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JPH0219372B2 - - Google Patents
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JPH0219372B2 - - Google Patents

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Publication number
JPH0219372B2
JPH0219372B2 JP59190051A JP19005184A JPH0219372B2 JP H0219372 B2 JPH0219372 B2 JP H0219372B2 JP 59190051 A JP59190051 A JP 59190051A JP 19005184 A JP19005184 A JP 19005184A JP H0219372 B2 JPH0219372 B2 JP H0219372B2
Authority
JP
Japan
Prior art keywords
hot air
combustion
furnace
raw material
air
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 - Lifetime
Application number
JP59190051A
Other languages
Japanese (ja)
Other versions
JPS6170314A (en
Inventor
Nagaharu Okuno
Akitoshi Yamada
Kenichi Yoshida
Katsushi Nagata
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.)
NGK Insulators Ltd
Original Assignee
NGK Insulators 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 NGK Insulators Ltd filed Critical NGK Insulators Ltd
Priority to JP19005184A priority Critical patent/JPS6170314A/en
Publication of JPS6170314A publication Critical patent/JPS6170314A/en
Publication of JPH0219372B2 publication Critical patent/JPH0219372B2/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
    • F23G5/02Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
    • F23G5/04Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment drying
    • 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
    • F23G5/08Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating
    • F23G5/085High-temperature heating means, e.g. plasma, for partly melting the waste
    • 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
    • F23G5/32Incineration of waste; Incinerator constructions; Details, accessories or control therefor the waste being subjected to a whirling movement, e.g. cyclonic incinerators

Landscapes

  • Engineering & Computer Science (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Physics & Mathematics (AREA)
  • Plasma & Fusion (AREA)
  • Gasification And Melting Of Waste (AREA)
  • Incineration Of Waste (AREA)
  • Fluidized-Bed Combustion And Resonant Combustion (AREA)

Description

【発明の詳細な説明】[Detailed description of the invention]

