JPH01288387A - Melting furnace for industrial waste - Google Patents

Melting furnace for industrial waste

Info

Publication number
JPH01288387A
JPH01288387A JP63117562A JP11756288A JPH01288387A JP H01288387 A JPH01288387 A JP H01288387A JP 63117562 A JP63117562 A JP 63117562A JP 11756288 A JP11756288 A JP 11756288A JP H01288387 A JPH01288387 A JP H01288387A
Authority
JP
Japan
Prior art keywords
ash
furnace
melting
melting furnace
furnace wall
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.)
Pending
Application number
JP63117562A
Other languages
Japanese (ja)
Inventor
Tomio Suzuki
富雄 鈴木
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.)
Kobe Steel Ltd
Original Assignee
Kobe Steel 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 Kobe Steel Ltd filed Critical Kobe Steel Ltd
Priority to JP63117562A priority Critical patent/JPH01288387A/en
Publication of JPH01288387A publication Critical patent/JPH01288387A/en
Pending legal-status Critical Current

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  • Gasification And Melting Of Waste (AREA)
  • Processing Of Solid Wastes (AREA)
  • Ceramic Products (AREA)
  • Furnace Housings, Linings, Walls, And Ceilings (AREA)

Abstract

PURPOSE:To extend the life of a melting furnace by constituting the furnace wall of the melting furnace of refractory containing a fine molten slag powder of a material to be melted. CONSTITUTION:Coke oven gas is blown in a melting furnace from a stabilizing burner 10 along with combustion air preheated to predetermined temp. to be burnt and the furnace wall 17 of said furnace 2 is held to temp. so as to become higher by 50-100 deg.C than the melting temp. of ash. Subsequently, ash is transported by a predetermined amount by an ash supply device 3 in this state so as to be carried by an air stream. The ash is uniformly mixed with combustion air in an ejector 13 and a solid-air two-phase steam wherein combustion air is mixed with the ash is formed into a strong revolving stream by the revolving blade of the burner 10 to be uniformly injected in a combustion chamber A. The ash is burnt rapidly while collides with the furnace wall 17 by centrifugal force to fall in a molten slag pot 9a and received in a cooling and solidifying device 15 from a cinder notch 9b. By this method, the life of the furnace wall can be extended to a large extent.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、石炭を焼却した石炭灰、都市ゴミ。[Detailed description of the invention] [Industrial application field] The present invention uses coal ash produced by incinerating coal and municipal waste.

下水汚泥スラフジ、一般廃棄物等の産業廃棄物。Industrial waste such as sewage sludge, general waste, etc.

または該産業廃棄物を焼却した焼却灰を溶融処理する溶
融炉に関し、特に溶融炉の炉壁の寿命を延長できるよう
にした構造に関する。
The present invention also relates to a melting furnace for melting incineration ash obtained by incinerating the industrial waste, and particularly relates to a structure capable of extending the life of the furnace wall of the melting furnace.

〔従来の技術〕[Conventional technology]

都市ゴミ、下水汚泥スラッジ、一般廃棄物等の産業廃棄
物を処分する場合は、そのまま埋め立てたり、また上記
産業廃棄物を焼却して焼却灰とした後、埋め立てたりし
ている。また、石炭を燃料とするボイラ、キルン、工業
炉等から排出される石炭灰もその大部分は埋め立て処分
されている。
When disposing of industrial waste such as municipal garbage, sewage sludge, and general waste, the industrial waste is either directly buried in a landfill, or the industrial waste is incinerated to form incineration ash and then buried in a landfill. Furthermore, most of the coal ash discharged from boilers, kilns, industrial furnaces, etc. that use coal as fuel is disposed of in landfills.

しかし、近年、上記産業廃棄物の排出量が年々増大して
いることから、埋め立て地の確保が困難になってきてお
り、しかもこれらの埋め立てられた廃棄物からの有害物
質の流出による二次公害が懸念されており、この埋め立
て処分は困難になっている。
However, in recent years, as the amount of industrial waste mentioned above has been increasing year by year, it has become difficult to secure land for landfill, and secondary pollution is occurring due to the outflow of hazardous substances from these landfilled wastes. This is a concern, making landfill disposal difficult.

