JP3461090B2 - Preheating method for chlorine-containing scrap iron - Google Patents

Preheating method for chlorine-containing scrap iron

Info

Publication number
JP3461090B2
JP3461090B2 JP24921296A JP24921296A JP3461090B2 JP 3461090 B2 JP3461090 B2 JP 3461090B2 JP 24921296 A JP24921296 A JP 24921296A JP 24921296 A JP24921296 A JP 24921296A JP 3461090 B2 JP3461090 B2 JP 3461090B2
Authority
JP
Japan
Prior art keywords
scrap iron
exhaust gas
preheating
chlorine
iron
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
Application number
JP24921296A
Other languages
Japanese (ja)
Other versions
JPH1072614A (en
Inventor
陽二 大垣
健三 山田
郁宏 鷲見
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.)
JFE Steel Corp
Original Assignee
JFE Steel Corp
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 JFE Steel Corp filed Critical JFE Steel Corp
Priority to JP24921296A priority Critical patent/JP3461090B2/en
Publication of JPH1072614A publication Critical patent/JPH1072614A/en
Application granted granted Critical
Publication of JP3461090B2 publication Critical patent/JP3461090B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related 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

  • Refinement Of Pig-Iron, Manufacture Of Cast Iron, And Steel Manufacture Other Than In Revolving Furnaces (AREA)
  • Waste-Gas Treatment And Other Accessory Devices For Furnaces (AREA)
  • Furnace Details (AREA)
  • Carbon Steel Or Casting Steel Manufacturing (AREA)
  • Manufacture And Refinement Of Metals (AREA)

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】この発明は塩素を含有する屑
鉄の溶解炉、特に電気炉において環境に有害な芳香族有
機塩素化合物の発生を抑制する屑鉄の予熱方法に関す
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for preheating scrap iron containing chlorine, which suppresses the generation of environmentally harmful aromatic organic chlorine compounds in a melting furnace, particularly in an electric furnace.

【0002】[0002]

【従来技術】従来屑鉄(鉄スクラップ)は主に電気炉、
その他転炉等において再溶解されてリサイクルされてい
る。この際、電気炉では溶解電力消費量を低減するため
屑鉄を予め電気炉で発生した高温の排ガスにより予熱し
て、電気炉に装入することが通常行われている。
BACKGROUND ART Conventionally, scrap iron (iron scrap) is mainly used in electric furnaces,
Others are remelted in converters and recycled. At this time, in the electric furnace, in order to reduce the consumption of the melting power, it is usual to preheat the scrap iron with the high-temperature exhaust gas generated in the electric furnace and charge the scrap iron into the electric furnace.

【0003】図4には、最近の電気炉設備の1例を示
す。電気炉100からの排ガスは排風機106によって
誘引され、排ガス中のCOは燃焼塔102内で空気吹き
込み口116から供給された空気によって燃焼し、高温
(600〜800℃)の排ガスとなる。電気炉に投入さ
れる屑鉄は予めこの高温の排ガスにより予熱炉103内
で予熱された後、電気炉へ装入される。
FIG. 4 shows an example of recent electric furnace equipment. The exhaust gas from the electric furnace 100 is attracted by the exhaust fan 106, and the CO in the exhaust gas is burned by the air supplied from the air blowing port 116 in the combustion tower 102 to become a high temperature (600 to 800 ° C.) exhaust gas. The scrap iron charged into the electric furnace is preheated in the preheating furnace 103 by the high-temperature exhaust gas in advance and then charged into the electric furnace.

【0004】一方、予熱炉からの排ガスは200〜40
0℃に冷却され、ガスクーラー105、排気ファン10
6、バグフィルター107を通過し、大気に排出され
る。場合によっては、電気炉の排ガスは電気炉周りの建
屋集塵系の排ガスとともに合流させ、集塵機107で除
塵される場合もある。
On the other hand, the exhaust gas from the preheating furnace is 200 to 40
Cooled to 0 ° C, gas cooler 105, exhaust fan 10
6. It passes through the bag filter 107 and is discharged to the atmosphere. In some cases, the exhaust gas of the electric furnace may be combined with the exhaust gas of the building dust collecting system around the electric furnace and dust may be removed by the dust collector 107.

【0005】上記の屑鉄溶解炉や予熱炉において屑鉄の
溶解又は予熱を行う場合、通常は屑鉄に油類、塗料やプ
ラスチック類などが付着しており、電気炉内および予熱
炉においてこれらの燃焼および熱分解によって、炭化水
素化合物が発生する。この際、これら付着物中には通常
塩素が含まれており、そのため微量ではあるが有毒な芳
香族有機塩素化合物も発生する。
When the scrap iron is melted or preheated in the scrap iron melting furnace or the preheating furnace, oils, paints, plastics, etc. are usually attached to the scrap iron. Hydrocarbon compounds are generated by thermal decomposition. At this time, these deposits usually contain chlorine, and therefore, a trace amount of toxic aromatic organic chlorine compounds is also generated.

【0006】この芳香族有機塩素化合物には人体に好ま
しくないクロロベンゼン類(CBs)、クロロフェノー
ル類(CPs)やポリクロロビフェニール類(PCBs
)あるいは極微量であるが、一般にダイオキシンとよ
ばれるポリクロロジベンゾパラジオキシン類(PCDD
s)およびポリクロロジベンゾフラン類(PCDFs )
が含まれる。
The aromatic organochlorine compounds include chlorobenzenes (CBs), chlorophenols (CPs) and polychlorobiphenyls (PCBs) which are not desirable for the human body.
) Or an extremely small amount, but generally called dioxins, polychlorodibenzoparadioxins (PCDD
s) and polychlorodibenzofurans (PCDFs)
Is included.

