JPH0570519B2 - - Google Patents
Info
- Publication number
- JPH0570519B2 JPH0570519B2 JP61034765A JP3476586A JPH0570519B2 JP H0570519 B2 JPH0570519 B2 JP H0570519B2 JP 61034765 A JP61034765 A JP 61034765A JP 3476586 A JP3476586 A JP 3476586A JP H0570519 B2 JPH0570519 B2 JP H0570519B2
- Authority
- JP
- Japan
- Prior art keywords
- slag
- coolant
- waste
- furnace
- incineration 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
Links
Landscapes
- Gasification And Melting Of Waste (AREA)
- Processing Of Solid Wastes (AREA)
Description
【発明の詳細な説明】
[産業上の利用分野]
本発明は、廃棄物溶融処理炉における溶融物の
急速出滓停止方法に関する。さらに詳しくは、廃
棄物溶融処理炉の運転中、例えば停電のような緊
急事態が発生した場合における廃棄物溶融処理炉
からの溶融物の出滓を即時に停止する方法に係る
ものである。DETAILED DESCRIPTION OF THE INVENTION [Industrial Application Field] The present invention relates to a method for rapidly stopping slag of melt in a waste melting furnace. More specifically, the present invention relates to a method for immediately stopping the flow of molten material from a waste melting furnace when an emergency situation such as a power outage occurs while the waste melting furnace is in operation.
[従来技術]
都市ゴミ焼却灰、下水汚泥焼却灰、皮革処理汚
泥焼却灰等の各種廃棄物は、従来、埋立などによ
り処理されてきた。しかし、埋立用地の確保が困
難であること、含有される有害重金属類が地中に
溶出し、埋立用地周辺を汚染して、二次公害を引
き起す恐れがあることなどから最近では、前記廃
棄物を溶融処理炉で溶融処理し、無害化減容する
方法が提案され、上記問題の解決がはかられてい
る。溶融処理炉の一つとして、アーク式加熱炉が
知られており、その代表例として、サブマージド
アーク加熱炉がある。[Prior Art] Various wastes such as municipal garbage incineration ash, sewage sludge incineration ash, and leather processing sludge incineration ash have conventionally been treated by landfilling or the like. However, due to the difficulty of securing land for landfill, and the risk that the hazardous heavy metals contained in it may leach into the ground and contaminate the area around the landfill site, causing secondary pollution, recently, the above-mentioned disposal A method of melting materials in a melting furnace to render them harmless and reduce their volume has been proposed, and attempts have been made to solve the above problems. An arc heating furnace is known as one type of melting processing furnace, and a typical example thereof is a submerged arc heating furnace.
この溶融炉は、溶融物の出滓口を備えた耐火構
造の炉本体と、廃棄物投入口、複数の主電極、ガ
ス排出ダクト等を備えた炉蓋とからなつており、
これには、出滓口から排出された溶融物を受け入
れて冷却し固化破砕する水砕槽が付設されてい
る。また前記出滓口の手前には、排出中に溶融物
がそこで冷却固化して出滓を妨げられることがな
いように加熱用の補助電極が配置されている。 This melting furnace consists of a furnace body with a fireproof structure equipped with a molten slag outlet, and a furnace lid equipped with a waste inlet, multiple main electrodes, a gas exhaust duct, etc.
This is equipped with a water crushing tank that receives the molten material discharged from the slag outlet, cools it, solidifies it, and crushes it. Further, in front of the slag outlet, an auxiliary electrode for heating is arranged so that the molten material will not be cooled and solidified there during discharge, thereby preventing the slag discharge from being obstructed.
そして、電極はその下端乃至全長の約半分が廃
棄物投入口から炉本体内に投入された廃棄物によ
つて、埋没され、電極に通電することによつて、
アーク熱が発生し、投入された廃棄物は遂次溶融
して、前記出滓口から炉外に排出され、水砕槽に
て冷却されて細砂状に破砕固化される。 Then, the lower end or about half of the entire length of the electrode is buried in the waste thrown into the furnace main body from the waste inlet, and by energizing the electrode,
Arc heat is generated, and the input waste is sequentially melted and discharged from the furnace through the slag outlet, cooled in a water crushing tank, and crushed and solidified into fine sand.
