JPH0987728A - Method for simultaneously executing production of alloy iron in electric furnace and melting treatment of incineration ash - Google Patents

Method for simultaneously executing production of alloy iron in electric furnace and melting treatment of incineration ash

Info

Publication number
JPH0987728A
JPH0987728A JP25226795A JP25226795A JPH0987728A JP H0987728 A JPH0987728 A JP H0987728A JP 25226795 A JP25226795 A JP 25226795A JP 25226795 A JP25226795 A JP 25226795A JP H0987728 A JPH0987728 A JP H0987728A
Authority
JP
Japan
Prior art keywords
refining
metal
incineration ash
electric furnace
slag
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.)
Granted
Application number
JP25226795A
Other languages
Japanese (ja)
Other versions
JP3732561B2 (en
Inventor
Masaaki Senoo
昌明 妹尾
Takanori Kikuno
孝則 菊野
Fumio Yoshida
文夫 吉田
Takashi Furukawa
孝 古川
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Chuo Denki Kogyo Co Ltd
Original Assignee
Chuo Denki Kogyo 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 Chuo Denki Kogyo Co Ltd filed Critical Chuo Denki Kogyo Co Ltd
Priority to JP25226795A priority Critical patent/JP3732561B2/en
Publication of JPH0987728A publication Critical patent/JPH0987728A/en
Application granted granted Critical
Publication of JP3732561B2 publication Critical patent/JP3732561B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Landscapes

  • Gasification And Melting Of Waste (AREA)
  • Treatment Of Steel In Its Molten State (AREA)
  • Refinement Of Pig-Iron, Manufacture Of Cast Iron, And Steel Manufacture Other Than In Revolving Furnaces (AREA)

Abstract

PROBLEM TO BE SOLVED: To treat incineration ash simultaneously with refining of metal (including alloy) by using incineration ash of various kinds of waste as a part of raw materials for metal refining at the time of refining the metal in an electric furnace. SOLUTION: A three-phase submerged arc type hermetic electric furnace is used in, for example, the melting treatment of in the electric furnace for producing silicon manganese and the incineration ash from municipal refuse are used by previously compounding the incineration ash with raw materials for refining. As a result, the silicon manganese and recyclable slag are obtd. The component compsns. of these products are substantially the same as the component compsns. of the products obtd. by ordinary refining. Although harmful components, such as As and Hg, are included in the incineration ash, the amts. thereof are small and, therefore, these components do not adversely affect the refining metal. On the other hand, the results of tests indicate that the harmful components are confined into the slag and problem, such as elution, does not arise. Then, the incineration ash is made pollution-free and reduced in volume by melting while the refining of the metal is executed.

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、一般廃棄物、産業
廃棄物、下水道スラッジ、シュレッダーダスト、その他
の廃棄物の焼却灰を溶融により、減容化、無害化する方
法に関する。更に詳しく述べれば、本発明は、電気炉に
おいて、金属(合金も含む)を精錬するとともに、併せ
て焼却灰を処理する方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for reducing the volume and detoxifying the incineration ash of general waste, industrial waste, sewer sludge, shredder dust and other wastes by melting. More specifically, the present invention relates to a method for refining metals (including alloys) in an electric furnace and treating incinerated ash at the same time.

【0002】[0002]

