JP2752333B2 - Waste incineration method and apparatus - Google Patents

Waste incineration method and apparatus

Info

Publication number
JP2752333B2
JP2752333B2 JP7047436A JP4743695A JP2752333B2 JP 2752333 B2 JP2752333 B2 JP 2752333B2 JP 7047436 A JP7047436 A JP 7047436A JP 4743695 A JP4743695 A JP 4743695A JP 2752333 B2 JP2752333 B2 JP 2752333B2
Authority
JP
Japan
Prior art keywords
fluidized bed
sintering furnace
waste
bed incinerator
ash
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 - Fee Related
Application number
JP7047436A
Other languages
Japanese (ja)
Other versions
JPH08247426A (en
Inventor
一博 小泉
隆之 森
理 石川
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.)
NIPPON GAISHI KK
Original Assignee
NIPPON GAISHI KK
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Filing date
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Application filed by NIPPON GAISHI KK filed Critical NIPPON GAISHI KK
Priority to JP7047436A priority Critical patent/JP2752333B2/en
Publication of JPH08247426A publication Critical patent/JPH08247426A/en
Application granted granted Critical
Publication of JP2752333B2 publication Critical patent/JP2752333B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Processing Of Solid Wastes (AREA)
  • Treatment Of Sludge (AREA)

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】本発明は、下水汚泥、都市ゴミ、
産業廃棄物等の廃棄物を流動層焼却炉により焼却する廃
棄物焼却方法及び装置に関するものである。
The present invention relates to sewage sludge, municipal waste,
The present invention relates to a waste incineration method and apparatus for incinerating waste such as industrial waste by a fluidized bed incinerator.

【0002】[0002]

【従来の技術】従来一般の流動層焼却炉は、流動媒体と
して粒径が0.3 〜0.9mm程度のケイ砂を用いて流動層を
形成したもので、この流動媒体を650 〜800 ℃に保持し
た状態で廃棄物を投入し、流動媒体の熱容量と攪拌作用
によって燃焼を行わせるようにしたものである。
2. Description of the Related Art A conventional general fluidized bed incinerator has a fluidized bed formed of silica sand having a particle size of about 0.3 to 0.9 mm as a fluidized medium, and the fluidized medium is maintained at 650 to 800.degree. Waste is charged in this state, and combustion is performed by the heat capacity of the fluid medium and the stirring action.

【0003】ところがこのような流動層焼却炉から排出
される焼却灰は微粒子であるために粉塵を発生し易く、
また嵩密度も0.4 〜0.7t/m3 と非常に小さいためにハン
ドリングが容易ではなく、埋め立て費用も嵩むという問
題があった。しかも前記流動媒体の吹き飛びを防止する
ために炉内の流速を約1.2m/s以下に抑制しなければなら
ず、炉の単位面積当たりの処理量を増加させることがで
きないという問題があった。
[0003] However, incineration ash discharged from such a fluidized bed incinerator is liable to generate dust because it is fine particles.
Further, since the bulk density is very small, 0.4 to 0.7 t / m 3 , handling is not easy, and there is a problem that the cost of landfill is increased. In addition, the flow rate in the furnace must be suppressed to about 1.2 m / s or less in order to prevent the fluid medium from being blown off, and there is a problem that the throughput per unit area of the furnace cannot be increased.

【0004】[0004]

【発明が解決しようとする課題】本発明は上記した従来
の問題点を解決し、処分に費用が嵩む微粒子状の焼却灰
の発生をなくして骨材として使用可能な強度の高い造粒
焼結灰を得ることができ、炉の単位面積当たりの処理量
を増加させることができる廃棄物焼却方法及び装置を提
供するためになされたものである。
SUMMARY OF THE INVENTION The present invention solves the above-mentioned conventional problems and eliminates the generation of incinerated ash which is expensive to dispose of. An object of the present invention is to provide a waste incineration method and apparatus capable of obtaining ash and increasing the throughput per unit area of a furnace.