[発明が解決しようとする問題点]
サブマージドアーク加熱炉による溶融処理は、
前記のとおり、電極下端乃至全長の約半分が処理
されるべき廃棄物に埋没して行なわれるが、廃棄
物の加熱溶融が進むにつれて、炉内における溶融
物の溶融面レベルが上昇し、出滓口に設けられて
いる堰レンガのU字型切欠溝から炉外にオーバー
フローし、連続して出滓される。[Problems to be solved by the invention] The melting process using a submerged arc heating furnace is
As mentioned above, the lower end of the electrode or about half of its total length is buried in the waste to be processed, but as the waste is heated and melted, the level of the melted surface of the molten material in the furnace rises, causing the slag to come out. The slag overflows out of the furnace through the U-shaped notch groove of the weir brick provided at the mouth and is continuously discharged.
ところが、溶融処理操作中、緊急事態例えば落
雷、断線事故等による全停電があつた場合は、主
電極、補助電極への送電は勿論、水砕槽に付帯す
る水砕水送給ポンプも稼働を停止する。この場合
溶融物は、前記堰レンガのU字型切欠溝のレベル
以下になるまではオーバーフローし、炉外に排出
され続ける。すなわち、出滓は即停止されない。
従つて、水砕槽中の貯留水のみでは、冷却効果が
不足し、場合によつては、水蒸気爆発を引き起す
恐れがあり、また水砕槽底部に大量に固化し、そ
の取り出しに難渋するといつた事態が起りかねな
い。これを回避するために、大容量の水砕槽を設
置すればよいが、設備コストならびに配置スペー
ス的にみて、必ずしも有利とはいえない。 However, in the event of a total power outage due to an emergency such as a lightning strike or disconnection accident during the melting process, not only will power be transmitted to the main electrode and auxiliary electrode, but the granulated water supply pump attached to the granulated water tank will not be able to operate. Stop. In this case, the melt continues to overflow and be discharged out of the furnace until it reaches below the level of the U-shaped notch of the weir brick. That is, the slag is not immediately stopped.
Therefore, if only the water stored in the granulation tank is used, the cooling effect will be insufficient, and in some cases, there is a risk of causing a steam explosion.Also, if a large amount of water solidifies at the bottom of the granulation tank, it will be difficult to remove it. Something bad could happen. In order to avoid this, a large-capacity water granulation tank may be installed, but this is not necessarily advantageous in terms of equipment cost and installation space.
本発明は、このような事態に即刻対処しうる安
全な操業方法を提供することを目的とする。 An object of the present invention is to provide a safe operating method that can immediately deal with such a situation.
[問題点を解決するための手段]
本発明は上記緊急事態発生の際に、炉出滓口に
おいて、溶融物を固化させ、溶融物がオーバーフ
ローするのを堰止め、出滓を即時に停止させるも
のである。しかして、その要旨とするところは、
廃棄物溶融処理炉における溶融物の出滓を急速停
止するに当り、溶融物と同等またはそれ以上の比
重を有する冷却材を出滓口手前に散布することを
特徴とる廃棄物溶融処理炉における溶融物の急速
出滓停止方法に存する。[Means for Solving the Problems] The present invention solidifies the molten material at the furnace slag outlet, dams the melt from overflowing, and immediately stops the slag extraction when the above-mentioned emergency situation occurs. It is something. However, the gist of it is that
Melting in a waste melting furnace characterized by spraying a coolant having a specific gravity equal to or higher than that of the molten material in front of the slag outlet when rapidly stopping the slag output in the waste melting furnace. It consists in a method for rapidly stopping the slag discharge.
以下本発明の図面に基いて説明する。 The present invention will be explained below based on the drawings.