そこで、上記焼却灰1石炭灰(以下、灰と称す)、及び
下水汚泥スラッジ等の産業廃棄物を溶融スラグ化した後
、冷却固化させる溶融処理方法が注目されている。この
溶融処理することにより上記産業廃棄物の処分量の減容
化、有害物質の固定化ができ、埋め立てに利用できると
ともに、上記溶融スラグを土木、建築材料等に有効利用
できる。
Therefore, attention has been paid to a melt processing method in which the above-mentioned incineration ash 1 coal ash (hereinafter referred to as ash) and industrial waste such as sewage sludge sludge are melted into slag and then cooled and solidified. By this melting treatment, the volume of the industrial waste to be disposed of can be reduced, harmful substances can be immobilized, it can be used for landfill, and the molten slag can be effectively used for civil engineering, building materials, etc.

上記産業廃棄物を溶融する場合、そのほとんどはコーク
ス、電気、各種燃料、マイクロ波等の熱源を利用した高
温溶融が採用されており、この被溶融物を高温に保持す
る溶融炉が不可欠である。
When melting the industrial waste mentioned above, most of the time, high-temperature melting using heat sources such as coke, electricity, various fuels, and microwaves is used, and a melting furnace that maintains the material to be melted at a high temperature is essential. .

この溶融炉は、炉内を高温に保持し、かつ熱損失を最小
限にする必要があることから、炉殻を構成する鉄板の内
側に耐火物が施工されている。
In this melting furnace, it is necessary to maintain the inside of the furnace at a high temperature and minimize heat loss, so a refractory is installed inside the iron plate that makes up the furnace shell.

ところで、上記溶融炉においては、被溶融物の中にさま
ざまな物質が含まれていることから、これらの物質が高
温条件下で上記耐火物と反応して侵食し易いという問題
がある。その結果、溶融炉の操業をしばしば休止して炉
壁を補修したり、あるいは予備の溶融炉と切り替えて運
転したりする必要があり、補修コスト、設備費が上昇す
る。従って、上記耐火物の寿命の延長は非常に重要な課
題となっている。
By the way, in the above-mentioned melting furnace, since various substances are contained in the material to be melted, there is a problem that these substances tend to react with the above-mentioned refractory and corrode it under high-temperature conditions. As a result, it is often necessary to stop the operation of the melting furnace to repair the furnace wall, or to switch to operation with a spare melting furnace, which increases repair costs and equipment costs. Therefore, extending the life of the refractories is a very important issue.

従来、上記溶融炉の炉壁には比較的寿命の長い耐火物が
、一般に市販されている各種の耐火物の中から選択して
採用されている。
Conventionally, a refractory with a relatively long life has been selected from various commercially available refractories for the walls of the melting furnace.

〔発明が解決しようとする問題点〕[Problem that the invention seeks to solve]

しかしながら、上記従来の耐火物の中から最適のものを
選択する方法では、侵食速度を充分に抑制することは困
難であり、炉壁の寿命はあまり延長できないという問題
点がある。
However, with the conventional method of selecting the optimal refractory from among the refractories described above, it is difficult to sufficiently suppress the erosion rate, and there is a problem that the life of the furnace wall cannot be extended much.

ここで、本発明者は、上記耐火物の寿命延長を実現する
ために、一般に市販されているさまざまな耐火物を使用
して各被溶融物の熔融試験を行ったところ、いずれの耐
火物においても侵食を抑制することは非常に難しいとい
う結論を得た。これは、都市ゴミ、下水汚泥などは、そ
れぞれ発生場所によって成分が異なり、また同一処理場
に持ち込まれる都市ゴミ等であっても、その処理日によ
って成分変動があることから、これらの条件に合わせて
耐火物を選定するのは困難である。
Here, in order to extend the life of the above-mentioned refractories, the inventor conducted a melting test of each object to be melted using various refractories that are generally commercially available. It was also concluded that it is very difficult to control erosion. This is because the composition of municipal waste, sewage sludge, etc. differs depending on where it is generated, and even if municipal waste is brought to the same treatment plant, the composition may vary depending on the date of treatment. Therefore, it is difficult to select refractories.

本発明は上記従来の状況に鑑みてなされたもので、被溶
融物の成分変動が生じても耐火物の侵食速度を抑制して
炉壁の寿命を延長でき、補修コスト、設備費を低減でき
る産業廃棄物用溶融炉を提供することを目的としている
The present invention was made in view of the above-mentioned conventional situation, and even if the composition of the material to be melted changes, it is possible to suppress the erosion rate of the refractory, extend the life of the furnace wall, and reduce repair costs and equipment costs. The purpose is to provide melting furnaces for industrial waste.