【0005】[0005]

【課題を解決するための手段】上記の課題を解決するた
めになされた本発明の廃棄物焼却方法は、廃棄物を焼却
する流動層焼却炉の排ガスから回収された焼却灰を造粒
し、これを集塵装置により捕集した吹き飛び流動媒体を
前記流動層焼却炉へ返送する返送管の途中に設置した前
記流動層焼却炉よりも高温の流動層焼結炉に投入し、焼
結することを特徴とするものである。
Means for Solving the Problems A waste incineration method according to the present invention, which has been made to solve the above problems, granulates incinerated ash recovered from exhaust gas of a fluidized bed incinerator for incinerating waste. This is thrown into a fluidized bed sintering furnace having a higher temperature than the fluidized bed incinerator installed in the return pipe for returning the blown-off fluid medium collected by the dust collecting device to the fluidized bed incinerator, and sintering. It is characterized by the following.

【0006】また上記の課題を解決するためになされた
本発明の廃棄物焼却装置は、廃棄物を焼却する流動層焼
却炉と、吹き飛び流動媒体を回収する一次集塵装置と、
排ガスから焼却灰を回収する二次集塵装置と、回収され
た焼却灰を造粒する造粒機と、造粒灰を流動させつつ前
記流動層焼却炉よりも高温で焼結する流動層焼結炉と、
一次集塵装置により捕集した吹き飛び流動媒体を流動層
焼結炉へ返送し、また高温となった流動層焼結炉中の流
動媒体および流動層焼結炉排ガスを前記流動層焼却炉へ
返送する返送管とからなることを特徴とするものであ
る。
[0006] Further, a waste incinerator according to the present invention, which has been made to solve the above-mentioned problems, comprises a fluidized bed incinerator for incinerating waste, a primary dust collector for collecting a blow-off fluid medium, and
A secondary dust collector for collecting incinerated ash from exhaust gas, a granulator for granulating the collected incinerated ash, and a fluidized bed sintering sintering at a higher temperature than the fluidized bed incinerator while flowing the granulated ash. Kiln and
The blow-off fluid medium collected by the primary dust collector is returned to the fluidized bed sintering furnace, and the fluidized medium in the fluidized bed sintering furnace and the exhaust gas of the fluidized bed sintering furnace which have become high temperature are returned to the fluidized bed incinerator. And a return pipe.

【0007】[0007]

【作用】本発明によれば、流動層焼却炉の排ガスから回
収された焼却灰を造粒して、これを前記流動層焼却炉よ
りも高温の流動層焼結炉により焼結させるため、従来の
ような微粒子状の焼却灰の発生がなく、強度の高い造粒
焼結灰を得ることができ、骨材等として利用価値が高い
ものとなる。また、炉内流速を4〜8m/sと従来よりも
大幅に増加させることができるため、炉の単位面積当た
りの廃棄物処理量を増加させることができる。
According to the present invention, incineration ash recovered from the exhaust gas of a fluidized bed incinerator is granulated and sintered in a fluidized bed sintering furnace having a higher temperature than the fluidized bed incinerator. As a result, it is possible to obtain a high-strength granulated sintered ash without the generation of incinerated ash in the form of fine particles as described above. Further, the flow rate in the furnace can be significantly increased from 4 to 8 m / s as compared with the conventional method, so that the amount of waste disposal per unit area of the furnace can be increased.

【0008】さらに本発明によれば、流動層焼却炉は廃
棄物の焼却に適した700〜900 ℃に保持し、流動層焼結
炉は造粒灰の焼結に適した900 〜1050℃とすることがで
きるので、焼却と焼結を同じ炉で行わせる場合よりも全
体的な熱エネルギのロスが少ないという利点がある。
Further, according to the present invention, the fluidized bed incinerator is maintained at 700 to 900 ° C suitable for incineration of waste, and the fluidized bed sintering furnace is maintained at 900 to 1050 ° C suitable for sintering granulated ash. Therefore, there is an advantage that the overall heat energy loss is smaller than when incineration and sintering are performed in the same furnace.