第1図は、本発明方法の適用される溶融処理炉
の1つに挙げられるサブマージドアーク炉の概略
側面図であり、1はカーボン、マグネシア、アル
ミナ等の1種または、複数を含有した耐火材料で
構築された炉本体である。炉本体1の上面は炉蓋
2で蔽われている。炉蓋2は複数の主電極3が貫
通し、また、焼却灰投入口4、排ガスダクト5が
設けられる。炉本体1の下方には、出滓口6が設
けられており、該出滓口6には第2図の拡大概略
側面図、および同図の矢視図である第3図に示す
ように、U字型の切欠溝8を備えた耐火堰レンガ
7が設けられており炉本体1内で形成された溶融
物がここからオーバーフローして炉外へ出滓され
る。そして、炉本体1から出滓口6に至るまでの
間の溶融物通路は樋状に構築され、通常の出滓中
に溶融物がここで固化するのを防止するための補
助加熱電極9、溶融開始材貯蔵ホツパー11から
該開始材10を投入するための溶融開始材投入口
12が設けられる。さらに、緊急時に、冷却材貯
蔵ホツパー32から該冷却材14を散布するため
の冷却材投入口15も設けられ、冷却材投入口1
5と冷却材貯蔵ホツパー14とを連結する配管途
中には、冷却材14投入量を調節する開閉コツク
13aが設けられる。以上の冷却材投入口15、
溶融促進材投入口12、補助加熱電極9はいずれ
も出滓口蓋16に配置されるものである。出滓口
6の直下には、出滓される溶融物を受け入れて、
これを急冷し、細粒固化させるための水17を満
した水砕槽18が配置される。 FIG. 1 is a schematic side view of a submerged arc furnace, which is one of the melting furnaces to which the method of the present invention is applied. The furnace body is constructed of materials. The upper surface of the furnace body 1 is covered with a furnace lid 2. A plurality of main electrodes 3 pass through the furnace lid 2, and an incineration ash inlet 4 and an exhaust gas duct 5 are provided. A slag outlet 6 is provided below the furnace body 1, as shown in the enlarged schematic side view in FIG. 2 and in FIG. , a refractory weir brick 7 having a U-shaped cutout groove 8 is provided, through which the molten material formed in the furnace body 1 overflows and slags out of the furnace. The molten material passage from the furnace body 1 to the slag outlet 6 is constructed in the form of a gutter, and an auxiliary heating electrode 9 is provided to prevent the molten material from solidifying here during normal slag tapping. A molten initiator inlet 12 is provided for charging the initiator 10 from the molten initiator storage hopper 11 . Furthermore, a coolant inlet 15 is also provided for dispersing the coolant 14 from the coolant storage hopper 32 in an emergency.
5 and the coolant storage hopper 14, an opening/closing pot 13a for adjusting the amount of coolant 14 input is provided. The above coolant input port 15,
Both the melting accelerator inlet 12 and the auxiliary heating electrode 9 are arranged in the slag outlet cover 16. Immediately below the slag outlet 6, there is a space for receiving the molten material to be slag discharged,
A water pulverization tank 18 filled with water 17 is arranged to rapidly cool the water and solidify it into fine particles.
尚、炉本体1の底面全面には耐火性材料よりな
るキヤスタブル1Aで内張りしてあり、該キヤス
タブル1Aは出滓口6近傍では、溶融物の排出が
容易なように樋状に構築してある。 The entire bottom surface of the furnace body 1 is lined with a castable 1A made of a refractory material, and the castable 1A is constructed in the form of a gutter near the slag outlet 6 to facilitate the discharge of the melt. .