【0007】また、屑鉄付着物中には有機塩素化合物が
添加された切削油や研削油、または塩化ビニール等有機
塩素化合物が多く含まれている場合には、付着物の熱分
解過程で塩素ガスCl2 や塩化水素HClが多く発生
し、そのため芳香族有機塩素化合物類の発生濃度も高く
なる傾向にあることが知られている。
When the scrap iron deposit contains a large amount of cutting oil or grinding oil to which an organochlorine compound is added, or an organochlorine compound such as vinyl chloride, chlorine gas is generated during the pyrolysis process of the deposit. It is known that a large amount of Cl 2 and hydrogen chloride HCl are generated, and therefore the generation concentration of aromatic organic chlorine compounds tends to be high.

【0008】上記排ガス温度が800℃以上の温度に1
秒以上滞留し、酸素濃度が5vol%以上存在する条件
下では、これら芳香族有機塩素化合物は完全燃焼するこ
とによって低分子の炭化水素もしくは二酸化炭素(CO
2 )と水(H2 O)に一旦分解される。
When the exhaust gas temperature is 800 ° C. or higher,
Under the condition of staying for a second or more and oxygen concentration of 5 vol% or more, these aromatic organochlorine compounds are completely burned to cause low molecular hydrocarbons or carbon dioxide (CO
2 ) and water (H 2 O) once decomposed.

【0009】しかし、上記排ガスが冷却される過程で、
排ガス中の酸素濃度が2vol%以上存在する場合は、
上記排ガス中に含まれているダスト中のCu、Feなど
の重金属の触媒作用によって、250〜500℃、特に
300〜350℃の温度範囲において排ガス中にクロロ
ベンゼン類(CBs)、クロロフェノール類(CPs)
やポリクロロビフェニール類(PCBs )、ポリクロロ
ジベンゾパラジオキシン類(PCDDs )およびポリク
ロロジベンゾフラン類(PCDFs )等の再合成反応が
活発に起こることが知られている。
However, in the process of cooling the exhaust gas,
When the oxygen concentration in the exhaust gas is 2 vol% or more,
Due to the catalytic action of heavy metals such as Cu and Fe in the dust contained in the exhaust gas, chlorobenzenes (CBs) and chlorophenols (CPs) are contained in the exhaust gas in the temperature range of 250 to 500 ° C, particularly 300 to 350 ° C. )
It is known that re-synthesis reaction of polychlorobiphenyls (PCBs), polychlorodibenzoparadioxins (PCDDs), polychlorodibenzofurans (PCDFs) and the like actively occurs.

【0010】このように生成した芳香族有機塩素化合
物、特にポリクロロジベンゾジオキシン類およびポリク
ロロジベンゾフラン類は予熱炉後の排ガスの冷却過程で
200℃以下、好ましくは100℃以下に冷却し、ダス
トに吸着させ、バグフィルターで集塵することによって
排ガスから大部分を除去することができる。しかしなが
ら、集塵ダスト中にはこれら物質が存在することにな
る。従って、従来の屑鉄溶解炉においては環境に好まし
くない芳香族有機塩素化合物等がダスト中に吸着された
状態で環境に放出されるという問題が潜在している。
The aromatic organochlorine compounds thus produced, particularly polychlorodibenzodioxins and polychlorodibenzofurans, are cooled to 200 ° C. or lower, preferably 100 ° C. or lower in the course of cooling the exhaust gas after the preheating furnace to form dust. Most of the exhaust gas can be removed by adsorbing it and collecting dust with a bag filter. However, these substances are present in the collected dust. Therefore, in the conventional scrap iron melting furnace, there is a potential problem that aromatic organic chlorine compounds and the like, which are unfavorable to the environment, are released to the environment while being adsorbed in the dust.

【0011】そこで、特開平6−117780号公報で
は、電気炉の予熱炉の後段に燃焼装置と熱分解のための
保持室を設け、排ガスを急冷し、バグフィルターを通過
させて大気に放散する方法が開示されている(従来技術
1)。また、特開平7−207328号公報では、上底
吹き転炉にスクラップの溶解に際して、炭素材を吹き込
み、発生した有機塩素化合物を含有するガスを炭素材に
吸収させる方法が開示されている(従来技術2)。
In view of this, in Japanese Unexamined Patent Publication No. 6-117780, a combustion device and a holding chamber for thermal decomposition are provided at the latter stage of the preheating furnace of an electric furnace to quench exhaust gas, pass through a bag filter, and dissipate into the atmosphere. A method is disclosed (prior art 1). Further, Japanese Patent Application Laid-Open No. 7-207328 discloses a method of blowing carbon material into a carbon material when the scrap is melted in the upper-bottom blowing converter and absorbing the gas containing the generated organic chlorine compound in the carbon material. Technology 2).

【0012】[0012]

【発明が解決しようとする課題】上記従来技術1では、
溶解炉または予熱炉で発生した排ガス中の芳香族有機塩
素化合物を高温の燃焼装置又は保持室で分解している
が、排ガスの冷却過程で再び合成される可能性があり、
そこで排ガスを冷却塔で急冷する。この際残存した芳香
族有機塩素化合物はダストに吸着されるので、このダス
トをバグフィルターで捕捉する。そのため上記のとお
り、燃焼炉と保持室が必要となり、設備が複雑になって
いる。
In the above-mentioned prior art 1,
Aromatic organic chlorine compounds in the exhaust gas generated in the melting furnace or the preheating furnace are decomposed in the high temperature combustion device or the holding chamber, but they may be synthesized again in the exhaust gas cooling process,
Therefore, the exhaust gas is rapidly cooled in a cooling tower. At this time, the remaining aromatic organic chlorine compound is adsorbed by the dust, so the dust is captured by the bag filter. Therefore, as mentioned above, a combustion furnace and a holding chamber are required, and the equipment is complicated.

【0013】また、従来技術2では、上底吹き転炉で鉄
スクラップを溶解しているが、屑鉄の溶解炉として転炉
は汎用性がある設備ではなく、その技術を電気炉には適
用できないという問題がある。更に、いずれの場合に
も、芳香族有機塩素化合物が付着したダストが排出さ
れ、環境上好ましくない。
Further, in the prior art 2, although iron scrap is melted in the upper-bottom blowing converter, the converter is not a versatile equipment as a scrap iron melting furnace, and the technology cannot be applied to an electric furnace. There is a problem. Furthermore, in any case, dust with an aromatic organochlorine compound attached thereto is discharged, which is environmentally unfavorable.