(産業上の利用分野) 本発明は下水処理場やごみ処理場等から発生す
る汚泥を乾燥させ、得られた乾燥汚泥のような粉
体原料を熱効率良く溶融処理してスラグ化するこ
とができる旋回流式燃焼溶融炉を用いた汚泥処理
装置に関するものである。 (従来の技術) 傾斜円筒状の炉体の内部に下水汚泥等を乾燥さ
せた乾燥汚泥等の粉体原料を燃焼用熱風に乗せて
接線方向に噴射し、炉体の内部で旋回させつつ燃
焼させるとともに燃焼灰を溶融させて炉体基部の
炉出口部から流出させるようにした旋回流式燃焼
溶融炉は従来から知られており、このような旋回
流式燃焼溶融炉を汚泥乾燥装置と組み合わせて汚
泥処理することも既に行われている。 (発明が解決しようとする問題点) ところが上記のような従来の旋回流式燃焼溶融
炉においては、粉体原料の平均粒径が105μパス
のものが50%以下と粗くなると燃焼時間が長くな
り焼却灰が炉内で完全に溶融されずに煙道まで飛
散して煙道の閉塞を生じ、逆に105μパスのもの
が50%以上と細かくなると浮遊状態で燃焼し易い
ためやはり焼却灰が煙道まで飛散して閉塞を生じ
易い問題があつた。また、処理量を増大させると
未燃物を生じ易く、逆に処理量が少なすぎる場合
には炉内における発熱量が減少するために炉内を
安定した高温に維持することができない問題もあ
つた。 更に旋回流式燃焼溶融炉と組み合わせて使用さ
れる汚泥乾燥装置からは悪臭が発生し、上記の焼
却灰や未燃物とともに付近の住民に迷惑をかける
ことがあつた。 (問題点を解決するための手段) 本発明は上記のような従来の問題点を解消する
ために完成されたものであり、汚泥乾燥装置と旋
回流式燃焼溶融炉とを組み合わせた汚泥処理装置
において、旋回流式燃焼溶融炉が先端部にバーナ
ーを備えた傾斜円筒状の炉体の先方部に粉体原料
を燃焼用熱風に乗せて炉体の内部へ接線方向に噴
射する原料噴射管を設けるとともに該炉体の基部
の炉出口部に近い位置に上記噴射により生ずる旋
回流と同方向に燃焼用熱風を噴射する熱風噴射管
を設けた構造のものであり、かつ熱風噴射管の燃
焼用熱風として汚泥乾燥装置から生じた乾燥空気
を含んだ空気を使用し、その風量を原料噴射管の
燃焼用熱風の風量以下としたことを特徴とするも
のである。 次に本発明を実施例について詳細に説明する。 (実施例) 第1図は本発明に用いられる旋回流式燃焼溶融
炉を示す一部切欠斜視図であり、1は傾斜円筒状
の炉体、2は該炉体1の先端部に設けられたバー
ナーであり、該バーナー2はオイル供給管3とオ
イル圧送用の圧縮空気供給管4とオイル燃焼用の
圧縮空気供給管5とを備え、オイル燃焼によつて
生ずる高温の燃焼ガスを炉体1の先端部から炉体
1の内部に吹込むものである。6は炉体1のバー
ナー2に近い先方部に炉体1の内壁に対して接線
方向に設けられた原料噴射管であり、下水汚泥等
を乾燥させた乾燥汚泥のような粉体原料をフアン
により供給する原料供給管7と燃焼用熱風を供給
する熱風供給管8とを備え、粉体原料を燃焼用熱
風に乗せて炉体1の内部へ接線方向に噴射するも
のである。 このようにして噴射された粉体原料及び燃焼用
熱風は炉体1の内部を旋回しつつバーナー2の熱
によつて燃焼され、焼却灰は溶融してスラグ化し
て断面が縮小された炉体基部の炉出口部9から下
方へ流出することとになるが、この炉出口部9か
ら30mm〜250mm程度の近い位置には300〜500℃程
度の高温の燃焼用熱風を上記の噴射により生ずる
旋回流と同一方向に噴射する熱風噴射管10が設
けられている。この熱風噴射管10は炉体1内の
炉出口部9に近い部分に熱風によるエアカーテン
を形成して未燃物や未溶融の焼却灰が炉外へ流出
することを防止するためのもので、その風速は熱
風供給管8から吹込まれる燃焼用熱風と同じかあ
るいはそれ以上として旋回流に対抗できるように
し、その風量は旋回流を妨害することのないよう
熱風供給管8からの燃焼用熱風と同量乃至半分と
する。なお、11は排ガス用の煙道、12は炉出
口部9の下方に形成された溶融スラグ排出口であ
る。 第2図は上記の旋回流式燃焼溶融炉と汚泥乾燥
装置とを組み合わせた汚泥処理装置を示すもの
で、20は脱水汚泥貯留槽、21は脱水汚泥供給
機、22は熱風粉砕乾燥式の汚泥乾燥装置、23
は粉砕ハンマー、24は分級機、25はバグフイ
ルタ、26は除湿塔、27は熱交換器、28は溶
融スラグ結晶化装置である。後述するように、旋
回流式燃焼溶融炉の熱風噴射管10から噴出され
る燃焼用熱風として、汚泥乾燥装置22から生じ
た乾燥空気を含んだ空気が使用されている。 (作 用) このように構成されたものは、脱水汚泥貯留槽
20に貯留された脱水汚泥を汚泥乾燥装置22に
より乾燥、粉砕、分級し、分級された乾燥汚泥で
ある粉体原料をバグフイルタ25により補集した
うえブロア29により原料供給管7へ送るととも
に、バグフイルタ25で分離された乾燥空気はブ
ロア30により除湿塔26、熱交換器27へ送ら
れ排ガスにより400〜500℃に加熱されたうえでそ
の一部は熱風供給管8へ、残りの一部は熱風噴射
管10へ、残部は熱風粉砕式の汚泥乾燥装置22
へと送られるものである。そして粉体原料は傾斜
円筒状の炉体1の先方部の原料噴射管6から燃焼
用熱風に乗せられて炉体1の内部へ接線方向に噴
射されて炉体1の内部を旋回流となつて旋回する
間に、炉体1の先端部のバーナー2の熱により燃
焼されるとともに焼却灰も炉内の高温により溶融
して溶融スラグとなり、炉体1の基部の炉出口部
9へ向かつて移動して行く。 しかし本発明では炉出口部9に近い位置に上記
旋回流と同方向に熱風供給管8からの燃焼用熱風
の風量以下の燃焼用熱風を噴射する熱風噴射管1
0が設けられており、旋回流を妨害することなく
高温のエアカーテンを形成しているので、粉体原
料の粒度が粗い場合や処理量を増大させたい場合
にも未燃物や未溶融の焼却灰はこのエアカーテン
に捕捉されて燃焼溶融されることとなり、そのま
ま煙道11へ排出されることがない。また、粉体
原料の粒度が細かい場合にも旋回流中に浮遊して
いる焼却灰は同様にこのエアカーテンにより捕捉
され、処理量が少く炉内における発熱量が少い場
合にも炉内の温度は熱風噴射管10から噴射され
る燃焼用熱風により安定した高温に維持されるの
で粉体原料は完全に溶融スラグ化して溶融スラグ
排出口12へ流出するものである。 更に本発明においては、熱風噴射管10の燃焼
用熱風として汚泥乾燥装置22から生じた乾燥空
気を含んだ空気を使用しているため、この乾燥空
気中の悪臭成分は炉内で分解されてしまい、旋回
流式燃焼溶融炉から大気中に放出される排ガスは
無臭となる。 本発明の効果を測定するために、次のとおりの
実験を行つた。 先ず、水分76〜80%、強熱減料60%、発熱量
3000Kcal/Kgの下水汚泥の脱水ケーキを熱風粉
砕乾燥式の汚泥乾燥装置に170Kg/Hの割合で投
入し、乾燥粉砕して平均水分5%の粉体原料とし
た。これを予め1000℃に保熱されている500φ×
700の炉体内へ50〜80Kg/Hの割合で噴射し、
熱風噴射管から噴射される燃焼用熱風の風量や炉
内温度等の条件を変化させてスラグ補集率を測定
した。その結果は次表のとおりである。なお表
中、風量比は熱風噴射管10からの風量/原料噴
射管6からの風量をNm3/Hで示したものであ
り、表2の平均粒径は105μパスの比率を%で示
したものである。