この炉は、一般に銑鉄、フエロアロイ、銅、亜
鉛、錫等の精練や、カーバイド、燐、溶性燐肥等
の化成品の製造に用いられるものを改良したもの
で、主電極3から電流を導入し、炉内に挿入され
た被溶融物、または、溶融物との間にアークを発
生させながら廃棄物を溶融処理する溶融処理炉で
ある。 This furnace is an improved version of the furnace generally used for refining pig iron, ferroalloy, copper, zinc, tin, etc., and for manufacturing chemical products such as carbide, phosphorus, and soluble phosphorous fertilizer. This is a melting furnace that melts waste while generating an arc between the object to be melted or the molten material inserted into the furnace.
上記炉の操作法は、まず焼却物としての焼却灰
aを焼却灰投入口4より均一な厚みとなるように
順次投入して、これを溶融処理していく。この処
理により、焼却灰aからはメタル分を主体とする
溶融金属層bと無機質成分を主体とする溶融スラ
グ層cの2層が形成され、炉底に溶融金属層b、
その上に、溶融スラグ層c、さらにその上に、末
溶融の焼却灰aが積層される。 The method of operating the furnace is to first sequentially charge incinerated ash a as the incinerated material from the incinerated ash input port 4 so as to have a uniform thickness, and then melt the incinerated ash a. Through this treatment, two layers are formed from the incineration ash a: a molten metal layer b mainly composed of metal components and a molten slag layer c mainly composed of inorganic components, and the molten metal layer b,
On top of that, a molten slag layer c is layered, and further on top of that, a partially molten incineration ash a is layered.
炉本体1内に形成された溶融物(溶融スラグc
層と溶融金属b層)は、1350〜1550℃の高温を維
持するが、焼却灰aの継続装入により、その嵩が
増加すると、排出口6の堰レンガ7のU字型切欠
溝8からオーバーフローし、流下物dとして、水
砕槽18に落下する。 The molten material (molten slag c) formed in the furnace body 1
The molten metal layer B) maintains a high temperature of 1,350 to 1,550°C, but when its volume increases due to continuous charging of incinerated ash a, it flows from the U-shaped notch groove 8 of the weir brick 7 of the discharge port 6. It overflows and falls into the granulation tank 18 as falling material d.
本発明は上記溶融処理中に停電などの緊急事態
が発生して、溶融物が、炉から排出され、水砕槽
中に落下するのを即時に停止させる必要を生じた
場合の緊急処置法として、炉本体内の排出口手前
に、冷却材を散布し、該溶融物を出滓口で固化さ
せることを特徴とするものである。 The present invention is an emergency treatment method when an emergency situation such as a power outage occurs during the melting process and it is necessary to immediately stop the melt from being discharged from the furnace and falling into the granulation tank. This method is characterized in that a coolant is sprinkled in front of the outlet in the furnace body, and the molten material is solidified at the slag outlet.
冷却材の散布は、前記出滓口6に至るまでの間
に樋状に構築された通路を流れつつある溶融物に
対して起われる。この場合停電の電気的信号を受
けた制御装置(図示せず)から、冷却材貯蔵ホツ
パー13下部に設けられている開閉コツク13a
に対し、開指令を発するような制御機構を設ける
のがよい。 Spreading of the coolant occurs on the melt flowing through the channel constructed in the shape of a gutter before reaching the slag outlet 6. In this case, from a control device (not shown) that receives an electric signal of a power outage, a switch 13a provided at the bottom of the coolant storage hopper 13
It is preferable to provide a control mechanism that issues an opening command.
冷却材の種類としては、例えば鋼球シヨツトブ
ラスト、磁選別シヨツトブラウト、屑シヨツトブ
ラスト、ソフトブラスト等で、熱伝導熱容量がよ
く且つ熱容量の大きいものが挙げられる。 Examples of the type of coolant include those having good thermal conductivity and large heat capacity, such as steel ball shot blast, magnetic separation shot blast, scrap shot blast, and soft blast.