〔問題点を解決するための手段〕[Means for solving problems]

本件発明者は、上記耐火物の寿命延長を実現するために
鋭意検討を重ねた結果、被溶融物の各成分変動に対応で
きるよう耐火材の各種成分を細かく調整するよりも、被
溶融物の成分変動に対して鈍感な耐火物が望ましいと考
えた。そして被溶融物同士は反応しにくいという着想か
ら、溶融炉の内壁を被溶融物自身で保護してやれば、最
も反応を起こりにくくできるとともに、成分変動に対し
ても鈍感な耐火物が得られ、しかも上記耐火材の各種成
分を細かく調整した耐火物を採用する場合に比べ、技術
的、コストの点からも最良であることに想到し、本発明
を成したものである。
As a result of extensive studies in order to extend the life of the refractory, the inventor of the present invention found that rather than finely adjusting the various components of the refractory material in order to respond to the fluctuations in each component of the refractory material, We thought it would be desirable to use a refractory that is insensitive to changes in composition. Based on the idea that materials to be melted are unlikely to react with each other, if the inner wall of the melting furnace is protected by the materials to be melted, it will be possible to minimize the possibility of reactions occurring, and to obtain a refractory that is insensitive to changes in composition. The present invention was developed based on the idea that this would be the best in terms of technology and cost compared to the case of using a refractory material in which the various components of the refractory material are finely adjusted.

そこで本発明は、産業廃棄物用溶融炉の内壁を、被溶融
物の溶融スラグ微粉末、又は被溶融物の灰を少なくとも
重量比で50%以上含む耐火物で構成したことを特徴と
している。
Therefore, the present invention is characterized in that the inner wall of the industrial waste melting furnace is made of a refractory material containing at least 50% or more by weight of pulverized molten slag of the material to be melted or ash of the material to be melted.

ここで、上記被溶融物とは、都市ゴミ、下水汚泥、一般
廃棄物及びこれらを焼却した焼却灰、あるいは石炭を焼
却した石炭灰が含まれる。
Here, the material to be melted includes municipal garbage, sewage sludge, general waste, incineration ash obtained by incinerating these, or coal ash obtained by incinerating coal.

また、上記含有量を50%以上としたのは、これ以下で
あると侵食速度の抑制効果があまり得られないからであ
る。これは、耐火物の補修頻度を低減する上で侵食速度
を月間51以下に抑制する必要があることから割り出さ
れたものである。さらに、50%を超えて含有量を増や
すほど侵食速度は低下するが、100%にするとバイン
ダー効果が少なくなって耐火物の強度が低下したり、炉
壁の耐溶融温度が低下したりすることから注意を要する
Further, the reason why the above content is set to 50% or more is because if it is less than this, the effect of suppressing the erosion rate cannot be obtained much. This was determined based on the need to suppress the erosion rate to 51 or less per month in order to reduce the frequency of repair of refractories. Furthermore, as the content increases beyond 50%, the erosion rate decreases, but when the content is increased to 100%, the binder effect decreases and the strength of the refractory decreases, and the melting temperature of the furnace wall decreases. Caution is required.

これらのことを考慮すると60〜90%の範囲にするの
が望ましい。
Taking these things into consideration, it is desirable to set it in the range of 60 to 90%.

〔作用〕 本発明に係る産業廃棄物用溶融炉によれば、溶融炉の炉
壁を構成する耐火物に、被溶融物の熔融スラグ微粉末、
又は灰を50%以上含有させたので、高温溶融時におい
て略同−成分の被溶融物同士が接触することとなり、つ
まり耐火物を侵食する物質に対して自分自身でガードす
るから、反応による侵食を大幅に抑制でき、しかも被溶
融物の成分変動が生じた場合でも反応は鈍感となり、こ
の点からも侵食を抑制できる。その結果、炉壁の寿命を
大幅に延長でき、補修頻度を削減でき、運転コスト、設
備費を低減できる。
[Function] According to the industrial waste melting furnace according to the present invention, the molten slag powder of the object to be melted is added to the refractory constituting the furnace wall of the melting furnace.
Alternatively, since the ash content is 50% or more, melted materials of approximately the same composition come into contact with each other during high-temperature melting, and in other words, they protect themselves against substances that corrode refractories, so corrosion due to reactions is prevented. can be significantly suppressed, and even if a change in the composition of the material to be melted occurs, the reaction becomes insensitive, and from this point of view as well, erosion can be suppressed. As a result, the life of the furnace wall can be significantly extended, the frequency of repairs can be reduced, and operating costs and equipment costs can be reduced.

