入れることが可能になる。It will also be possible to incorporate resource-saving pollution prevention equipment into the plan to utilize ash.
そして同一装置を用いて焼却炉設備としての性能の向上
につながるリドリング還元装置をも併用することができ
て公害防止上、コスト低減上、性能向上上、その複次的
に拡がる効用は計り知れないものがある。Furthermore, the same equipment can also be used with a ridgling reduction device that improves the performance of the incinerator equipment, and its multi-dimensional benefits are immeasurable in terms of pollution prevention, cost reduction, and performance improvement. There is something.
図1−Aは従来の都市ごみ焼却設備の灰処理装置を示す
説明図、図1−Bは図1−Aのa −a線に沿うフライ
トコンベアの断面図、図2は本発明の都市ごみ焼却設備
灰引出し装置を有する全体系統図、図3−Aは要部拡大
説明図、図3−Bは図3Aのa’−a’線に沿う断面図
、図3−Cは図3Aのb−b線に沿う断面図である。
図面内構成機器の名称、1:ごみホッパおよびシュート
、2;供給フィーダ、3ニストーカ、4:空気箱兼落じ
んホッパ、5:灰出しシュート、6:フライトコンベア
、7:燃焼残渣貯蔵ピット、8:灰出しクレーン、9:
リドリングシュー、10:ロータリバルブ、11:放射
、および接触ソーンボイラ、12:ボイラドラム、13
:電気集じん装置、14,43:ガスダト、15:吸出
し送風機、16 : E/P灰移送コンベア、17:カ
ーテン、18:吸気室、19:吸引ダクト、20;吸気
ブロワ、21,23:サイクロンセパレータ、22 、
30 、32 、44 :導管、24:バグフィルタ、
25:リドリング吸引ブロワ、26:排気ダクト、27
:ケーヌコンベア、28:空気吹出しノズル、29:コ
ンプレッサ、31:冷却水スプレノズル、33:冷却水
噴射ポンプ、34:冷却水槽、35:コンベアフライ、
36:駆動チェーン 37:エプロンコンベア、38:
コンベア水槽、39:コンベア上蓋、40:落じんシュ
ート、41:自動コントロール装置、42:ダンパ。FIG. 1-A is an explanatory diagram showing an ash processing device of a conventional municipal waste incineration facility, FIG. 1-B is a sectional view of a flight conveyor taken along line a-a in FIG. 1-A, and FIG. 2 is a municipal waste according to the present invention. 3-A is an enlarged explanatory diagram of the main parts; FIG. 3-B is a sectional view taken along line a'-a' of FIG. 3A; FIG. 3-C is a diagram of b of FIG. 3A. It is a sectional view along line -b. Names of component equipment in the drawing: 1: Garbage hopper and chute, 2: Supply feeder, 3 Nistoker, 4: Air box and dust removal hopper, 5: Ash removal chute, 6: Flight conveyor, 7: Combustion residue storage pit, 8 : Ash removal crane, 9:
Ridding shoe, 10: rotary valve, 11: radiant and contact sawn boiler, 12: boiler drum, 13
: Electrostatic precipitator, 14, 43: Gas dust, 15: Suction blower, 16: E/P ash transfer conveyor, 17: Curtain, 18: Intake chamber, 19: Suction duct, 20; Intake blower, 21, 23: Cyclone Separator, 22,
30, 32, 44: conduit, 24: bag filter,
25: Ridling suction blower, 26: Exhaust duct, 27
: Cane conveyor, 28: Air blowing nozzle, 29: Compressor, 31: Cooling water spray nozzle, 33: Cooling water injection pump, 34: Cooling water tank, 35: Conveyor fly,
36: Drive chain 37: Apron conveyor, 38:
Conveyor water tank, 39: Conveyor top lid, 40: Dust chute, 41: Automatic control device, 42: Damper.