また、冷却材は、炉本体内で形成される溶融物
と同等またはそれよりも大きな比重のものを選定
することが必要である。即ち、溶融物の比重は、
通常、無機成分を主体とする溶融スラグが約2.6
で、これに溶融金属が混在した場合、約3である
ので、これよりも比重の大きな嵩比重4以上、真
比重7.8以上のものが好ましい。このような比重
を有する冷却材を選定することによつて、緊急時
に炉本体内から出滓口6へ流れる前記溶融物に対
し散布した場合、冷却材表面に浮遊することなく
溶融物中に一層よく浸透し、出滓口6近傍におけ
る溶融物の固化を促進させる。 Further, it is necessary to select a coolant having a specific gravity equal to or greater than that of the molten material formed within the furnace body. That is, the specific gravity of the melt is
Usually, molten slag mainly composed of inorganic components is about 2.6
When molten metal is mixed therein, the specific gravity is about 3, so it is preferable to use a material with a bulk specific gravity of 4 or more and a true specific gravity of 7.8 or more. By selecting a coolant with such a specific gravity, when spraying the molten material flowing from the furnace main body to the slag outlet 6 in an emergency, the coolant will not float on the surface of the coolant and will be dispersed further into the molten material. It penetrates well and promotes solidification of the molten material near the slag outlet 6.
さらに、本発明方法において用いられる冷却材
は0.5〜5mmの範囲の粒径を有することが好まし
い。一般に廃棄物のうち、例えば都市ゴミ焼却灰
は塩基度(CaO/SiO2以下同じ)が0.6以下、下
水汚泥焼却灰や皮革汚泥焼却肺は1.0以上のもの
が多い。したがつて、溶融物とした場合の粘度も
異なる。例えば都市ゴミ焼却灰からの溶融物は粘
度が50〜80Pa・S、であるのに対し、下水汚泥
焼却灰や皮革汚泥焼却灰の粘度は5〜20Pa・S
と前者に較べ1/4〜1/10と小さい。そこで、本発
明方法では、用いられる冷却材は、廃棄物の種類
によつて変動する溶融物の粘性に抵抗してこれに
よく浸透するサイズの上記粒径ものを上記範囲で
選択することが好ましい。即ち、例えば、都市ゴ
ミ焼却灰のように、塩基度の値が小さく、粘度の
高い溶融物に対しては、相対的に粒径の小さい例
えば0.5〜3mmの冷却材を多量に用い、下水汚泥
焼却灰や皮革汚泥焼却灰のように、塩基度の値が
大きく、粘度の低い溶融物に対しては相対的に粒
径の大きい例えば1〜5mmの冷却材が少量用いら
れる。このように、溶融物の有する粘度に応じて
粒径の異なる冷却材を適用することにより、炉本
体内で形成された溶融物が出滓口6に至るまでの
樋状通路において、粘性に対する抵抗もなく溶融
物の流れと、よくなじみ、該溶融物を冷却固化し
て急速な出滓停止の効果が発揮される。 Furthermore, it is preferred that the coolant used in the method of the invention has a particle size in the range 0.5 to 5 mm. In general, among wastes, for example, municipal garbage incineration ash has a basicity (same as CaO/SiO 2 and below) of 0.6 or less, and sewage sludge incineration ash and leather sludge incineration lung have a basicity of 1.0 or more. Therefore, the viscosity of the melted material also differs. For example, the viscosity of the molten material from municipal waste incineration ash is 50 to 80 Pa・S, whereas the viscosity of sewage sludge incineration ash and leather sludge incineration ash is 5 to 20 Pa・S.
This is 1/4 to 1/10 smaller than the former. Therefore, in the method of the present invention, it is preferable that the particle size of the coolant used is selected within the above range so that it can resist the viscosity of the melt and penetrate well into it, which varies depending on the type of waste. . That is, for example, for molten material with a low basicity value and high viscosity, such as municipal waste incineration ash, a large amount of coolant with a relatively small particle size, for example, 0.5 to 3 mm, is used, and sewage sludge is For melts with high basicity values and low viscosity, such as incineration ash and leather sludge incineration ash, a small amount of coolant having a relatively large particle size, for example, 1 to 5 mm, is used. In this way, by applying coolants with different particle sizes depending on the viscosity of the molten material, the molten material formed in the furnace body can resist viscosity in the trough-like passage leading to the slag outlet 6. It blends well with the flow of the molten material, cools and solidifies the molten material, and exhibits the effect of rapidly stopping slag extraction.