また、本発明は、市販の耐火物に上記溶融スラグ粉末等
を混在させるだけでよいから、被溶融物の各成分に応じ
て耐火材の各種成分を細かく調整する場合に比べて、技
術的、コスト的に有利である。
In addition, since the present invention only requires mixing the above-mentioned molten slag powder etc. with commercially available refractories, it is technically less expensive than the case where various components of the refractory material are finely adjusted according to each component of the refractory material to be melted. It is advantageous in terms of cost.

〔実施例〕〔Example〕

以下、本発明の実施例を図について説明する。 Embodiments of the present invention will be described below with reference to the drawings.

第1図及び第2図は本発明の一実施例を説明するための
図であり、本実施例は焼却灰9石炭灰の溶融処理炉の例
である。
FIG. 1 and FIG. 2 are diagrams for explaining one embodiment of the present invention, and this embodiment is an example of a furnace for melting incinerated ash and coal ash.

図において、■は焼却灰6石炭灰の溶融処理装置である
。この処理装置lは、垂直縦型の溶融炉2と、該溶融炉
2に貯蔵びん3aに収容された灰を圧縮空気3bにより
気流輸送する供給装置3と、上記溶融炉2に燃焼空気を
供給する燃焼空気供給装置4と、上記溶融炉2からの排
ガスの廃熱を回収し、上記燃焼空気を予熱する熱交換器
5と、該熱交換器5からの低温排ガス中の未処理灰を捕
集する集塵装置6とから構成されている。
In the figure, ■ is an incineration ash 6 coal ash melting processing device. This processing device 1 includes a vertical melting furnace 2, a supply device 3 that pneumatically transports ash stored in a storage bottle 3a to the melting furnace 2 using compressed air 3b, and a supply device 3 that supplies combustion air to the melting furnace 2. a combustion air supply device 4 for recovering the waste heat of the exhaust gas from the melting furnace 2, a heat exchanger 5 for preheating the combustion air, and capturing untreated ash in the low temperature exhaust gas from the heat exchanger 5. It is composed of a dust collector 6 that collects dust.

上記溶融炉2は、燃焼室Aが形成された円筒状の炉本体
7の上端部に燃料流入部8をフランジ接続し、下端部に
スラグ収容部9を接続するとともに、上記炉本体7の下
部に排ガス流出部7aを形成して構成されている。
The melting furnace 2 has a fuel inflow part 8 connected by a flange to the upper end of a cylindrical furnace body 7 in which a combustion chamber A is formed, a slag storage part 9 to the lower end, and a lower part of the furnace body 7. An exhaust gas outflow portion 7a is formed in the exhaust gas outflow portion 7a.

上記燃料流入部8にはバーナタイル8aが形成され、こ
れには助燃バーナ10が装着されている。
A burner tile 8a is formed in the fuel inlet 8, and an auxiliary burner 10 is attached to this.

この助燃バーナ10には、固気二相流供給管11及び燃
料供給管12aが接続されており、該燃料供給管12a
の延長端はコークス炉ガス供給装置12に接続されてい
る。また、上記固気二相流供給管11にはT字管型のエ
ジェクタ13が接続されており、該エジェクタ13には
上記灰供給装置3の灰供給管3c、及び上記熱交換器5
により予熱された燃焼空気を供給する燃焼空気供給管4
bが接続されており、この燃焼空気供給管4bの延長端
は上記熱交換器5を通ってブロア4aに接続されている
。上記エジェクタ13は、気流輸送された灰を予め燃焼
空気中に混合して固気二相流として上記バーナ10に供
給するように構成されており、この固気二相流はバーナ
10の先端部に配設された旋回羽根によって旋回を与え
られて燃焼室A内に噴射されるようになっている。
A solid-gas two-phase flow supply pipe 11 and a fuel supply pipe 12a are connected to this auxiliary combustion burner 10.
The extended end of the coke oven gas supply device 12 is connected to the coke oven gas supply device 12 . Further, a T-tube type ejector 13 is connected to the solid-gas two-phase flow supply pipe 11, and the ejector 13 is connected to the ash supply pipe 3c of the ash supply device 3 and the heat exchanger 5.
Combustion air supply pipe 4 that supplies combustion air preheated by
b is connected, and the extended end of this combustion air supply pipe 4b passes through the heat exchanger 5 and is connected to the blower 4a. The ejector 13 is configured to mix air-transported ash into combustion air in advance and supply it to the burner 10 as a solid-gas two-phase flow. The fuel is injected into the combustion chamber A by being given a swirl by swirling vanes arranged in the combustion chamber A.