【0014】そこで、本発明では、溶解炉、特に電気炉
及びこれに付属した予熱炉における芳香族有機塩素化合
物の発生自体を効果的に抑制し、大気中に放散される排
ガス及び排出されるダスト中の芳香族有機塩素化合物の
濃度を環境汚染しない程度にまで低減することを目的と
する。
Therefore, in the present invention, the generation itself of the aromatic organochlorine compound in the melting furnace, particularly the electric furnace and the preheating furnace attached thereto is effectively suppressed, and the exhaust gas emitted into the atmosphere and the dust discharged. The purpose is to reduce the concentration of aromatic organic chlorine compounds in the product to the extent that it does not pollute the environment.

【0015】[0015]

【課題を解決するための手段】本発明者らは上記問題に
ついて鋭意研究した結果、上記電気炉等からの排ガス中
の酸素濃度が上記芳香族有機塩素化合物、特にクロロフ
ェノール類(CPs)、ポリクロロジベンゾパラジオキ
シン類(PCDDs )、ポリクロロジベンゾフラン類
(PCDFs )といった酸素を含有する芳香族有機塩素
化合物の発生と一定の関係があることを知見し、以下の
発明をするに至った。
As a result of intensive studies on the above problems, the present inventors have found that the oxygen concentration in the exhaust gas from the electric furnace etc. is such that the aromatic organic chlorine compounds, especially chlorophenols (CPs), poly The inventors have found that there is a certain relation with the generation of oxygen-containing aromatic organochlorine compounds such as chlorodibenzoparadioxins (PCDDs) and polychlorodibenzofurans (PCDFs), and have made the following inventions.

【0016】第1の発明は、屑鉄を溶解する溶解炉から
の排ガスを屑鉄予熱装置に導入して前記屑鉄を予熱する
方法において、前記屑鉄予熱装置に塩素含有屑鉄と共に
炭素材を所定量混合して前記屑鉄を予熱するに際し、予
熱装置の排ガス中の酸素濃度を2vol%以下とするこ
とを特徴とする塩素含有屑鉄の予熱方法である。
A first aspect of the present invention is a method for preheating the scrap iron by introducing exhaust gas from a melting furnace for melting scrap iron into the scrap iron preheating device, wherein a predetermined amount of carbon material is mixed with the scrap iron containing scrap iron in the scrap iron preheating device. When preheating the scrap iron, the oxygen concentration in the exhaust gas of the preheating device is set to 2 vol% or less, which is a method of preheating chlorine-containing scrap iron.

【0017】従来、屑鉄の溶解又は予熱において、付着
した有機物の燃焼による芳香族有機塩素化合物の発生を
完全に押さえることはできない。しかしながら、発明者
らの研究によれば、排ガス中の酸素濃度2vol%以下
の排ガスで屑鉄を加熱した場合、後述するように芳香族
有機塩素化合物、特に酸素を含有する芳香族有機塩素化
合物の生成が抑制される。
Conventionally, in the melting or preheating of scrap iron, it is not possible to completely suppress the generation of aromatic organochlorine compounds due to the combustion of attached organic matter. However, according to the research conducted by the inventors, when scrap iron is heated with exhaust gas having an oxygen concentration of 2 vol% or less in the exhaust gas, an aromatic organic chlorine compound, particularly an oxygen-containing aromatic organic chlorine compound is produced as described later. Is suppressed.

【0018】この理由は、クロロフェノール類およびポ
リクロロジベンゾパラジオキシン類およびポリクロロジ
ベンゾフラン類はこれらの分子構造内に酸素原子を含ん
でいるので、排ガス中に酸素ガスが存在しない場合には
これらの酸素を含有する芳香族有機塩素化合物の合成が
抑制されるからである。そこで、排ガス中の酸素ガスの
濃度を2vol%以下とするために屑鉄の予熱に際して
炭素材を混合するのである。ここで、溶解炉は通常アー
ク加熱電気炉であるが、本発明はこの電気炉の他に例え
ば転炉に対しても適用できる。
The reason for this is that chlorophenols, polychlorodibenzoparadioxins and polychlorodibenzofurans contain oxygen atoms in their molecular structures, so that when oxygen gas is not present in the exhaust gas, these This is because the synthesis of the aromatic organochlorine compound containing oxygen is suppressed. Therefore, in order to keep the concentration of oxygen gas in the exhaust gas at 2 vol% or less, the carbon material is mixed when the scrap iron is preheated. Here, the melting furnace is usually an arc heating electric furnace, but the present invention can be applied to, for example, a converter as well as this electric furnace.

【0019】第2の発明は、第1の発明において、前記
屑鉄予熱装置に前記炭素材と共に、アルカリ剤を所定量
混合装入して前記屑鉄を予熱することを特徴とする塩素
含有屑鉄の予熱方法である。炭素材と共にアルカリ剤を
所定量混合装入しておくと、屑鉄の溶解若しくは予熱に
際して発生する塩素ガス、塩化水素を中和し、芳香族系
有機塩素化合物の発生を更に抑制できる。
A second aspect of the present invention is the preheating of waste iron containing chlorine according to the first aspect of the present invention, characterized in that a predetermined amount of an alkaline agent is mixed and charged into the waste iron preheating device together with the carbon material to preheat the waste iron. Is the way. When a predetermined amount of an alkali agent is mixed and charged together with the carbonaceous material, chlorine gas and hydrogen chloride generated during the dissolution or preheating of scrap iron can be neutralized and the generation of aromatic organic chlorine compounds can be further suppressed.