また、冷却材の散布量は、溶融炉の容量、溶融
物の排出速度、排出量、排出温度等によつて異る
も通常30Kg以上である。 Further, the amount of coolant sprayed is usually 30 kg or more, although it varies depending on the capacity of the melting furnace, the discharge speed of the melt, the discharge amount, the discharge temperature, etc.
[作用]
緊急時に、出滓口手前に冷却材を散布すること
により、炉外にオーバーフローする溶融物がそこ
で固化し、堰止められたヘツドによる流下出滓が
即時に停止される。従つて水砕槽への溶融物排出
が即中断されるので、水砕水送給ポンプの稼働停
止による水補給がストツプしても、それによる水
蒸気爆発、溶融物の過剰排出による水砕槽内での
固化等不測の事態が回避される。また、出滓口近
傍における固化範囲が小さいので、補助加熱電極
による再溶融操業再開が容易である。[Operation] In an emergency, by spraying a coolant in front of the slag outlet, the molten material overflowing to the outside of the furnace will solidify there, and the flow of slag from the dammed head will be immediately stopped. Therefore, the discharge of molten material to the fracking tank is immediately interrupted, so even if water supply is stopped due to the granulated water supply pump stopping operation, there may be a steam explosion due to this, or the inside of the fracking tank may be damaged due to excessive discharge of molten material. This prevents unforeseen situations such as solidification. Furthermore, since the solidified area near the slag outlet is small, it is easy to restart the remelting operation using the auxiliary heating electrode.
[実施例]
炉床面積が3.3M3の第1図に示すような廃棄物
溶融処理炉(サブマージドアーク炉)に都市ゴミ
焼却灰(含水率10%)を約1ton/hrの速度で溶融
処理したところ、約800Kg/hrの割合で、溶融物
(溶融スラグと溶融金属)が生成した。この溶融
物中の溶融金属は全体の5〜10%で大部分が鉄分
である。又、無機質成分主体の溶融スラグの比重
は約2.6で、溶融金属を含めた溶融物全体の比重
は、約3であつた。[Example] Municipal waste incineration ash (moisture content 10%) was melted at a rate of approximately 1 ton/hr in a waste melting furnace (submerged arc furnace) as shown in Figure 1 with a hearth area of 3.3M3 . Upon treatment, molten material (molten slag and molten metal) was produced at a rate of approximately 800 kg/hr. The molten metal in this melt is 5 to 10% of the total, mostly iron. Further, the specific gravity of the molten slag mainly composed of inorganic components was about 2.6, and the specific gravity of the entire molten material including the molten metal was about 3.
停電による緊急時を想定して、「都市ゴミ焼却
灰の投入停止」、「電極に対する電力投入停止」を
行つたところ、停止後6〜10分の間に、出滓口か
ら80〜150Kgの溶融物が流出して出滓はとまつた。 Assuming an emergency due to a power outage, we stopped the input of municipal waste incineration ash and the power supply to the electrodes, and within 6 to 10 minutes after the shutdown, 80 to 150 kg of melted from the slag outlet. Materials flowed out and the slag stopped.
次に、「電極に対する電力投入」と「都市ゴミ
焼却灰の投入」を再開し、通常の溶融処理運転に
戻したのち、再度、前記「停止」を行い、直ちに
冷却材として粒径が1〜2mm、嵩比重4、真比重
7.8の鋼球シヨツトブラスト約30Kgを出滓口近傍
の樋上に散布した。その結果、約30秒後に出滓口
からの溶融物の流出が止つた。 Next, we restarted the "power supply to the electrodes" and the "injection of municipal waste incineration ash" to return to the normal melting process operation, and then "stopped" the process again, and immediately used the coolant as a particle size of 1 to 1. 2mm, bulk specific gravity 4, true specific gravity
Approximately 30 kg of 7.8 steel ball shot blast was sprayed onto the gutter near the slag outlet. As a result, the flow of molten material from the slag outlet stopped after about 30 seconds.