また、上記排ガス流出部7aには、熱交換器5の排ガス
導入部5aが接続されており、これの排出部5bには集
塵装置6が接続されている。また、この集塵装置6は誘
引ファン6aを介して煙突14に接続されている。
Furthermore, the exhaust gas introduction section 5a of the heat exchanger 5 is connected to the exhaust gas outflow section 7a, and the dust collector 6 is connected to the discharge section 5b thereof. Further, this dust collector 6 is connected to a chimney 14 via an induction fan 6a.

さらに、上記燃焼室Aの下方にはスラグ収容部りのスラ
グボット9aが位置しており、これには出滓口9bが突
出形成されている。これにより上記ボッ)9a内に捕集
された溶融スラグは出滓口9bから抽出され、冷却同化
装置15に回収される。
Further, a slag bot 9a serving as a slag storage section is located below the combustion chamber A, and a slag outlet 9b is formed protruding from this slag bot 9a. As a result, the molten slag collected in the bowl 9a is extracted from the slag outlet 9b and collected in the cooling assimilation device 15.

上記溶融炉2の炉本体7には、炉殻を構成する鉄皮7b
の最外周に冷却水ジャケット16が形成されており、該
ジャケット16の下部には冷却水流入口16aが、上部
には流出口16bがそれぞれ形成されている。そして、
上記炉本体7の鉄皮7bの内周面には、半径方向の厚さ
が100鶴の炉壁17が形成されている。この炉壁17
は、アルミナセメントの混合粉末に被溶融物の溶融スラ
グ微粉末を重量比で50%以上混在させてなる耐火物を
内張すして構成されている。なお、上記冷却水ジャケッ
ト16は必ずしも必要なものではなく、上記炉壁17を
厚くして非水冷構造にしてもよく、またセルフクーリン
グ構造にしてもよい。
The furnace body 7 of the melting furnace 2 has an iron shell 7b constituting the furnace shell.
A cooling water jacket 16 is formed on the outermost periphery of the cooling water jacket 16, and a cooling water inlet 16a is formed in the lower part of the jacket 16, and an outlet port 16b is formed in the upper part of the jacket 16. and,
A furnace wall 17 having a thickness of 100 mm in the radial direction is formed on the inner circumferential surface of the iron shell 7b of the furnace body 7. This furnace wall 17
The refractory is lined with a refractory made of mixed powder of alumina cement mixed with 50% or more by weight of fine molten slag powder. Note that the cooling water jacket 16 is not necessarily necessary, and the furnace wall 17 may be thickened to have a non-water-cooled structure, or a self-cooling structure may be provided.

次に本実施例の作用効果について説明する。Next, the effects of this embodiment will be explained.

本実施例の溶融処理装置1により灰を溶融固化させる場
合は、コークス炉ガス及び所定温度に予熱された燃焼空
気を助燃バーナlOから溶融炉2内に吹き込んで燃焼さ
せ、この炉壁17が灰の溶融温度より50〜100℃高
くなるように保持する。
When ash is melted and solidified by the melting processing apparatus 1 of this embodiment, coke oven gas and combustion air preheated to a predetermined temperature are blown into the melting furnace 2 from the auxiliary combustion burner IO and burned, so that the furnace wall 17 becomes the ash. The melting temperature is maintained at 50 to 100°C higher than the melting temperature.

