JPH09329318A - Separation method of molten salt and molten slag - Google Patents

Separation method of molten salt and molten slag

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Publication number
JPH09329318A
JPH09329318A JP14931996A JP14931996A JPH09329318A JP H09329318 A JPH09329318 A JP H09329318A JP 14931996 A JP14931996 A JP 14931996A JP 14931996 A JP14931996 A JP 14931996A JP H09329318 A JPH09329318 A JP H09329318A
Authority
JP
Japan
Prior art keywords
molten
slag
molten salt
salt
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.)
Pending
Application number
JP14931996A
Other languages
Japanese (ja)
Inventor
Mutsuo Maki
睦夫 牧
Yoshitomo Yamamoto
義知 山本
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 Steel Corp
Daiho Giken Co Ltd
Original Assignee
Nippon Steel Corp
Daiho Giken Co 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 Nippon Steel Corp, Daiho Giken Co Ltd filed Critical Nippon Steel Corp
Priority to JP14931996A priority Critical patent/JPH09329318A/en
Publication of JPH09329318A publication Critical patent/JPH09329318A/en
Pending legal-status Critical Current

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  • Gasification And Melting Of Waste (AREA)

Abstract

PROBLEM TO BE SOLVED: To improve the qualities molten salt and molten slag in matter melting processed when city garbage burned ash is melted for a processing of making the ash unharmful and for a processing of reutilizing the ash. SOLUTION: The present separation method of molten salt and molten slag is adapted such that city garbage burned ash is melted in a first melting furnace 1 comprising a water cooling metal member to produce molten salt, molten slag 9, and ingot 8 being matter subjected to melting processing, and then the molten salt 10 and the molten slag 9 in the matter are transferred to a second melting furnace 26 comprising a water cooling metal part where the molten salt 10 and the melted slag 9 are separated into two owing to a difference therebetween and are separately independently taken out to the outside of the system.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は、都市ごみ、下水汚
泥、産業廃棄物等の都市ごみを焼却した際に発生する焼
却灰、とりわけその飛灰を溶融した時に生成する溶融塩
と溶融スラグを高品質化して分離する方法に関する。
TECHNICAL FIELD The present invention relates to incinerated ash generated when incinerating municipal solid waste such as municipal solid waste, sewage sludge, industrial waste, and the like, and particularly to molten salt and molten slag produced when the fly ash is melted. The present invention relates to a method of improving quality and separating.

【0002】[0002]

【従来の技術】都市ごみ焼却灰の中にはダイオキシンや
重金属等の有害物質が含まれ、しかも焼却灰は比重が小
さく、且つかさ張るという問題があるほか、そのまま埋
立地に投棄する場合、有害物質の溶出防止対策に多くの
費用がかかるだけでなく、近年、その投棄スペースを確
保することが困難となってきている。
2. Description of the Related Art Municipal solid waste incineration ash contains harmful substances such as dioxins and heavy metals. Moreover, incineration ash has a problem that it has a small specific gravity and is bulky, and when it is dumped directly to a landfill, it is a harmful substance. Not only is it costly to take measures to prevent elution, but in recent years it has become difficult to secure a dumping space.

【0003】そこで、都市ごみ焼却灰を無害化するとと
もに容積を大幅に減少し、その有効活用を図る方法とし
て、各種の溶融スラグ化方法が開発されており、一部は
自治体で採用されている。しかし、都市ごみ焼却灰に
は、通常、主灰と飛灰の二種類が発生しており、従来の
都市ごみ焼却灰の溶融方法は、主灰の溶融に関してはほ
ぼ実用の域に達したものもある。
[0003] Therefore, as a method of making the incinerated ash of municipal solid waste harmless and reducing its volume significantly and making effective use of it, various molten slag forming methods have been developed, and some of them are adopted by local governments. . However, two types of ash and fly ash are usually generated in the incineration ash of municipal solid waste, and the conventional method of melting incinerated ash of municipal solid waste has reached a practical range for melting the main ash. There is also.