【従来の技術】従来より、一般廃棄物、産業廃棄物、下
水道スラッジ、シュレッダーダスト等の各種廃棄物は、
焼却処理され、その灰(焼却灰)は多くの場合、埋立地
に廃棄処分されている。しかしながら、埋立地の確保が
年々難しくなっており、その埋立地の延命化が必要であ
る。また、焼却灰には、重金属等の各種有害物質が含ま
れているため、廃棄処分した場合に、雨水によりそのよ
うな有害物質が流出したり、地下水に溶出する等の問題
が生じ得る。このため、従来から、焼却灰の容積を小さ
くする、いわゆる減容化処理や、重金属等の有害物質の
流出や地下水への溶出等を防止するための焼却灰の無害
化処理が検討されている。更に、一歩進んで、焼却灰の
資源化による再利用や、リサイクル技術の開発が待望さ
れている。ところで、灰やスラッジ等を電気抵抗炉にお
いて処理し、これらの灰やスラッジ等から、重金属類を
無害化した人工鉱物と金属とを製造する方法が提案され
ている(特公昭60-56963号公報)。しかしながら、この
方法では、金属の精錬を伴う技術ではなく、単に焼却灰
の電気抵抗熱により溶融する技術であるため、焼却灰又
はその溶融物の電気抵抗の調整が困難であったり、有害
成分のスラグへの固定のため、珪酸分や、石灰分を加え
て、成分調整をする必要がある。その結果、成分調整に
加えられる珪酸分や、石灰分により、せっかくの焼却灰
の減容の効果が減ぜられるという問題点があった。一般
的に、焼却灰の成分や、性状は様々であり、変動も大き
いので、得られるスラグ及び金属成分並びにその性状の
調整が難しく、再利用の用途が少ないという問題もあっ
た。更に、未燃焼残渣の炭素分が多く含まれる廃棄物を
処理すると、炉上、炉外にて燃焼する必要があり、その
ためガス発生量が多くなるため、操業の安定化が図れ
ず、重金属等の有害物質の揮散が生じたり、あるいは排
出燃焼ガス処理のための大がかりな設備を必要とするな
ど問題となる。
2. Description of the Related Art Conventionally, various kinds of waste such as general waste, industrial waste, sewer sludge, shredder dust, etc.
It is incinerated, and its ash (incinerated ash) is often disposed of in landfills. However, securing landfills is becoming more difficult each year, and it is necessary to extend the life of those landfills. In addition, since the incinerated ash contains various harmful substances such as heavy metals, when discarded, problems such as the outflow of such harmful substances due to rainwater and the elution into groundwater may occur. Therefore, conventionally, so-called volume reduction treatment for reducing the volume of incinerated ash and detoxification treatment of incinerated ash for preventing outflow of harmful substances such as heavy metals and elution into groundwater have been studied. . Furthermore, there is a long-awaited need to go one step further and to reuse incineration ash by recycling it and to develop recycling technology. By the way, a method has been proposed in which ash, sludge, and the like are treated in an electric resistance furnace to produce an artificial mineral and a metal in which heavy metals are detoxified from these ash and sludge (Japanese Patent Publication No. 60-56963). ). However, in this method, it is difficult to adjust the electric resistance of the incineration ash or its melt, or to remove harmful components because it is not a technique involving refining of metal but a technique of simply melting the ash by electric resistance heat. In order to fix the slag, it is necessary to add silicic acid and lime to adjust the composition. As a result, there has been a problem that the silicic acid content and lime content added to adjust the components reduce the volume reduction effect of the incinerated ash. Generally, since the composition and properties of incinerated ash are various and vary greatly, it is difficult to control the obtained slag and metal components and their properties, and there is also a problem that they are not reused. Furthermore, when the waste containing a large amount of carbon in the unburned residue is treated, it is necessary to burn it on the furnace or outside the furnace, which increases the amount of gas generated, so the operation cannot be stabilized and heavy metals, etc. It causes problems such as the volatilization of harmful substances, or the need for large-scale equipment for processing exhaust gas.

【0003】[0003]

【発明が解決しようとする課題】従って、本発明は、金
属の精錬を行いながら、焼却灰の溶融による無害化及び
減容化を達成する方法を提供することを目的とする。ま
た、本発明は、焼却灰の成分調整を特に考慮することな
く、再利用可能なスラグを生成し、金属分の回収を行
い、未燃焼残渣(燃残)としての炭素分を金属成分の還
元に利用し、発生する一酸化炭素や水素を含むガスを燃
料として発電等に利用し、もって、エネルギーの有効利
用を図れる方法を提供することを目的とする。
SUMMARY OF THE INVENTION It is therefore an object of the present invention to provide a method for attaining detoxification and volume reduction by melting incineration ash while refining metal. Further, the present invention produces a reusable slag and recovers a metal content without particularly considering the component adjustment of incineration ash, and reduces the carbon content as an unburned residue (fuel residue) to reduce the metal component. It is an object of the present invention to provide a method for effectively utilizing energy by utilizing the generated gas containing carbon monoxide and hydrogen as a fuel for power generation and the like.