尚、比較例として、前記実施例における鋼球シ
ヨツトブラストの代りに、嵩比重1.1〜1.5、真比
重2.7の水砕スラグ約50Kgを散布したが溶融物の
流れの中に混入はしたが、溶融物の出滓口からの
流出をすぐには停止させることができなかつた。 As a comparative example, approximately 50 kg of granulated slag with a bulk specific gravity of 1.1 to 1.5 and a true specific gravity of 2.7 was sprayed instead of the steel ball shot blasting in the previous example, but although it mixed into the flow of the molten material, It was not possible to immediately stop the flow of the melt from the slag opening.
[効果]
本発明は以上述べたように、溶融処理炉の出滓
口手前に特定範囲の物性を持つ冷却材を緊急事態
発生時に散布して、溶融物の出滓を急停止させる
ことにより水砕槽における水蒸気爆発や、溶融物
の大塊固化を回避し、もつて安全操業と操業の効
率化をはかるもので、廃棄物処理分野に大きく寄
与することができる。[Effects] As described above, the present invention sprays a coolant having physical properties in a specific range in front of the slag outlet of a melting processing furnace in the event of an emergency to suddenly stop the flow of molten material. This system avoids steam explosions and large solidification of molten material in the crushing tank, thereby improving safe operation and efficiency, and can greatly contribute to the waste treatment field.
図面は本発明方法の適用される溶融処理炉の1
例を示すもので、第1図は概略側面図、第2図は
第1図における出滓口周辺の部分拡大図、第3図
は第2図の矢視図である。
1……炉本体、2……炉蓋、3……主電極、4
……焼却灰投入口、5……排ガスダクト、6……
出滓口、7……耐火堰レンガ、9……補助加熱電
極、13……冷却材貯蔵ホツパー、14……冷却
材、15……冷却材投入口、18……水砕槽。
The drawing shows one of the melting furnaces to which the method of the present invention is applied.
To illustrate an example, FIG. 1 is a schematic side view, FIG. 2 is a partially enlarged view of the vicinity of the slag outlet in FIG. 1, and FIG. 3 is a view taken in the direction of the arrows in FIG. 2. 1... Furnace body, 2... Furnace lid, 3... Main electrode, 4
...Incineration ash input port, 5...Exhaust gas duct, 6...
Slag outlet, 7... Fireproof weir brick, 9... Auxiliary heating electrode, 13... Coolant storage hopper, 14... Coolant, 15... Coolant inlet, 18... Water fracking tank.
Claims (1)
速停止するに当り、溶融物と同等またはそれ以上
の比重を有する冷却材を出滓口手前に散布するこ
とを特徴とする廃棄物溶融処理炉における出滓停
止方法。 2 廃棄物が、都市ゴミ焼却灰、下水汚泥焼却灰
または皮革処理汚泥焼却灰のいずれかである特許
請求の範囲第1項記載の廃棄物溶融処理炉におけ
る出滓停止方法。 3 冷却材が、0.5〜5mm径の鋼球シヨツトブラ
ストである特許請求の範囲第1項記載の廃棄物溶
融処理炉における出滓停止方法。 4 廃棄物が都市ゴミ焼却灰であり、冷却材が
0.5〜3mm径の鋼球シヨツトブラストである特許
請求の範囲第1項記載の溶融処理炉における出滓
停止方法。 5 廃棄物が下水汚泥焼却灰又は皮革処理汚泥焼
却灰であり、冷却材が1〜5mm径の鋼球シヨツト
ブラストである特許請求の範囲第1項記載の溶融
処理炉における出滓停止方法。[Claims] 1. In rapidly stopping the molten material slag in a waste melting processing furnace, a coolant having a specific gravity equal to or higher than that of the molten material is sprayed in front of the slag outlet. A method for stopping slag production in a waste melting processing furnace. 2. The method for stopping slag production in a waste melting processing furnace according to claim 1, wherein the waste is any one of municipal garbage incineration ash, sewage sludge incineration ash, or leather processing sludge incineration ash. 3. The method for stopping slag extraction in a waste melting processing furnace according to claim 1, wherein the coolant is shot blasting of steel balls having a diameter of 0.5 to 5 mm. 4 The waste is municipal garbage incineration ash, and the coolant is