【0020】第3の発明は、上記発明において、前記炭
素材がコークス、石炭、活性炭のいずれか若しくはそれ
らの混合物であり、これらの粒径が50μm〜10mm
であることを特徴とする塩素含有屑鉄の予熱方法であ
る。コークス、石炭、活性炭等の炭素材は比較的容易に
入手できると共に、有機塩素化合物を吸着しやすいよう
に、粒径を50μm〜10mmにすると確実に排ガス中
の芳香族有機塩素化合物を低減できる。
In a third aspect based on the above aspect, the carbonaceous material is coke, coal, activated carbon or a mixture thereof, and the particle size of these is 50 μm to 10 mm.
It is a preheating method for chlorine-containing scrap iron, characterized in that Carbon materials such as coke, coal, and activated carbon can be obtained relatively easily, and when the particle size is 50 μm to 10 mm so that the organic chlorine compound is easily adsorbed, the aromatic organic chlorine compound in the exhaust gas can be surely reduced.

【0021】第4の発明は、前述のアルカリ剤が、粒径
10μm〜1mmの消石灰、生石灰、石灰石、水酸化マ
グネシウム、水酸化ナトリウム、炭酸マグネシウムのい
ずれか、若しくはこれらの混合物であることを特徴とす
る塩素含有屑鉄の予熱方法である。消石灰、生石灰、石
灰石及び水酸化マグネシウム、水酸化ナトリウム、炭酸
マグネシウムは容易に入手できるアルカリ剤であって、
粒径を上記範囲とすることにより排ガス中の塩素ガス等
を効率的に中和することができ、芳香族有機塩素化合物
の発生を更に抑制することができる。
A fourth invention is characterized in that the above-mentioned alkaline agent is any one of slaked lime, quicklime, limestone, magnesium hydroxide, sodium hydroxide, magnesium carbonate having a particle size of 10 μm to 1 mm, or a mixture thereof. This is a preheating method for chlorine-containing scrap iron. Slaked lime, quick lime, limestone and magnesium hydroxide, sodium hydroxide, magnesium carbonate are readily available alkaline agents,
By setting the particle size within the above range, chlorine gas and the like in the exhaust gas can be efficiently neutralized, and the generation of aromatic organic chlorine compounds can be further suppressed.

【0022】第5の発明は、上記発明において、前記炭
素材及び/又はアルカリ剤を各々屑鉄1t当たり0.1
〜10kg混合して装入することを特徴とする塩素含有
屑鉄の予熱方法である。屑鉄中に含まれている各種の有
機化合物の量を特定は出来ないが、経験上炭素材及び/
又はアルカリ剤を各々屑鉄1t当たり0.1〜10kg
混合して装入することにより、排ガス中の芳香族有機塩
素化合物、例えばPCDDsとPCDFsの合計値を3
0ng/Nm3 以下に低減できる。
A fifth invention is the above invention, wherein the carbon material and / or the alkaline agent is added in an amount of 0.1 per 1 ton of scrap iron.
It is a method for preheating chlorine-containing scrap iron, which is characterized by mixing and loading 10 kg. Although the amount of various organic compounds contained in scrap iron cannot be specified, it is empirical that carbon materials and / or
Or 0.1-10 kg of alkaline agent per 1 ton of scrap iron
By mixing and charging, the total value of aromatic organic chlorine compounds, such as PCDDs and PCDFs, in the exhaust gas is 3
It can be reduced to 0 ng / Nm 3 or less.

【0023】第6の発明は、上記発明において、前記屑
鉄予熱装置の排ガス出口近傍において冷却ガスを導入
し、前記排ガス出口近傍の排ガス温度を100℃以下に
することを特徴とする塩素含有屑鉄の予熱方法である。
通常、屑鉄予熱装置の排ガス出口近傍のガス温度は20
0〜400℃程度であるが、空気その他の冷却ガスを導
入し、前記排ガス出口近傍の排ガス温度を100℃以下
にすると、排ガス中に有機化合物が含まれていても芳香
族有機塩素化合物が再合成されることはない。
In a sixth aspect of the present invention, there is provided the chlorine-containing waste iron according to the above invention, characterized in that a cooling gas is introduced in the vicinity of the exhaust gas outlet of the waste iron preheating device and the exhaust gas temperature in the vicinity of the exhaust gas outlet is set to 100 ° C. or less. It is a preheating method.
Normally, the gas temperature near the exhaust gas outlet of the scrap iron preheating device is 20
Although it is about 0 to 400 ° C., when cooling gas such as air is introduced and the exhaust gas temperature in the vicinity of the exhaust gas outlet is set to 100 ° C. or less, the aromatic organic chlorine compound is regenerated even if the exhaust gas contains an organic compound. It is never synthesized.

【0024】[0024]

【発明の実施の形態】有機化合物を燃焼させる場合、燃
焼方法によっては二酸化炭素(CO2 ) と水(H2 O)
に完全に分解させることは難しく、炭化水素の発生が起
こる。この時有機化合物中に塩素が存在する場合には、
微量であるが芳香族有機塩素化合物の発生が伴う。さら
に、有機化合物中にわずかな塩素が含まれる場合でも、
極微量のポリクロロジベンゾパラジオキシン類およびポ
リクロロジベンゾフラン類が発生する。
BEST MODE FOR CARRYING OUT THE INVENTION When an organic compound is burned, carbon dioxide (CO 2 ) and water (H 2 O) are used depending on the burning method.
It is difficult to completely decompose it, and generation of hydrocarbon occurs. At this time, if chlorine is present in the organic compound,
A slight amount is accompanied by the generation of aromatic organic chlorine compounds. Furthermore, even if a small amount of chlorine is contained in the organic compound,
Trace amounts of polychlorodibenzoparadioxins and polychlorodibenzofurans are generated.

【0025】屑鉄等に付着する有機化合物中の有機塩素
は勿論の事、塩分(NaCl)などの無機塩素からも塩
化水素の発生は確認されており、これらが有機塩素化合
物の塩素源となることが知られている。
It has been confirmed that hydrogen chloride is generated not only from the organic chlorine in the organic compound adhering to scrap iron, but also from the inorganic chlorine such as salt (NaCl), which serves as the chlorine source of the organic chlorine compound. It has been known.