【0004】[0004]

【課題を解決するための手段】本発明者は、上記課題を
達成する方法について鋭意検討した結果、電気炉におい
て金属の精錬を行う際に、金属精錬用の原料の一部とし
て焼却灰を使用することにより、上記課題が達成できる
ことを見出し、本発明に到達したものである。
Means for Solving the Problems As a result of earnest studies on a method for achieving the above object, the present inventor uses incinerated ash as a part of a raw material for metal refining when refining metal in an electric furnace. By doing so, they have found that the above problems can be achieved, and have reached the present invention.

【0005】[0005]

【発明の実施の形態】以下、本発明について、詳細に説
明する。本発明において処理される焼却灰は、一般廃棄
物、産業廃棄物、下水道スラッジ、シュレッダーダス
ト、その他の廃棄物の焼却灰である。例えば、都市ゴミ
からの焼却灰は、通常以下の組成からなっている。
BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, the present invention will be described in detail. The incineration ash treated in the present invention is incineration ash of general waste, industrial waste, sewer sludge, shredder dust, and other wastes. For example, incineration ash from municipal waste usually has the following composition.

【0006】[0006]

【表1】 表1 焼却灰化学分析値 成分 SiO2 CaO MgO Al2O3 Fe2O3 Na2O K2O P 濃度(%) 37.1 18.5 2.6 17.9 3.0 3.0 1.6 0.9 成分 Hg Pb As Cd Cr 濃度(ppm) 0.3 860 20 12 150 本発明において使用される金属精錬用の電気炉として
は、金属(合金を含む)を精錬するのに使用されるもの
であれば、特に制限なく各種の電気炉を使用することが
できる。このような電気炉としては、一般に、発熱方式
の相違に従って、抵抗によって発熱させる抵抗炉、アー
クの発熱を利用するアーク炉、誘導加熱を利用する誘導
炉等が挙げられる。熱効率及び重金属等の有害物質の飛
散防止の観点から、好ましくは、抵抗炉が挙げられる。
電気炉として使用される典型的な例の断面図を図1に概
略する。この電気炉1は、密閉型で、ほぼ円筒状の容器
の形態をしている。電気炉1には、上壁を通して3本の
電極2と、3本以上の原料装入装置3とが設けられてい
る。電極2は、それぞれ、精錬工程中、精錬金属層9の
上に生成するスラグ層8の上に装入されているコークス
層11内に先端が嵌入した状態で保持される。一方、原
料装入装置3は、精錬工程中に、コークス層11上に順
次原料12を装入するように、上端に設けられたホッパ
ー3aと、その下に設けられたシュート3bとから形成
されている。また、図1において、電気炉1の側壁4a
の下部に金属取出し口5が設けられ、その反対側の側壁
には、金属取出し口5よりも高い位置にスラグ取出し口
6が設けられている。更に、電気炉1の上壁端部には、
精錬工程で生成した気体を取り出すためのガス取出し口
7が設けられている。
[Table 1] Table 1 Chemical analysis values of incinerated ash Component SiO 2 CaO MgO Al 2 O 3 Fe 2 O 3 Na 2 OK 2 OP concentration (%) 37.1 18.5 2.6 17.9 3.0 3.0 1.6 0.9 Component Hg Pb As Cd Cr concentration (ppm ) 0.3 860 20 12 150 As the electric furnace for refining metals used in the present invention, various electric furnaces can be used without particular limitation as long as they are used for refining metals (including alloys). be able to. As such an electric furnace, generally, a resistance furnace that generates heat by resistance, an arc furnace that uses heat generation of an arc, an induction furnace that uses induction heating, and the like are listed according to the difference in heat generation method. From the viewpoint of thermal efficiency and prevention of scattering of harmful substances such as heavy metals, a resistance furnace is preferable.
A cross-sectional view of a typical example used as an electric furnace is outlined in FIG. The electric furnace 1 is of a closed type and is in the form of a substantially cylindrical container. The electric furnace 1 is provided with three electrodes 2 and three or more raw material charging devices 3 through the upper wall. During the refining process, each of the electrodes 2 is held with its tip fitted in a coke layer 11 charged on a slag layer 8 formed on a refined metal layer 9. On the other hand, the raw material charging device 3 is composed of a hopper 3a provided at the upper end and a chute 3b provided below the hopper 3a so that the raw material 12 is sequentially charged onto the coke layer 11 during the refining process. ing. Further, in FIG. 1, the side wall 4 a of the electric furnace 1
A metal outlet 5 is provided in the lower part of the, and a slag outlet 6 is provided at a position higher than the metal outlet 5 on the side wall on the opposite side. Furthermore, at the upper wall end of the electric furnace 1,
A gas outlet 7 is provided for taking out the gas generated in the refining process.