【0009】[0009]

【実施例】以下に本発明を図示の実施例により更に詳細
に説明する。1は流動層焼却炉であり、下水汚泥等の廃
棄物は廃棄物投入口2から炉内に投入され、流動空気に
より流動層を形成している流動媒体3との接触により、
700〜900 ℃で焼却される。本発明では流動層焼却炉1
内の流速は従来の流動層焼却炉よりも大幅に大きい4〜
8m/s に設定されるため、流動媒体3は炉頂より排ガス
とともに吹き飛んで炉外へ排出されるが、サイクロン等
の一次集塵装置14により排ガスと吹き飛び流動媒体とは
分離され、吹き飛び流動媒体は返送管15により流動層焼
結炉16に送られる。微細な焼却灰を含む排ガスは第1熱
交換器4と第2熱交換器5とを通過する間にブロワ6、
7から供給される空気との間で熱交換を行い冷却された
のち、バグフィルタ等の二次集塵装置8に導かれる。
DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described below in more detail with reference to the illustrated embodiments. Reference numeral 1 denotes a fluidized bed incinerator, and waste such as sewage sludge is introduced into the furnace through a waste inlet 2 and contacts with a fluidized medium 3 forming a fluidized bed by fluidized air.
Incinerated at 700-900 ° C. In the present invention, the fluidized bed incinerator 1
The flow rate inside the furnace is significantly higher than that of the conventional fluidized bed incinerator.
Since the flow rate is set to 8 m / s, the fluid medium 3 is blown off from the furnace top together with the exhaust gas and discharged to the outside of the furnace. Is sent to a fluidized bed sintering furnace 16 by a return pipe 15. Exhaust gas containing fine incineration ash passes through the first heat exchanger 4 and the second heat exchanger 5 while the blower 6
After being cooled by performing heat exchange with air supplied from 7, the air is guided to a secondary dust collecting device 8 such as a bag filter.

【0010】排ガス中に含まれている微細粒子の焼却灰
は、二次集塵装置8によって回収される。回収された焼
却灰は造粒機9によって粒径が1〜8mm程度の造粒灰と
され、更に第2熱交換器5から熱を受ける乾燥機10によ
り乾燥されたうえ、流動層焼結炉16に供給される。
The incinerated ash of fine particles contained in the exhaust gas is collected by the secondary dust collector 8. The collected incinerated ash is made into granulated ash having a particle size of about 1 to 8 mm by a granulator 9, further dried by a dryer 10 receiving heat from the second heat exchanger 5, and Supplied to 16.

【0011】この流動層焼結炉16は、流動層焼却炉1よ
りも高温の900 〜1050℃に保持された流動層炉であり、
造粒灰を高温で焼結して強度の高い造粒焼結灰とする。
流動層焼結炉16中の高温となった流動媒体は流動層焼結
炉16の上部から延びる返送管17を介して流動層焼却炉1
へ返送され、流動層焼却炉1の流動媒体3として再び使
用される。このため、流動媒体の吹き飛びを考慮して炉
内流速を下げる必要がなく、従来の5倍程度の4〜8m/
s とすることができ、炉の単位面積当たりの廃棄物処理
量を大幅に向上させることが可能となる。
The fluidized bed sintering furnace 16 is a fluidized bed furnace maintained at a temperature of 900 to 1050 ° C., which is higher than that of the fluidized bed incinerator 1.
The granulated ash is sintered at a high temperature to obtain a granulated ash having high strength.
The high temperature fluid medium in the fluidized bed sintering furnace 16 is passed through a return pipe 17 extending from the upper part of the fluidized bed sintering furnace 16 to obtain the fluidized bed incinerator 1.
To the fluidized medium of the fluidized bed incinerator 1 again. For this reason, there is no need to reduce the flow velocity in the furnace in consideration of the blow-off of the fluid medium, and it is about 5 to 4 times the conventional value of 4 to 8 m / m.
s, and the amount of waste disposal per unit area of the furnace can be greatly improved.