【0004】しかしながら、飛灰については未だ実用的
な方法が確立されていないのが実状である。以下その理
由を述べる。一般的に飛灰中にはナトリウムやカリウム
の塩化物を主体とした塩類が多量に含まれており、これ
を溶融すると前記塩類を主体とした溶融塩と、その他の
酸化物を主体とした溶融スラグとが生成し、溶融スラグ
は完全無害化されるが、溶融塩中には幾分溶出有害物を
含有するので、溶融スラグと溶融塩とを分離して取り出
す必要がある。そこで、比重差によって上層部に溶融塩
を生成させ、下層部に溶融スラグを生成させて両者を分
離して取り出す溶融方法として、電力を用いた溶融方法
が知られている。
However, the actual situation is that a practical method has not yet been established for fly ash. The reason will be described below. Fly ash generally contains a large amount of salts mainly containing chlorides of sodium and potassium. When this is melted, molten salts mainly composed of the above salts and other salts mainly composed of oxides are melted. Although the slag and the molten slag are completely detoxified, the molten salt contains some leaching harmful substances, so it is necessary to separate and take out the molten slag and the molten salt. Therefore, as a melting method in which molten salt is generated in the upper layer portion and molten slag is generated in the lower layer portion due to the difference in specific gravity, and both are separated and taken out, a melting method using electric power is known.

【0005】ところが、従来の電力を用いた溶融炉によ
る溶融は、炉体をすべて耐火物を内張りした炉内での溶
融であるため、前記溶融塩は、炉体の耐火物を激しく侵
食するだけでなく、溶融塩の流動性がきわめて高いため
に耐火物中に浸み込み、しかも溶融塩の電気抵抗が小さ
い特性も加わって漏電現象や短絡現象が生じて安定した
操業を継続することができず、実用的な溶融方法ではな
かった。
However, conventional melting using a melting furnace using electric power is melting in a furnace in which the entire refractory body is lined with refractory, so the molten salt only erodes the refractory body of the furnace body violently. Not only that, because the molten salt has extremely high fluidity, it penetrates into the refractory and, in addition, the electrical resistance of the molten salt is small, and the leakage and short-circuit phenomena occur, so that stable operation can be continued. No, it was not a practical melting method.

【0006】また、飛灰中には特に溶出し易い重金属や
有害物が多量に含まれているために飛灰が特別管理一般
廃棄物に指定され、そのため実用的な溶融処理方法の確
立が強く望まれていた。そこで、本出願人の一人が出願
し、特願平6−300272号で開示した溶融処理方法
は、耐火物を用いない単相電気抵抗溶融炉で飛灰溶融を
実施する実用的な飛灰溶融を実現することができた。
In addition, since fly ash contains a large amount of heavy metals and harmful substances that are particularly liable to be eluted, fly ash is designated as specially controlled general waste, and therefore a practical melting treatment method is strongly established. Was wanted. Therefore, the melting treatment method applied by one of the present applicants and disclosed in Japanese Patent Application No. 6-300272 is a practical fly ash melting method in which the fly ash is melted in a single-phase electric resistance melting furnace that does not use a refractory. Could be realized.

【0007】図2は前記の先に出願した耐火物を用いな
い単相電気抵抗溶融炉の一実施例の縦断面図である。す
なわち、図2において、電気抵抗溶融炉は、スラグタッ
プホール2と溶融塩オーバーフローホール3を備えた水
冷された金属部材からなる炉壁1と、前記各ホール2,
3に連接する水冷された金属部材からなる樋4a,4b
と、前記水冷された炉壁1とは分離して設けられた、電
気絶縁物14を介して設けられた炉底電極6と炉床昇降
装置7を備えている水冷された金属部材からなる炉床5
と、上部電極11とで構成されている。
FIG. 2 is a longitudinal sectional view of an embodiment of a single-phase electric resistance melting furnace which does not use a refractory material applied for the above-mentioned application. That is, in FIG. 2, the electric resistance melting furnace includes a furnace wall 1 made of a water-cooled metal member having a slag tap hole 2 and a molten salt overflow hole 3, and each of the holes 2, 2.
3 made of water-cooled metal members connected to 3
And a furnace comprising a water-cooled metal member provided separately from the water-cooled furnace wall 1 and provided with a furnace bottom electrode 6 and a hearth elevating device 7 provided via an electric insulator 14. Floor 5
And the upper electrode 11.