(Industrial Application Field) The present invention is capable of drying sludge generated from sewage treatment plants, garbage treatment plants, etc., and thermally efficiently melting and converting powdered raw materials such as the obtained dried sludge into slag. This invention relates to a sludge treatment device using a swirling flow combustion melting furnace. (Prior technology) Powder raw materials such as dried sludge, which is made by drying sewage sludge, etc., are placed inside an inclined cylindrical furnace body and are injected in the tangential direction with hot air for combustion, and burned while swirling inside the furnace body. Swirling flow type combustion melting furnaces have been known in the past, in which combustion ash is melted and flowed out from the furnace outlet at the base of the furnace body. Sludge treatment is already being carried out. (Problem to be Solved by the Invention) However, in the conventional swirling flow combustion melting furnace as described above, when the average particle diameter of the powder raw material is less than 50% of the 105μ path, the combustion time becomes longer. The incinerated ash is not completely melted in the furnace and scatters to the flue, causing a blockage of the flue.On the other hand, if the 105μ pass becomes more than 50% fine, it tends to burn in a suspended state, so the incinerated ash becomes a smoke. There was a problem that it could easily spread to the road and cause blockages. Additionally, if the throughput is increased, unburned material is likely to be generated, and conversely, if the throughput is too small, the amount of heat generated inside the furnace decreases, making it impossible to maintain a stable high temperature inside the furnace. Ta. Furthermore, the sludge drying equipment used in combination with the swirl-flow combustion melting furnace emitted a foul odor, which, along with the incinerated ash and unburned materials mentioned above, caused a nuisance to nearby residents. (Means for Solving the Problems) The present invention was completed in order to solve the above-mentioned conventional problems, and provides a sludge treatment device that combines a sludge drying device and a swirling flow combustion melting furnace. In a swirl-flow combustion melting furnace, a raw material injection tube is installed at the front end of an inclined cylindrical furnace body with a burner at the tip to inject the powdered raw material onto hot combustion air in a tangential direction into the inside of the furnace body. In addition, a hot air injection pipe for injecting hot air for combustion in the same direction as the swirling flow generated by the injection is provided at a position near the furnace outlet at the base of the furnace body, and a hot air injection pipe for combustion is provided at the base of the furnace body. This method is characterized in that air containing dry air generated from a sludge drying device is used as the hot air, and the air volume is set to be less than the air volume of the combustion hot air from the raw material injection pipe. Next, the present invention will be explained in detail with reference to examples. (Example) Fig. 1 is a partially cutaway perspective view showing a swirling flow type combustion melting furnace used in the present invention, in which 1 is a slanted cylindrical furnace body, 2 is a furnace body 1 provided at its tip. The burner 2 is equipped with an oil supply pipe 3, a compressed air supply pipe 4 for pressure-feeding oil, and a compressed air supply pipe 5 for oil combustion. 