【0012】また、造粒焼結灰は流動層焼結炉16の下端
に設けられたバルブ18から取り出され、高強度骨材とし
て使用できる。12は流動層焼却炉1の下端の不燃物排出
口13に設けられたバルブであり、このバルブ12を開いて
不燃物を排出することができる。不燃物排出口13より排
出された未燃物については、流動層焼結炉16に投入して
高温で完全燃焼させる。
The granulated sintered ash is taken out from a valve 18 provided at the lower end of the fluidized bed sintering furnace 16 and can be used as high strength aggregate. Numeral 12 is a valve provided at an incombustible discharge port 13 at the lower end of the fluidized bed incinerator 1, and the valve 12 can be opened to discharge incombustibles. The unburned matter discharged from the unburned matter discharge port 13 is put into a fluidized bed sintering furnace 16 and completely burned at a high temperature.

【0013】上記したように本発明によれば微粒子状の
焼却灰を回収して造粒し、これを前記流動層焼却炉1よ
りも高温の流動層焼結炉16により焼結するものである
が、この焼結を流動層焼却炉1において同時に行わせる
ことも考えられる。しかしもしそのような方法を採用し
た場合には、流動層焼却炉1の炉内温度を造粒灰の焼結
に適した温度まで上昇させねばならず、システム全体と
しては熱エネルギのロスが増加することとなる。特に水
分を多量に含む下水汚泥等の場合にはロスが大きく、本
発明者の試算によれば、本発明の方法はこの場合よりも
約5〜15%ほどエネルギ使用量を削減することができ
る。
As described above, according to the present invention, incinerated ash in the form of fine particles is collected, granulated, and sintered in a fluidized bed sintering furnace 16 at a higher temperature than the fluidized bed incinerator 1. However, it is conceivable that this sintering is performed simultaneously in the fluidized bed incinerator 1. However, if such a method is adopted, the temperature inside the fluidized bed incinerator 1 must be raised to a temperature suitable for sintering the granulated ash, and the heat energy loss increases as a whole system. Will be done. In particular, in the case of sewage sludge containing a large amount of water, the loss is large, and the present inventor estimates that the method of the present invention can reduce the energy consumption by about 5 to 15% compared to this case. .

【0014】次に実施例の方法及び装置によって下水汚
泥の焼却を行った結果を示す。使用した下水汚泥は高分
子薬注汚泥を脱水機により水分78%まで脱水したもので
あり、その物性値を表1に示す。
Next, the results of incineration of sewage sludge by the method and apparatus of the embodiment will be described. The used sewage sludge was obtained by dehydrating polymer-injected sludge to a water content of 78% with a dehydrator, and the physical properties are shown in Table 1.

【0015】[0015]

【表1】 [Table 1]

【0016】この実施例では、排ガスから回収された焼
却灰を造粒機9によって粒径が約3〜5mmに造粒した。
造粒灰は造粒直後の状態で約25%の水分を含んでいるた
め、そのまま流動層焼結炉16に投入すると急激な水分蒸
発により粒子が破壊してしまい、回収率が低下する。そ
こで本実施例では第2の熱交換器5により150 ℃に加熱
された熱風を用い、乾燥機10により水分が3%以下とな
るまで乾燥させてから流動層焼結炉16に投入した。
In this embodiment, the incinerated ash recovered from the exhaust gas was granulated by a granulator 9 to a particle size of about 3 to 5 mm.
Since the granulated ash contains about 25% of water immediately after granulation, if it is put into the fluidized bed sintering furnace 16 as it is, the particles are destroyed by rapid water evaporation and the recovery rate is reduced. Therefore, in the present embodiment, the hot air heated to 150 ° C. by the second heat exchanger 5 was used, dried by the dryer 10 until the water content became 3% or less, and then put into the fluidized bed sintering furnace 16.