【0008】前記構成において、上部電極11を降下さ
せ、都市ごみ焼却灰12を投入して通電すると、アーク
が発生し都市ごみ焼却灰12が溶融し、溶融の進行に伴
い上部電極11を上昇させる。定常溶融状態では、都市
ごみ焼却灰12が溶融されて、溶融スラグ層9、溶融塩
層10、都市ごみ焼却灰中に含まれる金属が溶融滴下し
て成長したインゴット8が形成され、水冷された炉壁1
には溶融スラグや溶融塩が凝固して耐火物の代わりとな
るセルフコーティング層13が形成される。
In the above structure, when the upper electrode 11 is lowered, and the municipal solid waste incineration ash 12 is charged to supply electricity, an arc is generated and the municipal solid waste incinerator 12 is melted, and the upper electrode 11 is raised as the melting progresses. . In a steady molten state, the municipal solid waste incineration ash 12 is melted, the molten slag layer 9, the molten salt layer 10, and the metal contained in the municipal solid waste incinerator ash is melted and dropped to form an ingot 8 which is water-cooled. Furnace wall 1
The molten slag or the molten salt is solidified therein to form the self-coating layer 13 as a substitute for the refractory.

【0009】都市ごみ焼却灰の溶融により溶融スラグ層
9及び溶融塩層10が深くなると、スラグタップホール
2と溶融塩オーバーフローホール3から排出し、各層
9,10を所定のレベルに維持する。都市ごみ焼却灰中
に含まれる金属は、溶融して炉床5へ滴下し、凝固して
インゴットを形成し、その成長に合わせて炉床昇降装置
7により炉床5を降下させながら都市ごみ焼却灰12を
溶融する。
When the molten slag layer 9 and the molten salt layer 10 become deep due to the melting of the municipal waste incineration ash, they are discharged from the slag tap hole 2 and the molten salt overflow hole 3 to maintain the respective layers 9 and 10 at a predetermined level. The metal contained in the municipal waste incineration ash is melted and dropped into the furnace floor 5, solidifies to form an ingot, and the furnace floor lifting device 7 lowers the furnace floor 5 in accordance with its growth to incinerate the municipal waste. Melt the ash 12.

【0010】インゴットが所定の大きさに成長すると、
溶融を中断し、溶融スラグ9及び溶融塩10を排出した
後、炉床昇降装置7により水冷炉床5を降下させてイン
ゴット8を取り出す。セルフコーティング層13は、熱
及び電気の絶縁体としての作用があるため、塩類を多量
に含む飛灰でも電気的には安定した溶融が可能となる。
When the ingot grows to a predetermined size,
After the melting is interrupted and the molten slag 9 and the molten salt 10 are discharged, the water-cooled hearth 5 is lowered by the hearth lifting device 7 to take out the ingot 8. Since the self-coating layer 13 acts as an insulator of heat and electricity, even if fly ash containing a large amount of salts is electrically stable, it can be melted.

【0011】[0011]