例えば、石炭灰の場合は1550℃、下水汚泥焼却灰の
場合は1400℃に保持する。次に、この状態で、灰供
給装置3により所定量づつ気流輸送する。すると上記灰
は、エジェクタ13内で燃焼空気中に均一に混入され、
この燃焼空気と灰とが混合された固気二相流は、バーナ
lOの旋回羽根によって強い旋回流が与えられて燃焼室
A内に均一に噴射される。これにより、上記灰は螺旋を
描き、かつ遠心力により炉壁17に衝突しながら急速燃
焼されることとなり、しかる後溶融スラグ化してスラグ
ポット9a内に落下し、出滓口9bから冷却同化装置1
5に収容される。一方、排ガスは、流出通路7aを通っ
て熱交換器5に進入し、ここで廃熱回収された後、集塵
装置6で排ガス中の未処理灰が捕集され、清浄された後
煙突14から放出される。
For example, coal ash is kept at 1550°C, and sewage sludge incineration ash is kept at 1400°C. Next, in this state, the ash supplying device 3 transports the ash in a predetermined amount at a time. Then, the ash is uniformly mixed into the combustion air in the ejector 13,
This solid-gas two-phase flow in which combustion air and ash are mixed is uniformly injected into the combustion chamber A by being given a strong swirling flow by the swirling vanes of the burner IO. As a result, the ash forms a spiral and rapidly burns while colliding with the furnace wall 17 due to centrifugal force, and then turns into molten slag and falls into the slag pot 9a, and is passed through the slag outlet 9b into the cooling assimilation device. 1
It is accommodated in 5. On the other hand, the exhaust gas enters the heat exchanger 5 through the outflow passage 7a, where waste heat is recovered, and untreated ash in the exhaust gas is collected and purified by the dust collector 6, and then the chimney 14 released from.

このように溶融固化された灰は、処分量の減容化及び有
害物質の固定化ができるから埋め立てに利用できるとと
もに、土木、l!築新材料に利用できる。
Ash that has been melted and solidified in this way can be used in landfills because it can reduce the volume of disposal volume and immobilize harmful substances, and it can also be used in civil engineering, l! Can be used as construction material.

ここで、上記灰を溶融処理する場合、この灰の中にさま
ざまな物質が含まれていることから、従来装置ではこれ
らの物質が炉壁と反応して侵食し易く、また上記灰中の
成分がさまざまな状況によって変動することから、侵食
が速く寿命が短いという問題があった。これに対して、
本実施例では、溶融炉2の炉壁17を、一般に市販され
ているアルミナセメントの混合粉末に溶融スラグ微粉末
を重量比で50%以上混在させた耐火物で構成したので
、セルコーティングが促進されるから、高温溶融時にお
ける反応を防止でき、侵食速度を低減でき、炉壁の寿命
を大幅に延長できる。その結果、補修額度を削減できる
から、運転コスト、設備費を低減できる。
When the ash is melted, the ash contains various substances, and in conventional equipment, these substances tend to react with the furnace wall and erode it, and the components in the ash are easily eroded. The problem is that it erodes quickly and has a short lifespan because it fluctuates depending on various conditions. On the contrary,
In this example, the furnace wall 17 of the melting furnace 2 is made of a refractory material in which 50% or more by weight of fine molten slag powder is mixed with a generally commercially available mixed powder of alumina cement, thereby promoting cell coating. Therefore, reactions during high-temperature melting can be prevented, the erosion rate can be reduced, and the life of the furnace wall can be significantly extended. As a result, the amount of repairs can be reduced, and thus operating costs and equipment costs can be reduced.

また、本実施例によれば、市販のアルミナセメント粉末
に溶融スラグ粉末を混合させるだけでよいから、上述し
たような被溶融物の各成分に応して耐火材の各種成分を
細か(調整する場合に比べて、技術的に容易であり、か
つ製造コストを低減できる。
In addition, according to this embodiment, it is only necessary to mix molten slag powder with commercially available alumina cement powder. It is technically easier and the manufacturing cost can be reduced compared to the conventional method.

なお、上記実施例では、耐火物に溶融スラグ粉末を混在
させた場合を例にとって説明したが、これはスラグ自体
の性状が安定しているからである。
In the above embodiments, the case where molten slag powder was mixed with the refractory was explained as an example, but this is because the properties of the slag itself are stable.