【0017】使用した流動層焼却炉1は内径0.3 m、高
さ10mの小型の炉であり、流動層焼結炉16は内径0.5
m、高さ2.5 mである。汚泥焼却量は約120kg/hrであ
り、空気比は約1.3 とした。流動層焼却炉1の温度を60
0 、700 、800 、900、1000℃と変化させ、流動層焼結
炉16の温度は800 、900 、1000、1050、1150℃と変化さ
せた。また補助燃料としてLNG(13A)を使用し、流動媒体
にはケイ砂(JIS6号) を用いた。その結果と評価を表2
に示す。
The fluidized bed incinerator 1 used is a small furnace having an inner diameter of 0.3 m and a height of 10 m, and the fluidized bed sintering furnace 16 has an inner diameter of 0.5 m.
m, height 2.5 m. The sludge incineration rate was about 120 kg / hr, and the air ratio was about 1.3. Set the temperature of fluidized bed incinerator 1 to 60
The temperature of the fluidized bed sintering furnace 16 was changed to 800, 900, 1000, 1050, and 1150 ° C. LNG (13A) was used as an auxiliary fuel, and silica sand (JIS No. 6) was used as a fluid medium. Table 2 shows the results and evaluation.
Shown in

【0018】[0018]

【表2】 [Table 2]

【0019】なお、表2中の評価基準は次の通りであ
る。 汚泥燃焼状態は、排ガス中のCO濃度200 ppm 以下、
二次集塵装置により回収した焼却灰の強熱減量1%以下
の場合を◎、CO濃度200 〜300 ppm 、焼却灰の強熱減
量1〜1.5 %のいずれかとなった場合は○、CO濃度30
0 ppm 以上、または焼却灰の強熱減量1.5 %以上となっ
た場合を×とした。 一軸圧潰強度は、5kgf/粒子以上を◎、3〜5kgf/粒
子を○、3kgf/粒子以下を×とした。 粒子残存率については、80%以上を◎、70〜80%を
○、70%以下を×とした。 総合評価は、〜の全て◎の場合を◎、〜にお
いて×はなく○が一つでもある場合を○、〜におい
て×が一つでもある場合を×とした。
The evaluation criteria in Table 2 are as follows. The sludge combustion state is 200 ppm or less of CO concentration in exhaust gas,
◎: If the ignition loss of the incinerated ash collected by the secondary dust collector is 1% or less, ◎, CO: 200 to 300 ppm, or 1 to 1.5% of the incinerated ash: ○, CO concentration 30
A case of 0 ppm or more or a loss on ignition of incinerated ash of 1.5% or more was evaluated as x. The uniaxial crushing strength was evaluated as ◎ for 5 kgf / particle or more, ○ for 3 to 5 kgf / particle, and × for 3 kgf / particle or less. Regarding the particle residual ratio, ◎ indicates 80% or more, ○ indicates 70 to 80%, and X indicates 70% or less. The overall evaluation was evaluated as ◎ when all of 〜 were 、, ○ when there was no X and no に お い て in ○, and × when there was even one X in 〜.

【0020】[0020]

【発明の効果】以上に説明したように、本発明の廃棄物
焼却方法及び装置によれば、処分に費用が嵩む微粒子状
の焼却灰の発生をなくして骨材として使用可能な強度の
高い造粒焼結灰を得ることができる。また炉内流速を4
〜8m/s と従来の流動層焼却炉よりも大幅に増加させる
ことができるため、炉の単位面積当たりの処理量を増加
させることができる。更に本発明によれば、システム全
体のエネルギーロスを防止しつつ、焼却灰を骨材として
有効利用可能な強度の高い造粒焼結灰とすることができ
る。
As described above, according to the waste incineration method and apparatus of the present invention, it is possible to eliminate the generation of particulate incineration ash which is expensive to dispose of, and to provide a high strength material which can be used as an aggregate. Grain sintered ash can be obtained. The flow velocity in the furnace was 4
Since it can be increased to about 8 m / s, which is much larger than that of the conventional fluidized bed incinerator, the throughput per unit area of the furnace can be increased. Further, according to the present invention, it is possible to obtain high-strength granulated sintered ash that can effectively use incinerated ash as aggregate while preventing energy loss of the entire system.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明の実施例を示すブロック図である。FIG. 1 is a block diagram showing an embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1 流動層焼却炉、2 廃棄物投入口、3 流動媒体、
4 第1熱交換器、5第2熱交換器、6 ブロワ、7
ブロワ、8 二次集塵装置、9 造粒機、10乾燥機、12
バルブ、13 不燃物排出口、14 一次集塵装置、15
返送管、16流動層焼結炉、17 返送管、18 バルブ
1 fluidized bed incinerator, 2 waste inlets, 3 fluidized media,
4 First heat exchanger, 5 Second heat exchanger, 6 Blower, 7
Blower, 8 secondary dust collector, 9 granulator, 10 dryer, 12
Valve, 13 Noncombustible material outlet, 14 Primary dust collector, 15
Return pipe, 16 fluidized bed sintering furnace, 17 Return pipe, 18 valve