【0007】本発明において、精錬される金属の種類
は、特に限定されるものではない。純度の高い金属を精
錬する場合であっても、添加する焼却灰の量を調整する
ことによって、不純金属の量を抑制することができるの
で、通常問題は生じない。また、精錬される金属には、
合金が含まれる。典型的には、金属としては、例えば、
銑鉄が挙げられる。また、合金としては、典型的には、
鉄との合金、例えば、シリコマンガン等が挙げられる。
金属の精錬においては、通常、精錬する金属に応じて各
種の原料の組合せが存在する。例えば、合金鉄、銑鉄の
精錬における原料は、鉄鉱石、マンガン鉱石、クロム鉱
石ニッケル鉱石等の原料鉱石、スラグ塩基度調整用の石
灰石や珪石と、還元材料としてのコークスや石炭等を用
いる。本発明においては、焼却灰は、金属の精錬用の原
料の一部として使用する。具体的には、精錬すべき金属
に応じて変動するが、通常使用する原料全体に対して2
0重量%以下、好ましくは1〜10重量%、更に好まし
くは2〜5重量%の量で使用すれば、精錬金属中の不純
物の量を大きく変動させることなく、また焼却灰の減容
化を達成するに充分である。焼却灰に含まれる珪酸分、
CaO、MgOの塩基成分、未燃残の炭素分は原料とし
て作用するため、焼却灰に含まれる珪酸分、塩基成分、
炭素分相当の原料を減少することができる。また、精錬
する金属に応じて、その金属を比較的多く含む焼却灰を
選択し、原料の一部として使用すれば、精錬金属の収量
を改善するのにも有効である。
In the present invention, the kind of metal to be refined is not particularly limited. Even when refining a metal with high purity, the amount of impure metal can be suppressed by adjusting the amount of incinerated ash to be added, so that no problem usually occurs. Also, for the metal to be refined,
Alloys are included. Typically, as the metal, for example,
Pig iron is an example. Also, as an alloy, typically,
An alloy with iron, such as silicomanganese, may be used.
In metal refining, there are usually various combinations of raw materials depending on the metal to be refined. For example, raw materials ores such as iron ore, manganese ore, chromium ore and nickel ore, limestone or silica stone for adjusting slag basicity, and coke or coal as a reducing material are used as raw materials for refining ferroalloys and pig iron. In the present invention, the incineration ash is used as a part of a raw material for refining metal. Specifically, it varies depending on the metal to be refined, but it is 2 with
When used in an amount of 0% by weight or less, preferably 1 to 10% by weight, more preferably 2 to 5% by weight, the volume of impurities in the refined metal is not significantly changed, and the volume of incinerated ash can be reduced. Enough to achieve. Silicic acid content in incineration ash,
Since the basic components of CaO and MgO and the unburned carbon content act as raw materials, the silicic acid content, basic components, and
The raw material equivalent to carbon content can be reduced. Further, if the incineration ash containing a relatively large amount of the metal is selected according to the metal to be refined and used as a part of the raw material, it is also effective in improving the yield of the refined metal.