【発明が解決しようとする課題】しかし、前記の電気抵
抗溶融炉では溶融塩と溶融スラグが電磁気力によって対
流に似た激しい撹拌現象を伴っており、しかも溶融塩1
0は常に未溶融の都市ごみ焼却灰層12と接しており、
これを巻き込むようにして溶融が進行する。そしてその
一部は沈降してスラグ層の中に入りスラグ化するが、都
市ごみ焼却灰は溶融塩層及び溶融スラグ層で多量のガス
も発生するため、タップされる溶融塩中には一部未溶融
の都市ごみ焼却灰が懸濁しており、タップされるスラグ
中には気泡を含んだ状態の物がしばしば排出される。こ
れは後に、回収した塩を水で処理して塩化カリウム等の
有用物を回収する場合に未溶融の都市ごみ焼却灰が残滓
として多量に発生しスラッジとなるので好ましくなく、
なるべく溶融塩のみを得たいという課題があった。一
方、気泡を含んだスラグは強度が弱いだけでなく品質む
らが生じるので、その再利用を計る場合に問題が生じる
ことがあるので、なるべく気泡を含まない完全に滓化し
たスラグを得たいという課題があった。また、一次溶融
炉ではスラグの温度管理が困難なのでスラグをスラグウ
ール等に加工しようとした場合、一定の品質の物が得ら
れない困難もあった。
However, in the above-mentioned electric resistance melting furnace, the molten salt and the molten slag are accompanied by a vigorous stirring phenomenon similar to convection due to electromagnetic force.
0 is always in contact with the unmelted municipal solid waste incineration ash layer 12,
Melting proceeds as it is involved. And part of it sinks into the slag layer and becomes slag.However, since the municipal solid waste incineration ash also generates a large amount of gas in the molten salt layer and the molten slag layer, some of it is contained in the tapped molten salt. Unmelted municipal solid waste incineration ash is suspended, and air bubbles are often discharged into tapped slag. This is not preferable because afterwards, when the recovered salt is treated with water to recover useful substances such as potassium chloride, a large amount of unmelted municipal waste incineration ash becomes sludge and becomes sludge,
There was a problem to obtain only molten salt as much as possible. On the other hand, slag containing bubbles not only has weak strength but also uneven quality, so problems may occur when reusing it, so I would like to obtain completely slag that does not contain bubbles as much as possible. There were challenges. Further, since it is difficult to control the temperature of the slag in the primary melting furnace, it was difficult to obtain a product of a certain quality when processing the slag into slag wool or the like.

【0012】[0012]

【課題を解決するための手段】前記のごとく、第1の溶
融炉で塩とスラグを別々にタップした場合は、いずれも
不完全なものが得られてしまうので、第1の溶融炉から
は塩とスラグを同時にタップして第2の溶融炉に受け、
未溶融の都市ごみ焼却灰との縁を完全に断った状態で塩
とスラグを二層分離する手段を取ることによって、未溶
融都市ごみ焼却灰をほとんど含まない塩と、気泡をほと
んど含まない完全に滓化されたスラグとを得ることが可
能になる。また、スラグの温度管理も容易に行えるので
スラグウール等の高付加価値品を得ようとする場合にも
好都合である。
As described above, when salt and slag are separately tapped in the first melting furnace, incomplete ones are obtained in both cases. Tap salt and slag at the same time to receive in the second melting furnace,
By taking a means to separate the salt and slag into two layers with the edge of the unmelted municipal solid waste incinerated completely cut off, the salt containing almost no unmelted municipal solid waste incinerated ash and the complete mixture containing almost no air bubbles are obtained. It becomes possible to obtain slag that has been slagged. Further, since the temperature control of the slag can be easily performed, it is also convenient when trying to obtain a high value-added product such as slag wool.

【0013】すなわち本発明は、都市ごみ焼却灰を水冷
金属部材で構成された第1の溶融炉で溶融処理して、溶
融処理物である溶融塩、溶融スラグ及びインゴットを生
成せしめ、次に、前記溶融処理物の中の溶融塩と溶融ス
ラグとを水冷金属部材で構成された第2の溶融炉に移送
し、この第2の溶融炉にて、溶融塩と溶融スラグとを比
重差により二層に分離し、各々を別々に系外に取り出す
ことを特徴とする溶融塩と溶融スラグの分離方法であ
る。
That is, according to the present invention, incineration ash of municipal solid waste is melt-processed in a first melting furnace composed of a water-cooled metal member to produce a molten salt, a molten slag and an ingot which are molten products, and then, The molten salt and the molten slag in the molten processed product are transferred to a second melting furnace composed of a water-cooled metal member, and the molten salt and the molten slag are separated by a difference in specific gravity in the second melting furnace. It is a method for separating molten salt and molten slag, which is characterized by separating into layers and taking them out of the system separately.