【0026】屑鉄に付着した塩素を完全に除去すること
は不可能であることから、屑鉄に付着した有機物の燃焼
により、芳香族有機塩素化合物の発生を完全に押さえる
ことはできない。しかしながら、発明者らの研究によれ
ば、酸素を含まない雰囲気において屑鉄を加熱した場
合、芳香族有機塩素化合物、特に酸素を含有する芳香族
有機塩素化合物の生成が抑制されることを見いだした。
以下において、上記知見を得た実験について述べる。
Since it is impossible to completely remove the chlorine adhering to the scrap iron, it is impossible to completely suppress the generation of the aromatic organochlorine compound by burning the organic matter adhering to the scrap iron. However, studies by the inventors have found that when scrap iron is heated in an oxygen-free atmosphere, the production of aromatic organochlorine compounds, particularly aromatic organochlorine compounds containing oxygen, is suppressed.
Below, the experiment which acquired the said knowledge is described.

【0027】図1に示す外気の進入を防止してある誘導
加熱炉2に自動車のシュレッダー屑3を50kg(大き
さ20〜50mmのもの)装入し、100〜1000℃
間の種々の温度に加熱する。加熱装置の底部の導入管か
らCO2 :15vol%,N2 :85vol%のガス
に、更に酸素ガス(O2 )を0〜20vol%を加えた
ものを導入ガス6として装入し、装置内のガスを排気フ
ァン10で吸引し、排出されたガスを分析した。尚、加
熱時間は約30分で、この間に連続してガスサンプリン
グを行い、その間の平均値としての排ガス組成を求め
た。
50 kg (size 20-50 mm) of automobile shredder scraps 3 are loaded into an induction heating furnace 2 shown in FIG.
Heat to various temperatures in between. From the introduction pipe at the bottom of the heating device, a gas of CO 2 : 15 vol% and N 2 : 85 vol% to which 0 to 20 vol% of oxygen gas (O 2 ) was further added was introduced as an introduction gas 6, and the inside of the device was charged. Was exhausted by the exhaust fan 10 and the exhausted gas was analyzed. The heating time was about 30 minutes, during which gas sampling was continuously performed, and the exhaust gas composition as an average value during that period was determined.

【0028】図2に800℃に加熱した状態における、
排ガス中の酸素濃度と芳香族有機塩素化合物(PCDD
s+PCDFs,CPs,CBs)の濃度変化を示す。
この図から排ガス中の酸素濃度が約2vol%を超える
と上記芳香族有機塩素化合物が増加していることが明ら
かである。従って、屑鉄の予熱においては酸素濃度を2
vol%以下にすることが重要であると判明した。
In FIG. 2, in the state of being heated to 800 ° C.,
Oxygen concentration in exhaust gas and aromatic organic chlorine compounds (PCDD
s + PCDFs, CPs, CBs).
From this figure, it is clear that when the oxygen concentration in the exhaust gas exceeds about 2 vol%, the amount of the aromatic organochlorine compound increases. Therefore, in the preheating of scrap iron, the oxygen concentration is set to 2
It has been found that it is important to keep it to be not more than vol%.

【0029】更に、温度と酸素濃度を種々変化させて実
験した結果、図3が得られた。この図は以下の様な結果
を示す。 約900℃以上では、酸素濃度によらず芳香族有機塩
素化合物は、殆ど分解する。 200〜900℃の範囲では、酸素濃度が約2vol
%以上の場合には芳香族有機塩素化合物の再合成若しく
は分解再合成が生じて、排ガス中に芳香族有機塩素化合
物が含まれる。 200℃以下では、芳香族有機塩素化合物は発生しな
い。即ち、屑鉄に含まれている有機化合物は分解しない
こと、更にはガス中に芳香族有機化合物が仮に含まれて
いても芳香族有機塩素化合物の合成が行われないことも
意味する。
Further, as a result of an experiment in which the temperature and the oxygen concentration were variously changed, FIG. 3 was obtained. This figure shows the following results. At about 900 ° C or higher, the aromatic organic chlorine compound is almost decomposed regardless of the oxygen concentration. In the range of 200 to 900 ° C, the oxygen concentration is about 2 vol.
When it is more than 0.1%, re-synthesis or decomposition re-synthesis of the aromatic organochlorine compound occurs and the exhaust gas contains the aromatic organochlorine compound. At 200 ° C or lower, no aromatic organic chlorine compound is generated. That is, it means that the organic compound contained in the scrap iron is not decomposed, and further, even if the aromatic organic compound is contained in the gas, the synthesis of the aromatic organic chlorine compound is not performed.

【0030】従って、200〜900℃の温度範囲にあ
る屑鉄予熱装置において、酸素濃度を2vol%以下に
すると酸素を含有する芳香族有機塩素化合物は発生しな
い。しかし、通常、電気炉の排ガスは燃焼塔で燃焼され
るために予熱炉に導入される排ガスは酸素濃度が2vo
l%以下となる。
Therefore, in the scrap iron preheating apparatus in the temperature range of 200 to 900 ° C. , when the oxygen concentration is 2 vol% or less, the aromatic organic chlorine compound containing oxygen is not generated. However, since the exhaust gas of the electric furnace is usually burned in the combustion tower, the exhaust gas introduced into the preheating furnace has an oxygen concentration of 2 vo.
It becomes 1% or less.

【0031】そこで、上記酸素濃度を2vol%以下と
する対策が必要となる。そこで、前述と同一の実験装置
において、炭素材としてコークス粉(粒径0.5〜5m
m,被表面積20m2 /g)を100〜500g、及び
/又は消石灰(特号級)を100〜500gを屑鉄に均
一に混合して実験を行った。なお、この実験において
は、導入ガス中の酸素濃度は5vol%であり、温度は
800℃であった。その結果を表1に示す。なお、表1
には炭素材とアルカリ剤を全く混合しない場合の結果を
併せて示した。
Therefore, it is necessary to take measures to reduce the oxygen concentration to 2 vol% or less. Therefore, in the same experimental device as described above, coke powder (particle size 0.5 to 5 m) was used as the carbon material.
m, surface area 20 m 2 / g) and / or 100 to 500 g of slaked lime (special grade) and / or slaked lime (special grade) were uniformly mixed with scrap iron to conduct an experiment. In this experiment, the oxygen concentration in the introduced gas was 5 vol% and the temperature was 800 ° C. The results are shown in Table 1. In addition, Table 1
In addition, the results when the carbon material and the alkaline agent are not mixed are shown together.