1 into the inside of the furnace body 1. Reference numeral 6 denotes a raw material injection pipe installed in a tangential direction to the inner wall of the furnace body 1 at the front end of the furnace body 1 near the burner 2, and is used to inject powder raw materials such as dried sludge obtained by drying sewage sludge etc. into the fan. The furnace is equipped with a raw material supply pipe 7 for supplying raw material through a combustion chamber and a hot air supply pipe 8 for supplying hot air for combustion, and the powder raw material is carried on the hot air for combustion and is injected into the interior of the furnace body 1 in a tangential direction. The powder raw material and hot air for combustion injected in this way are burned by the heat of the burner 2 while swirling inside the furnace body 1, and the incineration ash is melted and turned into slag, and the furnace body has a reduced cross section. It will flow downward from the furnace outlet 9 at the base, and at a position close to the furnace outlet 9, about 30 mm to 250 mm, hot combustion air with a high temperature of about 300 to 500°C is generated by the swirling air generated by the above injection. A hot air injection pipe 10 is provided which sprays in the same direction as the flow. This hot air injection pipe 10 is used to form an air curtain of hot air in a portion of the furnace body 1 near the furnace outlet 9 to prevent unburned materials and unmelted incineration ash from flowing out of the furnace. The wind speed is set to be the same as or higher than the combustion hot air blown from the hot air supply pipe 8 to counter the swirling flow, and the air volume is set to be equal to or higher than the combustion hot air blown from the hot air supply pipe 8 so as not to disturb the swirling flow. Use the same amount to half the amount of hot air. In addition, 11 is a flue for exhaust gas, and 12 is a molten slag discharge port formed below the furnace outlet part 9. Fig. 2 shows a sludge treatment device that combines the above-mentioned swirl flow type combustion melting furnace and sludge drying device, in which 20 is a dehydrated sludge storage tank, 21 is a dehydrated sludge feeder, and 22 is a hot air pulverized drying type sludge. Drying device, 23
24 is a crushing hammer, 24 is a classifier, 25 is a bag filter, 26 is a dehumidifying tower, 27 is a heat exchanger, and 28 is a molten slag crystallization device. As will be described later, air containing dry air generated from the sludge drying device 22 is used as the combustion hot air ejected from the hot air injection pipe 10 of the swirling flow combustion melting furnace. (Function) In the device configured as described above, the dehydrated sludge stored in the dehydrated sludge storage tank 20 is dried, crushed, and classified by the sludge drying device 22, and the powder raw material, which is the classified dry sludge, is transferred to the bag filter 25. The dried air is collected by a blower 29 and sent to the raw material supply pipe 7, and the dried air separated by a bag filter 25 is sent to a dehumidifying tower 26 and a heat exchanger 27 by a blower 30, where it is heated to 400 to 500°C by exhaust gas. A part of it goes to the hot air supply pipe 8, the other part goes to the hot air injection pipe 10, and the rest goes to the hot air crushing type sludge dryer 22.