【0014】[0014]

【実施例】本発明を図示する一実施例によってさらに詳
しく説明する。図1は本発明の第1の溶融炉(以下一次
炉という)および第2の溶融炉(以下二次炉という)を
説明するための縦断面図で、図の左側は一次炉を示し1
〜14の符号は前記図2で説明したものと全く同じで、
操業方法も変わりない。図2と異なるのはスラグタップ
ホール2と溶融塩オーバーフローホール3が省略され、
両者を同時にタップするタップホール21が一つ設けら
れている。
The invention will be explained in more detail by means of an illustrated embodiment. FIG. 1 is a longitudinal sectional view for explaining a first melting furnace (hereinafter referred to as a primary furnace) and a second melting furnace (hereinafter referred to as a secondary furnace) of the present invention, and the left side of the drawing shows the primary furnace.
The symbols of 14 are exactly the same as those described in FIG.
The operation method does not change. The difference from FIG. 2 is that the slag tap hole 2 and the molten salt overflow hole 3 are omitted,
There is one tap hole 21 that taps both at the same time.

【0015】このタップホールより溶融塩とスラグを同
時にタップし樋4を経由して図右側の二次炉26に受け
る。この二次炉26は一次炉と全く似た形態をしてお
り、溶融塩オーバーフローホール22とスラグタップホ
ール23を備えた水冷金属部材からなる炉壁と、同じく
炉底電極28を備えた水冷炉床27及び上部電極29よ
り構成されている。両電極28,29には図示しない電
源より単相電力が印加されている。
Molten salt and slag are tapped at the same time from this tap hole and received by the secondary furnace 26 on the right side of the drawing through the gutter 4. This secondary furnace 26 has a form quite similar to that of the primary furnace, and has a furnace wall made of a water-cooled metal member having a molten salt overflow hole 22 and a slag tap hole 23, and a water-cooled furnace also having a furnace bottom electrode 28. It is composed of a floor 27 and an upper electrode 29. Single-phase power is applied to both electrodes 28, 29 from a power source (not shown).

【0016】一次炉から受けた塩とスラグは二次炉でセ
ルフコーティング層を形成しつつ保持され比重差によっ
て溶融塩層30と溶融スラグ層31とに二層分離する。
二次炉では未溶融都市ごみ焼却灰層が存在しないので、
両電極28,29から印加された電力によって昇温さ
れ、塩中に懸濁していた未溶融灰が完全に溶融し塩とス
ラグに分離され、同時にガス成分も除去されて、スラグ
は完全に滓化される。
The salt and slag received from the primary furnace are held in the secondary furnace while forming a self-coating layer and separated into a molten salt layer 30 and a molten slag layer 31 due to a difference in specific gravity.
Since there is no unmelted municipal refuse incineration ash layer in the secondary furnace,
The temperature is raised by the electric power applied from both electrodes 28 and 29, the unmelted ash suspended in the salt is completely melted and separated into salt and slag, and at the same time, the gas component is also removed, and the slag is completely slag. Be converted.

【0017】また、印加する電力を調整することによっ
て二次炉内の温度は任意に上昇することが可能である。
高品質化された塩とスラグはそれぞれオーバーフローホ
ール22及びスラグタップホール23より樋24a,2
4bを経て後工程に適した形態に鋳造される。
Further, the temperature in the secondary furnace can be arbitrarily increased by adjusting the applied power.
High-quality salt and slag are collected from the overflow hole 22 and the slag tap hole 23, respectively, in the gutters 24a and 2a.
After 4b, it is cast into a form suitable for the subsequent process.

【0018】[0018]

【発明の効果】本発明の実施によって以下の効果を奏す
る。すなわち、 (1)未溶融都市ごみ焼却灰をほとんど含まない高品質
の塩を回収できるため後処理で塩から有用物を回収する
際、極めて有利になる。 (2)十分滓化が行われた、気泡をほとんど含まず、強
度が大きく、特定の一定した高品質スラグが得られるの
で、その再利用分野が広くなる効果がある。 (3)溶融スラグの温度管理が容易に行えるのでスラグ
をスラグウール等に直接加工することが可能になる。 (4)第2の溶融炉も第1の溶融炉と同じく水冷金属壁
構造であるため、溶融塩による耐火物の損傷がなく、
又、耐火物の溶出によるスラグや溶融塩への不純物の混
入がない。
The following effects can be obtained by implementing the present invention. That is, (1) high-quality salt containing almost no unmelted municipal solid waste incineration ash can be recovered, which is extremely advantageous when recovering useful substances from the salt by post-treatment. (2) Since the slag is sufficiently slag-free, contains almost no bubbles, has a high strength, and has a specific and constant high quality, it has an effect of broadening the reuse field. (3) Since the temperature of the molten slag can be easily controlled, the slag can be directly processed into slag wool or the like. (4) Since the second melting furnace also has a water-cooled metal wall structure like the first melting furnace, there is no damage to the refractory due to the molten salt,
Further, impurities are not mixed in the slag or the molten salt due to the elution of the refractory.