【0008】焼却灰は、金属精錬用の原料に予め添加し
ておいてもよいし、精錬作業中に溶融金属又はその上の
スラグ上に添加してもよい。本発明においては、合金
鉄、銑鉄精錬でのスラグ溶湯温度は1400〜1500
℃と極めて高温であり、焼却灰の完全溶融がなされ、そ
して重金属等の有害成分はスラグ中の珪酸(SiO2)の網
目構造中に移行し、固化後は安定なガラス質となるた
め、雨による流出や、地下水への溶出等の二次的公害の
防止が図られる。また、焼却灰中の鉄、その他の金属成
分は、合金鉄、銑鉄として回収され、未燃残の炭素分は
その還元材として利用され、発生する一酸化炭素及び水
素を含むガスは発電用の燃料として利用される。更に、
生成したスラグも、従来と同様に道路基盤、建設材料と
して使用することができ、すでに規格化されている合金
鉄、スラグと同一のものとなり、使用用途等の汎用性に
優れたものである。
The incinerated ash may be added to the raw material for refining the metal in advance, or may be added to the molten metal or the slag on the molten metal during the refining operation. In the present invention, the temperature of molten slag in ferroalloy and pig iron refining is 1400 to 1500.
The temperature is extremely high (° C), the incineration ash is completely melted, and harmful components such as heavy metals are transferred to the network structure of silicic acid (SiO 2 ) in the slag and become a stable vitreous substance after solidification. Secondary pollution such as runoff by water and elution into groundwater will be prevented. Further, iron and other metal components in the incinerated ash are recovered as alloy iron and pig iron, the unburned carbon content is used as a reducing agent, and the generated gas containing carbon monoxide and hydrogen is used for power generation. It is used as fuel. Furthermore,
The generated slag can be used as a road base and a construction material as in the conventional case, is the same as the standardized alloy iron and slag, and is excellent in versatility such as intended use.

【0009】[0009]

【実施例】以下、実施例を参照しながら、本発明を更に
詳細に説明する。実施例1 以下に、本発明のシリコマンガン製造電気炉での溶融処
理の実施例を説明する。この実施例は、基本的に図1に
示す構造を有する3相潜弧式密閉電気炉を使用し、シリ
コマンガンを製造した例である。この電気炉の製造能力
は、65,000t/年であり、主要部の仕様はトラン
ス容量は、50,000KVA(最大負荷、28,00
0kw)、炉直径、15m、炉高、6m 電極径、1.
7mであった。なお、この実施例では、予め、上記表1
で示す組成を有する焼却灰を精錬用原料中に配合してお
いたものを使用した。精錬用原料は、以下の通りであっ
た。 原料組成 Kg マンガン鉱石 2285 珪石 435 鉄鉱石 145 ドロマイト 30 コークス 400 焼却灰 100 次いで、精錬作業を行った。精錬作業の条件は、以下の
通りであった。 電気炉負荷 5000〜28000KW 電圧 100〜200V 抵抗 500〜600MΩ 精錬工程によって得られたシリコマンガン及びスラグの
品質を調べ、通常の精錬によって得られた製品と比較し
た。その結果を、以下の表2及び表3に示す。
EXAMPLES The present invention will be described in more detail below with reference to examples. Example 1 Hereinafter, an example of the melting process in the electric furnace for producing silicomanganese of the present invention will be described. This example is an example of producing silicomanganese by using a three-phase submerged arc type closed electric furnace having a structure basically shown in FIG. The production capacity of this electric furnace is 65,000t / year, and the specifications of the main part are that the transformer capacity is 50,000KVA (maximum load, 28,000).
0 kw), furnace diameter, 15 m, furnace height, 6 m electrode diameter, 1.
It was 7 m. In addition, in this embodiment, the above-mentioned Table 1 is previously set.
The incineration ash having the composition shown in (1) was used as a raw material for refining. The raw materials for refining were as follows. Raw material composition Kg manganese ore 2285 silica stone 435 iron ore 145 dolomite 30 coke 400 incineration ash 100 Next, refining work was performed. The conditions for the refining work were as follows. Electric furnace load 5000-28000 KW voltage 100-200 V resistance 500-600 MΩ The quality of silico manganese and slag obtained by the refining process was examined and compared with the products obtained by normal refining. The results are shown in Tables 2 and 3 below.