【0032】その結果、CO2 :13vol%,N2:8
2vol%,O2 :5vol%の導入雰囲気ガスを通し
800℃で屑鉄を予熱すると、コークス塊および/又は
消石灰を添加した場合はこれらを添加しない場合と比較
し、これらの芳香族有機塩素化合物の生成が抑制される
ことが判明した。実験において導入ガスのO2 濃度が5
vol%でも、炭素材を装入してあれば排ガス中の酸素
はコークス塊の添加によって消費され、1.5vol%
となり酸素濃度が低下し、酸素を含有する芳香族有機塩
素化合物の発生が抑制されたものと考えられる。
As a result, CO 2 : 13 vol%, N 2 : 8
When scrap iron is preheated at 800 ° C. through an introduced atmosphere gas of 2 vol%, O 2 : 5 vol%, when coke lumps and / or slaked lime are added, as compared with the case where these are not added, these aromatic organic chlorine compounds It was found that generation was suppressed. In the experiment, the O 2 concentration of the introduced gas was 5
Even in vol%, if carbon material is charged, the oxygen in the exhaust gas is consumed by the addition of coke lumps, and 1.5 vol%
It is considered that the oxygen concentration decreased and the generation of oxygen-containing aromatic organic chlorine compounds was suppressed.

【0033】ここで、添加する炭素材は排ガス中の酸素
を消費する働きがある他、排ガス温度が200℃以下に
おいて炭化水素、特に沸点が200℃以上であり平面構
造を持つベンゼン環を有する芳香族有機塩素化合物を吸
着する性質があることがよく知られている。したがっ
て、屑鉄とともに添加した炭素材は予熱時に発生した芳
香族有機塩素化合物を吸着する。このため、添加する炭
素材は吸着能を高めるため、比表面積が10〜1200
2 /gであることが望ましい。
Here, the carbon material to be added has a function of consuming oxygen in the exhaust gas, and also a hydrocarbon having an exhaust gas temperature of 200 ° C. or lower, particularly a benzene ring having a boiling point of 200 ° C. or higher and having a benzene ring having a planar structure. It is well known that it has a property of adsorbing a group organic chlorine compound. Therefore, the carbon material added together with the scrap iron adsorbs the aromatic organic chlorine compound generated during preheating. For this reason, the carbon material to be added has a specific surface area of 10 to 1200 in order to enhance the adsorption ability.
It is preferably m 2 / g.

【0034】この目的のためには、コークスの他、リグ
ナイトコークスや活性炭等が適している。粒径は小さい
ほど排ガスとの接触効率が高くなるが、小さすぎると排
ガスと共に排出され、芳香族有機塩素化合物の吸着には
支障がないが、予熱時の排ガス中の酸素を消費すること
ができなくなる。このため炭素材の粒径は50μm 〜1
0mmであり、好ましくは0.5〜10mmが適当であ
る。また、添加量は屑鉄との混合性を考慮し、0.1〜
10kg/t屑鉄が適当である。
For this purpose, lignite coke, activated carbon and the like are suitable in addition to coke. The smaller the particle size, the higher the efficiency of contact with the exhaust gas, but if it is too small, it will be discharged together with the exhaust gas, and there will be no hindrance to the adsorption of aromatic organochlorine compounds, but oxygen in the exhaust gas during preheating can be consumed. Disappear. Therefore, the particle size of the carbon material is 50 μm-1
It is 0 mm, preferably 0.5 to 10 mm. In addition, the addition amount is 0.1-0.1 in consideration of the compatibility with scrap iron.
10 kg / t scrap iron is suitable.

【0035】一方、消石灰(Ca(OH)2 )の添加は
塩素を含むクロロベンゼン(CBs)等の芳香族有機塩
素化合物の発生抑制に効果があることが分かった。これ
は、熱分解によって、付着有機塩素化合物から発生した
HClを消石灰が中和し、芳香族有機塩素化合物の生成
を抑制したものと考えられる。尚、塩化ビニールは25
0〜300℃で分解し、HClを発生することはよく知
られている。
On the other hand, it was found that the addition of slaked lime (Ca (OH) 2 ) was effective in suppressing the generation of aromatic organic chlorine compounds such as chlorobenzene (CBs) containing chlorine. It is considered that this is because slaked lime neutralized HCl generated from the attached organic chlorine compound by thermal decomposition, and suppressed generation of the aromatic organic chlorine compound. In addition, vinyl chloride is 25
It is well known that it decomposes at 0 to 300 ° C to generate HCl.

【0036】発生するHClの中和のためには消石灰の
他、石灰石(CaCO3 ) 、生石灰(CaO)、水酸化
マグネシウム(Mg(OH)2 ) 、水酸化ナトリウム
(NaOH) 、および炭酸マグネシウム(MgCO3 )
等のその他のアルカリ剤を用いることができる。添加す
るアルカリ剤の径は反応性からは小さいほど好ましい
が、細かすぎると排ガスに同伴して飛散してしまうた
め、予熱炉内での中和反応に有効に消費されない。この
ため、粒径は10μm〜1mm、好ましくは100〜5
00μmが適当である。
In order to neutralize the generated HCl, in addition to slaked lime, limestone (CaCO 3 ), quick lime (CaO), magnesium hydroxide (Mg (OH) 2 ), sodium hydroxide (NaOH), and magnesium carbonate ( MgCO 3 )
Other alkaline agents such as The smaller the diameter of the alkali agent to be added, the more preferable it is from the viewpoint of reactivity, but if it is too fine, it will be entrained in the exhaust gas and scattered, so that it will not be effectively consumed for the neutralization reaction in the preheating furnace. Therefore, the particle size is 10 μm to 1 mm, preferably 100 to 5
00 μm is suitable.