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

【図1】本発明の溶融炉の例を示す断面図の説明図。FIG. 1 is an explanatory view of a sectional view showing an example of a melting furnace of the present invention.

【図2】従来の溶融炉を示す断面図の説明図。FIG. 2 is an explanatory view of a sectional view showing a conventional melting furnace.

【符号の説明】[Explanation of symbols]

1 炉壁(一次炉) 2,23 スラクグタップホール 3,22 溶融塩オーバーフローホール 4,24 樋 5,27 水冷炉床 6,28 炉底電極 7 炉床昇降装置 8 インゴット 9,31 溶融スラグ層 10,30 溶融塩層 11,29 上部電極 12 焼却灰 13 セルフコーティング層(スラグ+塩) 14 電気絶縁物 21 タップホール 26 二次炉 1 Furnace wall (primary furnace) 2,23 Slagg tap hole 3,22 Molten salt overflow hole 4,24 Gutter 5,27 Water-cooled hearth 6,28 Hearth bottom electrode 7 Hearth lifting device 8 Ingot 9,31 Molten slag layer 10,30 Molten salt layer 11,29 Upper electrode 12 Incinerated ash 13 Self-coating layer (slag + salt) 14 Electrical insulator 21 Tap hole 26 Secondary furnace

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 都市ごみ焼却灰を水冷金属部材で構成さ
れた第1の溶融炉で溶融処理して、溶融処理物である溶
融塩、溶融スラグ及びインゴットを生成せしめ、次に、
前記溶融処理物の中の溶融塩と溶融スラグとを水冷金属
部材で構成された第2の溶融炉に移送し、この第2の溶
融炉にて、溶融塩と溶融スラグとを比重差により二層に
分離し、各々を別々に系外に取り出すことを特徴とする
溶融塩と溶融スラグの分離方法。
1. Municipal refuse incineration ash is melted and processed in a first melting furnace composed of water-cooled metal members to produce molten salt, molten slag and ingot which are molten products, and then,
The molten salt and the molten slag in the molten processed product are transferred to a second melting furnace composed of a water-cooled metal member, and the molten salt and the molten slag are separated by a difference in specific gravity in the second melting furnace. A method for separating molten salt and molten slag, which is characterized in that the molten salt and molten slag are separated into layers and taken out of the system separately.
JP14931996A 1996-06-11 1996-06-11 Separation method of molten salt and molten slag Pending JPH09329318A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP14931996A JPH09329318A (en) 1996-06-11 1996-06-11 Separation method of molten salt and molten slag

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP14931996A JPH09329318A (en) 1996-06-11 1996-06-11 Separation method of molten salt and molten slag

Publications (1)

Publication Number Publication Date
JPH09329318A true JPH09329318A (en) 1997-12-22

Family

ID=15472527

Family Applications (1)

Application Number Title Priority Date Filing Date
JP14931996A Pending JPH09329318A (en) 1996-06-11 1996-06-11 Separation method of molten salt and molten slag

Country Status (1)

Country Link
JP (1) JPH09329318A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102967494A (en) * 2012-10-30 2013-03-13 中国科学院上海应用物理研究所 Molten salt sample preparation device, prepared molten salt sample and preparation and crystallization method thereof

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102967494A (en) * 2012-10-30 2013-03-13 中国科学院上海应用物理研究所 Molten salt sample preparation device, prepared molten salt sample and preparation and crystallization method thereof
CN102967494B (en) * 2012-10-30 2015-04-08 中国科学院上海应用物理研究所 Molten salt sample preparation device, prepared molten salt sample and preparation and crystallization method thereof

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