【0010】[0010]

【表2】 表2:シリコマンガンにおける成分品
質の変化 (%) Mn C Si P S 残りFe 通常品 61.4 2.15 14.2 0.067 0.009 実施例1 61.1 2.17 14.1 0.085 0.010
[Table 2] Table 2: Components of silicomanganese
Change in quality (%) Mn C Si P S Remaining Fe Normal product 61.4 2.15 14.2 0.067 0.009 Example 1 61.1 2.17 14.1 0.085 0.010

【0011】[0011]

【表3】 表3:スラグにおける成分品質の変化 Mn SiO2 CaO MgO Al2 3 (%) 通常品 12.7 37.7 16.9 5.64 15.9実施例1 12.8 37.7 16.4 5.42 16.5 上記表2及び表3から分かるように、実施例1で製造し
たシリコマンガン及びスラグの成分組成には、実質的に
変化はなかった。焼却灰には、AsやHg等の有害な成
分が含まれているが、もともと含まれている量が少ない
ので、精錬金属に悪影響を与えることはない。一方、ス
ラグ中に有害成分が固定化され、溶出等の問題がないか
否かの試験を行うために、溶出試験を実施した。溶出操
作は、環境庁告示第13号(昭和48年)に従い、ま
た、分析は、JIS K0102に従って行った。分析
結果を、以下の表4に示す。
[Table 3] Table 3: Change in component quality in slag Mn SiO 2 CaO MgO Al 2 O 3 (%) Normal product 12.7 37.7 16.9 5.64 15.9 Example 1 12.8 37. 7 16.4 5.42 16.5 As can be seen from Tables 2 and 3 above, there was substantially no change in the component composition of the silicomanganese and slag produced in Example 1. The incinerated ash contains harmful components such as As and Hg, but since it is originally contained in a small amount, it does not adversely affect the refined metal. On the other hand, a dissolution test was carried out in order to test whether harmful components were fixed in the slag and there was no problem such as dissolution. The elution operation was carried out according to the Environmental Agency Notification No. 13 (Showa 48), and the analysis was carried out according to JIS K0102. The results of the analysis are shown in Table 4 below.

【0012】[0012]

【表4】 表4:スラグの溶出試験 (ppm) Hg Pb As Cd Cr CN P 不検出 不検出 不検出 不検出 不検出 不検出 不検出 注)不検出:定量下限以下であることを示す。 上記表4から、生成したスラグ中には、有害物質が封じ
込められ、溶出等の問題が生じるおそれが実質上ないこ
とが分かる。従って、焼却灰を配合してシリコマンガン
を精錬した場合に、得られるスラグは、通常のシリコマ
ンガンスラグと同様に、路盤材、ケーソン材、コンクリ
ート骨材等の建設資材として使用することができる。従
来の単なる焼却灰のみによる溶融処理では、減容化効果
はある程度期待されるものの、焼却灰中の成分が有効に
利用されることがなく、更に、成分調整のために、塩基
成分や珪酸成分の添加が必要とされる場合が多い。この
ため、減量の効果は実際上ほとんど期待できない。これ
に対して、本発明の方法では、焼却灰中の珪酸成分や塩
基成分が精錬用の原料としても利用されるので、減量化
効果が生じる。しかも、その減容化率は、単なる焼却灰
の溶融処理では、被処理焼却灰の容積に対して、20〜
30%程度であるのに対して、本発明の方法では、生成
スラグ量から見て、減容化率で70%程度、減量化率で
60%となる。
[Table 4] Table 4: Dissolution test of slag (ppm) Hg Pb As Cd Cr CNP Not detected Not detected Not detected Not detected Not detected Not detected Not detected Note) Not detected: Indicates below the lower limit of quantification. From Table 4 above, it can be seen that harmful substances are contained in the generated slag and there is substantially no risk of problems such as elution. Therefore, when the incinerated ash is mixed and the silicomanganese is smelted, the obtained slag can be used as a construction material such as a roadbed material, a caisson material, a concrete aggregate and the like, as in a usual silicomanganese slag. Although the volume reduction effect is expected to some extent in the conventional melting treatment using only incinerated ash, the components in the incinerated ash are not effectively used. Is often required. Therefore, the effect of weight loss can hardly be expected in practice. On the other hand, in the method of the present invention, since the silicic acid component and the basic component in the incinerated ash are also used as raw materials for refining, a weight reduction effect is produced. Moreover, the volume reduction rate is 20 to 20% of the volume of the incineration ash to be treated in the simple incineration ash melting process.
On the other hand, in the method of the present invention, the volume reduction rate is about 70%, and the weight reduction rate is 60%, while the amount is about 30%.