【0037】また、添加量は屑鉄へ付着する有機物中の
塩素含量によって決定されるが、屑鉄中の塩素含量は多
くとも0.2wt%程度であり、これが全てHClにな
ったとして、中和に要するCa(OH)2 量は4kg/
t屑鉄である。これから、屑鉄との混合性を考慮すれ
ば、アルカリ剤の添加量は0.1〜10kg/t屑鉄が
適当である。
The amount of addition is determined by the chlorine content in the organic matter adhering to the scrap iron, but the chlorine content in the scrap iron is about 0.2 wt% at most, and if all of this becomes HCl, it will be neutralized. The amount of Ca (OH) 2 required is 4 kg /
It is scrap iron. From this, considering the compatibility with scrap iron, 0.1-10 kg / t scrap iron is suitable for the addition amount of the alkaline agent.

【0038】添加されたこれらの炭素材は屑鉄と共に溶
解炉に装入されて、炭素材として有効に使用される。ま
た、炭素材やアルカリ剤に吸着された芳香族有機塩素化
合物は予熱過程で高温になるとともに、炭素材やアルカ
リ剤から多少は放出されるが、溶解炉に装入されると、
残存した芳香族有機塩素化合物は溶解炉において120
0℃以上に加熱されるため、ほぼ完全に分解する。一
方、添加された石灰等のアルカリ剤は溶解炉におけるス
ラグの塩基度調整剤として有効に利用される。
These added carbon materials are charged into a melting furnace together with scrap iron and used effectively as carbon materials. Further, the aromatic organic chlorine compound adsorbed on the carbon material or the alkaline agent becomes high in temperature in the preheating process, and is slightly released from the carbon material or the alkaline agent, but when charged into the melting furnace,
The remaining aromatic organochlorine compound is 120 in the melting furnace.
Since it is heated above 0 ° C, it decomposes almost completely. On the other hand, the added alkaline agent such as lime is effectively used as a basicity adjusting agent for slag in the melting furnace.

【0039】また、既に述べた実験から、予熱炉の出口
近傍において空気等の冷却ガスを導入し、排ガスを20
0℃以下に冷却するとその後の段階で芳香族有機塩素化
合物の再合成を抑制できることも明らかである。
Further, from the above-mentioned experiment, a cooling gas such as air is introduced near the exit of the preheating furnace to reduce the exhaust gas to 20
It is also clear that cooling to 0 ° C. or lower can suppress the resynthesis of the aromatic organic chlorine compound in the subsequent stage.

【0040】[0040]

【表1】 [Table 1]

【0041】[0041]

【発明の効果】以上のように、この発明によれば、屑鉄
溶解炉からの高温排ガスを用いて、屑鉄を予熱する時
に、屑鉄に付着した有機物の燃焼および熱分解時に、炭
化水素や芳香族有機塩素化合物、特に、クロロフェノー
ル類(CPs)、クロロベンゼン類(CBs)、ポリク
ロロジベンゾパラジオキシン類(PCDDs)及びポリ
クロロジベンゾフラン類(PCDFs )等の芳香族有機
塩素化合物の発生を抑制することができる。
As described above, according to the present invention, when the waste iron is preheated by using the high temperature exhaust gas from the scrap iron melting furnace, hydrocarbons and aromatics are burned at the time of burning and pyrolyzing the organic matter adhering to the scrap iron. Suppressing the generation of organochlorine compounds, particularly aromatic organochlorine compounds such as chlorophenols (CPs), chlorobenzenes (CBs), polychlorodibenzoparadioxins (PCDDs) and polychlorodibenzofurans (PCDFs) it can.

【0042】即ち、屑鉄の予熱炉に炭素材を添加し、排
ガス中の酸素濃度を2vol%以下とし、更に、石灰な
どのアルカリ剤によって、屑鉄に付着した塩素分より発
生するHClおよびCl2 を中和することによって、上
記の芳香族系有機塩素化合物の発生を抑制するという効
果がある。
That is, a carbon material is added to a scrap iron preheating furnace so that the oxygen concentration in the exhaust gas is 2 vol% or less, and further, HCl and Cl 2 generated from the chlorine content adhering to the scrap iron by an alkaline agent such as lime. The neutralization has an effect of suppressing the generation of the above aromatic organic chlorine compound.

【0043】さらに加えて、屑鉄との熱交換によって、
高温の排ガスから屑鉄に熱回収するとともに、排ガス温
度が低下したことによって、添加された炭素材に炭化水
素や芳香族有機塩素化合物を吸着させることによって、
予熱炉後段へのこれらの化合物の排出を押さえるととも
に、最終段に設置された集塵装置に於いて捕集ダストに
吸着されることによつて、これら芳香族有機塩素化合物
の量を徹底的に低減する効果がある。従って、集塵ダス
トとして環境中に排出される量も極力低く押さえること
ができる。
In addition, by heat exchange with scrap iron,
While recovering heat from the high-temperature exhaust gas to scrap iron, the temperature of the exhaust gas has dropped, and by adsorbing hydrocarbons and aromatic organic chlorine compounds on the added carbon material,
By suppressing the discharge of these compounds to the latter stage of the preheating furnace and adsorbing them to the collected dust in the dust collector installed in the final stage, the amount of these aromatic organic chlorine compounds was thoroughly checked. There is an effect of reducing. Therefore, the amount of dust collected in the environment can be suppressed as low as possible.

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

【図1】本発明のための基礎実験をした実験装置の概要
図である。
FIG. 1 is a schematic diagram of an experimental device for basic experiments for the present invention.

【図2】排ガス中の酸素濃度と芳香族有機塩素化合物濃
度との関係を示す図である。
FIG. 2 is a diagram showing a relationship between oxygen concentration in exhaust gas and aromatic organic chlorine compound concentration.