しかし本発明は、このスラグ粉末に限定されるものでは
なく、可燃物が含まれていない灰を混在させてもよく、
この場合でも上記実施例と同様な効果が得られる。
However, the present invention is not limited to this slag powder, and ash that does not contain flammable substances may be mixed.
Even in this case, the same effects as in the above embodiment can be obtained.

また、上記溶融スラグ粉末は、被溶融物が都市ゴミの場
合は都市ゴミの溶融スラグ、下水汚泥の場合はこの下水
汚泥の溶融スラグというように一対一の関係にする方が
、寿命の延長を図るうえでより効果が大きい。
In addition, it is better to use the molten slag powder in a one-to-one relationship, such as when the object to be melted is municipal garbage, the molten slag of the municipal garbage, and when the object is sewage sludge, the molten slag of the sewage sludge. It is more effective in achieving this goal.

さらに、上記実施例では、旋回流式溶融炉を例にとって
説明したが、本発明の溶融炉は勿論これに限られるもの
ではなく、要は産業廃棄物用溶融炉の炉壁であればいず
れにも適用できる。
Furthermore, in the above embodiments, the explanation was given using a swirling flow type melting furnace as an example, but the melting furnace of the present invention is of course not limited to this, and in short, any furnace wall of an industrial waste melting furnace can be used. can also be applied.

第3図は、本実施例の効果を確認するために行った実験
結果を説明するための炉壁の侵食速度と溶融スラグ粉末
の混入割合との関係を示す特性図である。
FIG. 3 is a characteristic diagram showing the relationship between the erosion rate of the furnace wall and the mixing ratio of molten slag powder to explain the results of an experiment conducted to confirm the effects of this example.

この実験は、本実施例の溶融処理装置lにおいて、炉壁
17を、アルミナセメント混合粉末に溶融スラグ粉末を
重量比で20〜100%混入させた耐火物で構成し、こ
の溶融炉2内に石炭灰、下水汚泥灰を250 kg/H
供給して、燃焼溶融させた時の炉壁17の侵食速度を調
べた。なお、この実験では、比較のために従来のアルミ
ナセメント混合粉末のみの耐火物も採用した0図中、X
印は石炭灰、・印は下水汚泥灰を示す。
In this experiment, the furnace wall 17 was constructed of a refractory material in which 20 to 100% by weight of molten slag powder was mixed with alumina cement mixed powder in the melting processing apparatus 1 of this embodiment. 250 kg/h of coal ash and sewage sludge ash
The erosion rate of the furnace wall 17 when it was supplied and burned and melted was investigated. In addition, in this experiment, a conventional refractory made only of alumina cement mixed powder was also used for comparison.
The mark indicates coal ash, and the mark indicates sewage sludge ash.

第3図からも明らかなように、従来の耐火物では、1時
間あたり石炭灰×で0.11層、下水汚泥灰・で約3−
一侵食されているのに対して、本実施例の耐火物では、
溶融スラグ粉末が増加するほど、侵食速度は両者×、・
とも大幅に低下していることがわかる。また、炉壁17
の侵食速度を月間5龍以下に抑制するためには、時間あ
たり0.007 mにする必要があり、これをクリアす
るには上記溶融スラグ粉末を50%以上含有させればよ
いことになる。なお、本実験よれば、上記スラグ粉末を
100%にすると、該粉末同士を結合させるバインダー
効果が減少し、耐火物が脆くなり易く強度が低下するこ
とが判明した。従って望ましくは溶融スラグ粉末の添加
量は60〜90%の範囲が最適である。
As is clear from Figure 3, with conventional refractories, 0.11 layers of coal ash and approximately 3 layers of sewage sludge ash per hour.
However, in the refractory of this example,
As the molten slag powder increases, the erosion rate increases
It can be seen that both have decreased significantly. In addition, the furnace wall 17
In order to suppress the erosion rate to less than 5 yen per month, it is necessary to set it to 0.007 m per hour, and to meet this requirement, it is sufficient to contain the molten slag powder in an amount of 50% or more. According to this experiment, it was found that when the slag powder was increased to 100%, the binder effect that binds the powders to each other decreased, making the refractory more brittle and lowering its strength. Therefore, the amount of molten slag powder added is preferably in the range of 60 to 90%.