【0013】[0013]

【発明の効果】電気炉において金属の精錬を行うと同時
に、焼却灰を処理することにより、生成する金属の成分
に実質的に影響を与えることなく、焼却灰の減容化並び
に減量化が達成できるとともに、焼却灰に含まれる有害
物質が有効に無害化できる。また、焼却灰に含まれる成
分を資源として有効に利用することができ、精錬工程の
操業性、運転費用等の経済性の点で優れたものとなる。
EFFECTS OF THE INVENTION By refining metal in an electric furnace and treating incinerated ash at the same time, the volume of incinerated ash and the volume of the incinerated ash can be reduced without substantially affecting the components of the produced metal. At the same time, the harmful substances contained in the incinerated ash can be effectively rendered harmless. Further, the components contained in the incinerated ash can be effectively used as a resource, which is excellent in economical efficiency such as operability and operating cost in the refining process.

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

【図1】本発明の実施に使用できる電気炉の概略断面図
である。
FIG. 1 is a schematic cross-sectional view of an electric furnace that can be used to carry out the present invention.

【符号の説明】[Explanation of symbols]

1:電気炉 2:電極 3:原料装入装置 5:金属取出し口 6:スラグ取出し口 7:ガス取出し口 1: Electric furnace 2: Electrode 3: Raw material charging device 5: Metal outlet port 6: Slag outlet port 7: Gas outlet port

フロントページの続き (72)発明者 吉田 文夫 茨城県鹿嶋市光4番地 中央電気工業株式 会社鹿島工場内 (72)発明者 古川 孝 茨城県鹿嶋市光4番地 中央電気工業株式 会社鹿島工場内Front Page Continuation (72) Inventor Fumio Yoshida 4 Hikari, Kashima City, Ibaraki Prefecture, inside Kashima Plant Co., Ltd. (72) Inventor Takashi Furukawa 4 Hikari, Kashima City, Ibaraki Plant, Kashima Plant

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 電気炉において金属の精錬を行うと同時
に、焼却灰を処理する方法であって、金属の精錬に使用
する原料の一部として前記焼却灰を使用することを特徴
とする方法。
1. A method for refining metal in an electric furnace and treating incinerated ash at the same time, wherein the incinerated ash is used as a part of a raw material used for refining metal.
JP25226795A 1995-09-29 1995-09-29 Simultaneous implementation of iron alloy production and incineration ash melting in an electric furnace Expired - Lifetime JP3732561B2 (en)

Priority Applications (1)

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JP25226795A JP3732561B2 (en) 1995-09-29 1995-09-29 Simultaneous implementation of iron alloy production and incineration ash melting in an electric furnace

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP25226795A JP3732561B2 (en) 1995-09-29 1995-09-29 Simultaneous implementation of iron alloy production and incineration ash melting in an electric furnace

Publications (2)

Publication Number Publication Date
JPH0987728A true JPH0987728A (en) 1997-03-31
JP3732561B2 JP3732561B2 (en) 2006-01-05

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Country Link
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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5541423B1 (en) * 2012-06-27 2014-07-09 新日鐵住金株式会社 Steelmaking slag reduction treatment device and steelmaking slag reduction treatment system
CN108823349A (en) * 2018-06-15 2018-11-16 甘肃酒钢集团宏兴钢铁股份有限公司 A kind of method of dedusting ash of stainless steel classified use

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5541423B1 (en) * 2012-06-27 2014-07-09 新日鐵住金株式会社 Steelmaking slag reduction treatment device and steelmaking slag reduction treatment system
US9217185B2 (en) 2012-06-27 2015-12-22 Nippon Steel & Sumitomo Metal Corporation Method of reduction processing of steel-making slag
US9238846B2 (en) 2012-06-27 2016-01-19 Nippon Steel & Sumitomo Metal Corporation Reduction processing apparatus for steel-making slag and reduction processing system for steel-making slag
US9534266B2 (en) 2012-06-27 2017-01-03 Nippon Steel & Sumitomo Metal Corporation Slag-supplying container for use in electric furnace for reduction processing of steel-making slag
CN108823349A (en) * 2018-06-15 2018-11-16 甘肃酒钢集团宏兴钢铁股份有限公司 A kind of method of dedusting ash of stainless steel classified use

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