Claims (1)
ュートをフライトコンベアに結合し、そのフライトコン
ベア内を複数の隔室で区切り、その中の一室から自動制
御装置を備えたブロワで内気を吸引し、焼却炉下部炉内
圧力と同圧に保たせることによって焼却炉内への外気進
入を防止することを特徴とした都市ごみ焼却設備の乾式
灰引出し装置。 2 @記ブロワで吸引する室内の移送中の燃焼残渣に向
けて圧縮空気を空気吹出しノズルで吹きつけ、残渣中の
軽い灰分を強制的に飛散させ、そのブロワで吸引し、移
送燃焼残渣が残渣貯蔵ピットに落下する時の粉じん発生
を防止することを特徴とする特許請求の範囲第1項記載
の都市ごみ焼却設備の乾式灰引出し装置。 3 前記ブロワで吸引した吸気中の粉じんをサイクロン
セパレータで除去した後に、焼却炉下部ホッパ導管に導
ひき、焼却炉火格子空気溝より落ちる未燃カーボンを伴
ったりドリング灰を気体輸送し、第2のサイクロンセパ
レータで捕集し、これを焼却炉中に戻して、未然カーボ
ンを燃焼させるようにしたことを特徴とする特許請求の
範囲第1項又は第2項に記載都市ごみ焼却設備の乾式灰
弓出し装置。[Claims] 1. An ash removal chute for dropping combustion residue from a municipal waste incinerator is connected to a flight conveyor, the inside of the flight conveyor is divided into a plurality of compartments, and an automatic control device is operated from one of the compartments. A dry ash extraction device for municipal waste incineration equipment, which prevents outside air from entering the incinerator by sucking inside air with a blower and keeping it at the same pressure as the pressure inside the lower part of the incinerator. 2. Blow compressed air with an air blowing nozzle toward the combustion residue being transferred in the room, which is sucked in by the blower, to forcibly scatter the light ash in the residue, and then suck it in with the blower to remove the transferred combustion residue. A dry ash extraction device for a municipal waste incineration facility according to claim 1, characterized in that it prevents generation of dust when the ash falls into a storage pit. 3 After the dust in the intake air sucked in by the blower is removed by a cyclone separator, it is guided to the lower hopper conduit of the incinerator, and the unburned carbon and drying ash that fall from the incinerator grate air groove is transported as a gas, and the Dry ash from a municipal waste incineration facility as set forth in claim 1 or 2, characterized in that the ash is collected by a cyclone separator and returned to an incinerator to burn unused carbon. Bow-shooting device.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP10820676A JPS5855409B2 (en) | 1976-09-09 | 1976-09-09 | Dry ash extraction device for municipal waste incineration equipment |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP10820676A JPS5855409B2 (en) | 1976-09-09 | 1976-09-09 | Dry ash extraction device for municipal waste incineration equipment |
Publications (2)
Publication Number | Publication Date |
---|---|
JPS5334373A JPS5334373A (en) | 1978-03-30 |
JPS5855409B2 true JPS5855409B2 (en) | 1983-12-09 |
Family
ID=14478698
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP10820676A Expired JPS5855409B2 (en) | 1976-09-09 | 1976-09-09 | Dry ash extraction device for municipal waste incineration equipment |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS5855409B2 (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS6028813U (en) * | 1983-08-05 | 1985-02-27 | ヤンマー農機株式会社 | Combine harvester with steering control device |
Families Citing this family (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS54154170A (en) * | 1978-05-24 | 1979-12-05 | Takuma Co Ltd | Melting type afterburner connected with stoker type incinerator |
JPS558560A (en) * | 1978-07-04 | 1980-01-22 | Hitachi Plant Eng & Constr Co Ltd | Apparatus for dry discharge of residue, etc. from furnace |
JPS56129043A (en) * | 1980-03-14 | 1981-10-08 | Ngk Insulators Ltd | Honeycomb structure of ceramic |
JP3394449B2 (en) | 1998-06-18 | 2003-04-07 | 日本碍子株式会社 | Thin-walled honeycomb structure and method of reinforcing the same |
JP4504660B2 (en) | 2003-11-13 | 2010-07-14 | 日本碍子株式会社 | Ceramic honeycomb structure |
-
1976
- 1976-09-09 JP JP10820676A patent/JPS5855409B2/en not_active Expired
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS6028813U (en) * | 1983-08-05 | 1985-02-27 | ヤンマー農機株式会社 | Combine harvester with steering control device |
Also Published As
Publication number | Publication date |
---|---|
JPS5334373A (en) | 1978-03-30 |
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