【図3】排ガスの温度と酸素濃度との関係における芳香
族有機塩素化合物の発生状況を示す図である。
FIG. 3 is a diagram showing a state of generation of an aromatic organochlorine compound in relation to a temperature of exhaust gas and an oxygen concentration.

【図4】従来の屑鉄溶解炉における予熱および排ガス処
理装置を示す図である。
FIG. 4 is a diagram showing a preheating and exhaust gas treatment device in a conventional scrap iron melting furnace.

【符号の説明】[Explanation of symbols]

2 誘導加熱炉 3 シュレッダー屑 4 ガス導入管 6 導入ガス 8 配管 10 排気ファン 100 電気炉 102 燃焼塔 103 予熱炉 105 ガスクーラー 106 排気装置 107 集塵装置 2 induction heating furnace 3 shredder waste 4 gas introduction pipes 6 Introduced gas 8 piping 10 exhaust fan 100 electric furnace 102 combustion tower 103 Preheating furnace 105 gas cooler 106 exhaust system 107 Dust collector

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI F27D 17/00 101 F27D 17/00 101G 104 104D (56)参考文献 特開 平10−8118(JP,A) 特開 平8−42980(JP,A) 特開 平6−109367(JP,A) 特開 平8−269527(JP,A) 特開 平7−146082(JP,A) (58)調査した分野(Int.Cl.7,DB名) C21C 5/52 ZAB C21C 5/28 C22B 1/00 C22B 9/16 F27D 13/00 F27D 17/00 101 F27D 17/00 104 ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 7 Identification code FI F27D 17/00 101 F27D 17/00 101G 104 104D (56) Reference JP-A-10-8118 (JP, A) JP-A-8 -42980 (JP, A) JP-A-6-109367 (JP, A) JP-A-8-269527 (JP, A) JP-A-7-146082 (JP, A) (58) Fields investigated (Int.Cl) . 7, DB name) C21C 5/52 ZAB C21C 5/28 C22B 1/00 C22B 9/16 F27D 13/00 F27D 17/00 101 F27D 17/00 104

Claims (4)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 屑鉄を溶解する溶解炉からの排ガスを屑
鉄予熱装置に導入して前記屑鉄を予熱する方法におい
て、前記屑鉄予熱装置に塩素含有屑鉄と共に、コーク
ス、石炭、活性炭のうちから選択されるいずれか1種、
または2種以上の混合物であり、これらの粒径が50μ
m〜10mmである炭素材を所定量混合して屑鉄を予熱
するに際し、予熱装置の排ガス中の酸素濃度を2vol
%以下とすることを特徴とする塩素含有屑鉄の予熱方
法。
1. A method of preheating waste iron by introducing exhaust gas from a melting furnace for melting scrap iron into a scrap iron preheating device, wherein the scrap iron preheating device together with chlorine-containing scrap iron, coke.
Any one selected from coal, activated carbon,
Alternatively, it is a mixture of two or more kinds, and the particle size of these is 50 μm.
When mixing a predetermined amount of carbon material of m to 10 mm to preheat the scrap iron, the oxygen concentration in the exhaust gas of the preheating device is set to 2 vol.
% Or less, a method for preheating chlorine-containing scrap iron.
【請求項2】 前記屑鉄予熱装置に前記炭素材と共に、
消石灰、生石灰、石灰石、水酸化マグネシウム、水酸化
ナトリウム、炭酸マグネシウムのうちから選択されるい
ずれか1種、または2種以上の混合物であり、これらの
粒径が10μm〜1mmであるアルカリ剤を所定量混合
装入して屑鉄を予熱することを特徴とする請求項1に記
載された塩素含有屑鉄の予熱方法。
2. The scrap iron preheating device together with the carbon material,
Slaked lime, quick lime, limestone, magnesium hydroxide, hydroxide
Choose from sodium and magnesium carbonate
Either one or a mixture of two or more of these,
The method for preheating waste iron containing chlorine according to claim 1, wherein a predetermined amount of an alkaline agent having a particle diameter of 10 μm to 1 mm is mixed and charged to preheat the scrap iron.
【請求項3】 前記炭素材及び/又は前記アルカリ剤を
各々前記屑鉄1t当り0.1〜10kg混合して装入す
ることを特徴とする請求項1又は2に記載された塩素含
有屑鉄の予熱方法。
3. Preheating of chlorine-containing waste iron according to claim 1 or 2, wherein the carbon material and / or the alkaline agent are mixed and charged in an amount of 0.1 to 10 kg per ton of the waste iron. Method.
【請求項4】 前記屑鉄予熱装置の排ガス出口近傍にお
いて冷却ガスを導入し、前記排ガス出口近傍の排ガス温
度を200℃以下にすることを特徴とする請求項1〜3
のいずれか1項に記載された塩素含有屑鉄の予熱方法。
4. The cooling gas is introduced in the vicinity of the exhaust gas outlet of the scrap iron preheating device, and the exhaust gas temperature in the vicinity of the exhaust gas outlet is set to 200 ° C. or lower.
The method for preheating chlorine-containing scrap iron according to any one of 1.
JP24921296A 1996-08-30 1996-08-30 Preheating method for chlorine-containing scrap iron Expired - Fee Related JP3461090B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP24921296A JP3461090B2 (en) 1996-08-30 1996-08-30 Preheating method for chlorine-containing scrap iron

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP24921296A JP3461090B2 (en) 1996-08-30 1996-08-30 Preheating method for chlorine-containing scrap iron

Publications (2)

Publication Number Publication Date
JPH1072614A JPH1072614A (en) 1998-03-17
JP3461090B2 true JP3461090B2 (en) 2003-10-27

Family

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Country Link
JP (1) JP3461090B2 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4828211B2 (en) * 2005-11-25 2011-11-30 新日本製鐵株式会社 Steelmaking method and refining equipment for steelmaking

Also Published As

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JPH1072614A (en) 1998-03-17

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