It is sent to. The powder raw material is then tangentially injected into the furnace body 1 from the raw material injection pipe 6 at the front end of the slanted cylindrical furnace body 1 on hot air for combustion, forming a swirling flow inside the furnace body 1. While rotating, the incinerated ash is burned by the heat of the burner 2 at the tip of the furnace body 1, and the incinerated ash is also melted by the high temperature inside the furnace, becoming molten slag, and heading toward the furnace outlet 9 at the base of the furnace body 1. Move and go. However, in the present invention, a hot air injection pipe 1 that injects combustion hot air less than the amount of combustion hot air from the hot air supply pipe 8 in the same direction as the swirling flow at a position close to the furnace outlet 9.
0 is provided to form a high-temperature air curtain without interfering with the swirling flow, so even if the particle size of the powder raw material is coarse or when you want to increase the throughput, unburned and unmelted materials can be removed. Incineration ash is captured by this air curtain and burned and melted, and is not discharged to the flue 11 as it is. In addition, even when the particle size of the powder raw material is fine, the incineration ash floating in the swirling flow is similarly captured by this air curtain, and even when the throughput is small and the amount of heat generated in the furnace is small, the incineration ash inside the furnace is Since the temperature is maintained at a stable high temperature by the combustion hot air injected from the hot air injection pipe 10, the powder raw material is completely turned into molten slag and flows out to the molten slag discharge port 12. Furthermore, in the present invention, since air containing dry air generated from the sludge drying device 22 is used as the hot air for combustion in the hot air injection pipe 10, malodorous components in this dry air are decomposed in the furnace. , the exhaust gas released into the atmosphere from the swirl-flow combustion melting furnace is odorless. In order to measure the effects of the present invention, the following experiment was conducted. First, moisture 76-80%, ignition reduction 60%, calorific value
A dehydrated cake of 3000 Kcal/Kg of sewage sludge was put into a hot air pulverization drying type sludge dryer at a rate of 170 Kg/H, and was dried and pulverized to obtain a powder material with an average moisture content of 5%. This is 500φ× which is preheated at 1000℃.
700 into the furnace body at a rate of 50 to 80 kg/H,
The slag collection rate was measured by changing conditions such as the amount of combustion hot air injected from the hot air injection pipe and the temperature inside the furnace. The results are shown in the table below. In the table, the air volume ratio is the air volume from the hot air injection pipe 10/the air volume from the raw material injection pipe 6 in Nm 3 /H, and the average particle size in Table 2 is the ratio of the 105 μ path in %. It is something.