〔発明の効果〕〔Effect of the invention〕

以上のように本発明に係る産業廃棄物用溶融炉によれば
、溶融炉の炉壁を被熔融物の溶融スラグ粉末、又は灰を
重量比で50%以上混在させた耐火物で構成したので、
侵食速度を抑制して炉壁の寿命を大幅に延長できる効果
がある。
As described above, according to the industrial waste melting furnace of the present invention, the furnace wall of the melting furnace is made of a refractory mixed with molten slag powder of the material to be melted or ash at a weight ratio of 50% or more. ,
It has the effect of suppressing the erosion rate and significantly extending the life of the furnace wall.

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

第1図及び第2図は本発明の一実施例による産業廃棄物
用溶融炉を説明するだめの図であり、第1図はその溶融
処理装置の概略構成図、第2図はその溶融炉を示す断面
図、第3図は炉壁の侵食速度と溶融スラグ粉末の混合割
合との関係を示す特性図である。 図において、2は溶融炉、17は炉壁である。 特許出願人  株式会社 神戸製鋼所 代理人    弁理士 下 市  努 第2図 カー7
1 and 2 are diagrams for explaining a melting furnace for industrial waste according to an embodiment of the present invention, FIG. 1 is a schematic configuration diagram of the melting processing apparatus, and FIG. FIG. 3 is a characteristic diagram showing the relationship between the erosion rate of the furnace wall and the mixing ratio of molten slag powder. In the figure, 2 is a melting furnace, and 17 is a furnace wall. Patent Applicant Kobe Steel Co., Ltd. Representative Patent Attorney Tsutomu Shimoichi Figure 2 Car 7

Claims (1)

【特許請求の範囲】[Claims] (1)石炭灰,都市ゴミ,下水汚泥スラッジ等の産業廃
棄物を溶融処理するための溶融炉であって、該溶融炉の
炉壁を、被溶融物の溶融スラグ微粉末、又は該被溶融物
の灰を重量比で50%以上含む耐火物で構成したことを
特徴とする産業廃棄物用溶融炉。
(1) A melting furnace for melting industrial waste such as coal ash, municipal garbage, sewage sludge, etc., in which the furnace wall of the melting furnace is covered with molten slag powder of the material to be melted or A melting furnace for industrial waste, characterized in that it is constructed of a refractory material containing 50% or more of industrial waste ash by weight.
JP63117562A 1988-05-13 1988-05-13 Melting furnace for industrial waste Pending JPH01288387A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP63117562A JPH01288387A (en) 1988-05-13 1988-05-13 Melting furnace for industrial waste

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP63117562A JPH01288387A (en) 1988-05-13 1988-05-13 Melting furnace for industrial waste

Publications (1)

Publication Number Publication Date
JPH01288387A true JPH01288387A (en) 1989-11-20

Family

ID=14714887

Family Applications (1)

Application Number Title Priority Date Filing Date
JP63117562A Pending JPH01288387A (en) 1988-05-13 1988-05-13 Melting furnace for industrial waste

Country Status (1)

Country Link
JP (1) JPH01288387A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1999039356A1 (en) * 1998-01-30 1999-08-05 Hitachi, Ltd. Solid material melting apparatus
CN105817463A (en) * 2016-03-25 2016-08-03 无锡宇辰工业污泥处理技术研究院有限公司 Resourceful treatment method for crystalline silicon cutting waste mortar and aluminum oxidation sludge
CN106765200A (en) * 2016-11-24 2017-05-31 商洛市海蓝科技有限公司 Oilfield drilling mud castoff processing system

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1999039356A1 (en) * 1998-01-30 1999-08-05 Hitachi, Ltd. Solid material melting apparatus
US6502520B1 (en) 1998-01-30 2003-01-07 Hitachi, Ltd. Solid material melting apparatus
KR100423686B1 (en) * 1998-01-30 2004-03-18 가부시키가이샤 히타치세이사쿠쇼 Solid material melting apparatus
CN105817463A (en) * 2016-03-25 2016-08-03 无锡宇辰工业污泥处理技术研究院有限公司 Resourceful treatment method for crystalline silicon cutting waste mortar and aluminum oxidation sludge
CN106765200A (en) * 2016-11-24 2017-05-31 商洛市海蓝科技有限公司 Oilfield drilling mud castoff processing system
CN106765200B (en) * 2016-11-24 2018-12-21 商洛市海蓝科技有限公司 Oilfield drilling mud castoff processing system

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