A method for stopping slag in a melting processing furnace according to claim 1, which is shot blasting of steel balls having a diameter of 0.5 to 3 mm. 5. The method for stopping slag in a melting processing furnace according to claim 1, wherein the waste is sewage sludge incineration ash or leather processing sludge incineration ash, and the coolant is steel ball shot blasting with a diameter of 1 to 5 mm.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP61034765A JPS62193689A (en) | 1986-02-19 | 1986-02-19 | Method for stopping slag discharge for melting treatment furnace |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP61034765A JPS62193689A (en) | 1986-02-19 | 1986-02-19 | Method for stopping slag discharge for melting treatment furnace |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS62193689A JPS62193689A (en) | 1987-08-25 |
| JPH0570519B2 true JPH0570519B2 (en) | 1993-10-05 |
Family
ID=12423401
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP61034765A Granted JPS62193689A (en) | 1986-02-19 | 1986-02-19 | Method for stopping slag discharge for melting treatment furnace |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS62193689A (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0428902U (en) * | 1990-06-25 | 1992-03-09 |
-
1986
- 1986-02-19 JP JP61034765A patent/JPS62193689A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS62193689A (en) | 1987-08-25 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| US4725307A (en) | Method of treating dust and sludge simultaneously with steel slag | |
| EP2797082B1 (en) | Method for processing solid radioactive waste | |
| KR100227003B1 (en) | Method for manufacturing artificial aggregate for concrete from incineration ash and its manufacturing apparatus | |
| US20090229406A1 (en) | Slag control in a channel induction furnace | |
| EP4062117B1 (en) | Improved plasma induced fuming furnace | |
| JPH0570519B2 (en) | ||
| WO2009114159A2 (en) | Feed material compostion and handling in a channel induction furnace | |
| WO1997012069A1 (en) | Material for use in manufacturing ingots for steel smelting treatment and a method of obtaining said material, ingot for steel smelting treatment, method and machine for obtaining said ingot | |
| JP7143029B2 (en) | Manufacturing method of clearance metal | |
| JPH09301750A (en) | Method and apparatus for producing artificial gravel from incinerated ash molten slag | |
| JP3871172B2 (en) | Molybdenum electrode body used in the former furnace attached to the electric melting furnace | |
| JP2958605B2 (en) | Melt treatment method for fibrous waste | |
| JP3809039B2 (en) | Method of granulating molten metal in melting furnace | |
| JPS62201686A (en) | Method for exchanging cinder notch black gate brick | |
| JP3508072B2 (en) | Method and apparatus for producing massive artificial aggregate for concrete | |
| CN220202006U (en) | Equipment for smelting reduction of copper-containing sludge based on oxygen-enriched top-blowing process | |
| JP2000039118A (en) | Side charge type dc electric melting furnace for reduction molten slag | |
| JPH0875136A (en) | Incinerated ash melting method and device therefor | |
| JPS62162815A (en) | Discharge method for molten slag | |
| JPS60215704A (en) | Treatment of steel making slag | |
| JPH0237282A (en) | Method of removing molten iron from rockwool electric furnace | |
| US902047A (en) | Liquation-furnace. | |
| JPS62172107A (en) | Method and device of discharging residue in waste melting disposing furnace | |
| JPS62171949A (en) | Water granulation equipment for waste molten slag | |
| JPS6287443A (en) | Treatment of steel slag |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| LAPS | Cancellation because of no payment of annual fees |