【表】【table】

【表】 (発明の効果) 本発明は以上の説明から明らかなように、粉体
原料の粒度の大小や処理量の増減にかかわらず常
に安定した溶融を行わせることができ、未燃物や
焼却灰が煙道へ飛散することによる煙道の閉塞を
防止できるものであるうえ、汚泥乾燥装置から生
ずる悪臭成分を含有する空気を熱分解することが
できるから、公害防止上極めて有効である。 よつて本発明は従来の旋回流式燃焼溶融炉を用
いた汚泥処理装置の問題点を一掃したものとして
産業の発展に寄与するところは極めて大きいもの
である。
[Table] (Effects of the Invention) As is clear from the above explanation, the present invention can always perform stable melting regardless of the particle size of the powder raw material or the increase or decrease in the throughput, and it can eliminate unburned materials and It is extremely effective in preventing pollution because it can prevent clogging of the flue due to incineration ash scattering into the flue, and it can also thermally decompose the air containing malodorous components generated from the sludge drying equipment. Therefore, the present invention greatly contributes to the development of industry by eliminating the problems of conventional sludge treatment equipment using a swirling flow type combustion melting furnace.

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

第1図は本発明に使用される旋回流式燃焼溶融
炉を示す一部切欠斜視図、第2図は本発明の旋回
流式燃焼溶融炉を用いた汚泥処理装置の配置説明
図である。 1:炉体、2:バーナー、6:原料噴射管、
9:炉出口部、10:熱風噴射管、22:汚泥乾
燥装置。
FIG. 1 is a partially cutaway perspective view showing a swirling flow type combustion melting furnace used in the present invention, and FIG. 2 is a layout explanatory diagram of a sludge treatment apparatus using the swirling flow type combustion melting furnace of the present invention. 1: Furnace body, 2: Burner, 6: Raw material injection pipe,
9: Furnace outlet section, 10: Hot air injection pipe, 22: Sludge drying device.

Claims (1)

【特許請求の範囲】[Claims] 1 汚泥乾燥装置と旋回流式燃焼溶融炉とを組み
合わせた汚泥処理装置において、旋回流式燃焼溶
融炉が先端部にバーナー2を備えた傾斜円筒状の
炉体1の先方部に粉体原料を燃焼用熱風に乗せて
炉体1の内部へ接線方向に噴射する原料噴射管6
を設けるとともに該炉体1の基部の炉出口部9に
近い位置に上記噴射により生ずる旋回流と同方向
に燃焼用熱風を噴射する熱風噴射管10を設けた
構造のものであり、かつ熱風噴射管10の燃焼用
熱風として汚泥乾燥装置22から生じた乾燥空気
を含んだ空気を使用し、その風量を原料噴射管6
の燃焼用熱風の風量以下としたことを特徴とする
旋回流式燃焼溶融炉を用いた汚泥処理装置。
1 In a sludge treatment device that combines a sludge drying device and a swirling flow combustion melting furnace, the swirling flow combustion melting furnace supplies powder raw material to the front part of an inclined cylindrical furnace body 1 equipped with a burner 2 at the tip. A raw material injection pipe 6 that injects tangentially into the inside of the furnace body 1 on hot air for combustion
It has a structure in which a hot air injection pipe 10 for injecting hot air for combustion in the same direction as the swirling flow generated by the above injection is provided at a position near the furnace outlet part 9 at the base of the furnace body 1, and Air containing dry air generated from the sludge drying device 22 is used as hot air for combustion in the pipe 10, and the air volume is adjusted to the raw material injection pipe 6.
A sludge treatment device using a swirling flow combustion melting furnace, characterized in that the amount of hot air for combustion is less than or equal to the amount of hot air for combustion.
JP19005184A 1984-09-11 1984-09-11 Whirling stream type fired melting furnace Granted JPS6170314A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP19005184A JPS6170314A (en) 1984-09-11 1984-09-11 Whirling stream type fired melting furnace

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP19005184A JPS6170314A (en) 1984-09-11 1984-09-11 Whirling stream type fired melting furnace

Publications (2)

Publication Number Publication Date
JPS6170314A JPS6170314A (en) 1986-04-11
JPH0219372B2 true JPH0219372B2 (en) 1990-05-01

Family

ID=16251523

Family Applications (1)

Application Number Title Priority Date Filing Date
JP19005184A Granted JPS6170314A (en) 1984-09-11 1984-09-11 Whirling stream type fired melting furnace

Country Status (1)

Country Link
JP (1) JPS6170314A (en)

Families Citing this family (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH01170833U (en) * 1988-05-16 1989-12-04
JPH0814366B2 (en) * 1988-07-22 1996-02-14 日揮株式会社 Combustion device
JP2769623B2 (en) * 1988-07-22 1998-06-25 月島機械株式会社 Inclined horizontal circulation melting method and apparatus
ZA896971B (en) * 1988-09-14 1990-06-27 M Kent John Method and apparatus for using hazardous waste to form non-hazardous aggregate
JP2531901B2 (en) * 1992-06-12 1996-09-04 株式会社神戸製鋼所 Waste treatment furnace and waste treatment method by the waste treatment furnace
KR100352790B1 (en) * 1999-11-05 2002-09-16 (주)대우 Device for the treatment of the sludge by burning and melting

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5248429B2 (en) * 1972-01-28 1977-12-09
JPS5666613A (en) * 1979-11-06 1981-06-05 Kurita Water Ind Ltd Waste incinerating device

Also Published As

Publication number Publication date
JPS6170314A (en) 1986-04-11

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