───────────────────────────────────────────────────── フロントページの続き (58)調査した分野(Int.Cl.6,DB名) F23G 5/30 B09B 3/00 C02F 11/00──────────────────────────────────────────────────続 き Continued on the front page (58) Field surveyed (Int. Cl. 6 , DB name) F23G 5/30 B09B 3/00 C02F 11/00

Claims (2)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 廃棄物を焼却する流動層焼却炉の排ガス
から回収された焼却灰を造粒し、これを集塵装置により
捕集した吹き飛び流動媒体を前記流動層焼却炉へ返送す
る返送管の途中に設置した前記流動層焼却炉よりも高温
の流動層焼結炉に投入し、焼結することを特徴とする廃
棄物焼却方法。
1. A return pipe for granulating incinerated ash collected from exhaust gas of a fluidized bed incinerator for incinerating waste and returning the blown fluid medium collected by a dust collector to the fluidized bed incinerator. A waste fluid incineration method, wherein the waste is put into a fluidized bed sintering furnace at a temperature higher than that of the fluidized bed incinerator installed in the middle of the step and sintered.
【請求項2】 廃棄物を焼却する流動層焼却炉と、吹き
飛び流動媒体を回収する一次集塵装置と、排ガスから焼
却灰を回収する二次集塵装置と、回収された焼却灰を造
粒する造粒機と、造粒灰を流動させつつ前記流動層焼却
炉よりも高温で焼結する流動層焼結炉と、一次集塵装置
により捕集した吹き飛び流動媒体を流動層焼結炉へ返送
し、また高温となった流動層焼結炉中の流動媒体および
流動層焼結炉排ガスを前記流動層焼却炉へ返送する返送
管とからなることを特徴とする廃棄物焼却装置。
2. A fluidized bed incinerator for incinerating waste, a primary dust collector for collecting a blown-away fluid medium, a secondary dust collector for collecting incinerated ash from exhaust gas, and granulating the collected incinerated ash. Bed sintering furnace, a fluidized bed sintering furnace that sinters the granulated ash at a higher temperature than the fluidized bed incinerator, and a blow-off fluid medium collected by the primary dust collector into the fluidized bed sintering furnace. A waste incineration apparatus, comprising: a return pipe for returning a fluidized medium in a fluidized bed sintering furnace and a fluidized bed sintering furnace exhaust gas to the fluidized bed incinerator.
JP7047436A 1995-03-07 1995-03-07 Waste incineration method and apparatus Expired - Fee Related JP2752333B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP7047436A JP2752333B2 (en) 1995-03-07 1995-03-07 Waste incineration method and apparatus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP7047436A JP2752333B2 (en) 1995-03-07 1995-03-07 Waste incineration method and apparatus

Publications (2)

Publication Number Publication Date
JPH08247426A JPH08247426A (en) 1996-09-27
JP2752333B2 true JP2752333B2 (en) 1998-05-18

Family

ID=12775112

Family Applications (1)

Application Number Title Priority Date Filing Date
JP7047436A Expired - Fee Related JP2752333B2 (en) 1995-03-07 1995-03-07 Waste incineration method and apparatus

Country Status (1)

Country Link
JP (1) JP2752333B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4504533B2 (en) * 2000-08-15 2010-07-14 メタウォーター株式会社 Sintering method of granular aggregate
JP5834411B2 (en) * 2011-01-18 2015-12-24 トヨタ自動車株式会社 Fluidized bed equipment
CN102249410A (en) * 2011-05-13 2011-11-23 西安建筑科技大学 Method and device for regenerating granule sludge activity

Also Published As

Publication number Publication date
JPH08247426A (en) 1996-09-27

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