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JP2008081845A - Method for treating slag containing chrome steel - Google Patents

Method for treating slag containing chrome steel Download PDF

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JP2008081845A
JP2008081845A JP2007278256A JP2007278256A JP2008081845A JP 2008081845 A JP2008081845 A JP 2008081845A JP 2007278256 A JP2007278256 A JP 2007278256A JP 2007278256 A JP2007278256 A JP 2007278256A JP 2008081845 A JP2008081845 A JP 2008081845A
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slag
chromium
refining
steel
containing steel
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Atsushi Mizukami
敦嗣 水上
Hidekazu Todoroki
秀和 轟
Teruaki Ishii
照彰 石井
Shinichi Nagashima
信一 長島
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Nippon Yakin Kogyo Co Ltd
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Abstract

【課題】含クロム鋼の炉外精錬に当たり、この精錬時に多量に発生するスラグに対し、該スラグ中に含まれるクロムを三価の状態に固定する含クロム鋼精錬スラグの処理方法について提案する。
【解決手段】含クロム鋼をAODまたはVODで炉外精錬する時に発生するスラグについて、このスラグの塩基度をCaO/SiO>1.2に調整することによって、クロムの還元を導いて、三価のクロム酸化物Crが濃度を3.0wt%以下にし、その後、精錬後の含クロム溶鋼を、排滓後のスラグが大気にさらされる面積を示す、スラグ湯面面積(Sm)とスラグ容積(Vm)との比(S/Vm−1)が4以下である容器中に排滓する含クロム鋼精錬スラグの処理方法。
【選択図】なし
A chromed steel refining slag treatment method is proposed in which chromium contained in a slag is fixed in a trivalent state with respect to slag generated in a large amount during refining of chromium-containing steel.
For slag generated when refining chromium-containing steel by AOD or VOD, the reduction of chromium is induced by adjusting the basicity of the slag to CaO / SiO 2 > 1.2. The slag hot water surface area (Sm 2) indicates that the valent chromium oxide Cr 2 O 3 has a concentration of 3.0 wt% or less, and then the smelted chromium-containing molten steel is exposed to the atmosphere. ) And the slag volume (Vm 3 ) ratio (S / Vm −1 ) of 4 or less, the method for treating chrome-containing steel refining slag discharged in a vessel.
[Selection figure] None

Description

本発明は、含クロム鋼を炉外精錬する工程において、このときに発生するスラグの処理方法に関し、とくに、土木材料や建築材料などの資源として再利用できるスラグを生成させるための技術を提案する。   The present invention relates to a method for treating slag generated at the time of smelting chromium-containing steel outside the furnace, and in particular, proposes a technique for generating slag that can be reused as resources such as civil engineering materials and building materials. .

ステンレス鋼を典型例とする含クロム鋼は、一般に、電気炉で溶解した後、AOD法およびVOD法等の炉外精錬を経て製造され、それぞれの段階でスラグを発生する。こうしたスラグは、精錬工程において、主として脱酸剤、脱硫材および脱燐材の添加により、溶鋼中に含まれる不純物(C、O、S、Pおよび非金属介在物)の除去に伴って発生し、とくに含クロム鋼の場合、スラグ中にCrが含まれる。その他の成分として、溶鋼中のSiやAl等が、脱酸工程およびCrの還元時に酸化されてSiOやAl等の酸化物となり、炉または取鍋等の耐火物を保護する目的で添加されるCaOやMgO等とともに溶融スラグを形成する。 Chromium-containing steels, typically stainless steel, are generally produced by melting in an electric furnace and then subjected to out-of-furnace refining such as AOD method and VOD method, and generate slag at each stage. Such slag is generated during removal of impurities (C, O, S, P, and non-metallic inclusions) contained in the molten steel mainly by the addition of a deoxidizing agent, a desulfurizing material and a dephosphorizing material. In particular, in the case of chromium-containing steel, Cr 2 O 3 is contained in the slag. As other components, Si, Al, etc. in the molten steel are oxidized during the deoxidation process and reduction of Cr 2 O 3 to become oxides such as SiO 2 , Al 2 O 3, etc. A molten slag is formed together with CaO or MgO added for the purpose of protection.

とくに、ステンレス鋼のような含クロム鋼の炉外精錬においては、脱炭用の酸素吹き込み期において、溶鋼中のクロムの一部が酸化されてクロム酸化物を生成し、前記溶融スラグ中に移行することが知られている。そのため、通常、精錬工程の末期において、クロム酸化物の還元処理を行なうが、どうしても一部のクロム酸化物がスラグ中に残存してしまい、こうしたスラグを有価資源として路盤材等に再利用できない場合があった。   In particular, in the out-of-core refining of chromium-containing steel such as stainless steel, part of chromium in molten steel is oxidized during the oxygen blowing stage for decarburization to produce chromium oxide, which is transferred into the molten slag. It is known to do. For this reason, reduction treatment of chromium oxide is usually performed at the end of the refining process, but some of the chromium oxide remains in the slag, and such slag cannot be reused as roadside material as a valuable resource. was there.

しかしながら、近年、廃棄物の低減や天然資源の枯渇等の問題点から、このようなスラグを土木向け材料等として再利用することが注目されるようになってきた。   However, in recent years, attention has been focused on reusing such slag as a material for civil engineering due to problems such as reduction of waste and depletion of natural resources.

そのため、こうしたクロム酸化物含有スラグの処理の方法について様々な検討が行なわれてきた。たとえば、排出スラグから六価クロムが溶出するのを防止する方法として、特許文献1、特許文献2および特許文献3など、多数の技術が開示がされている。しかしならが、これらの方法はいずれも、炉外に排出したスラグを高温で還元処理する方法やそのスラグをBa塩等を添加し処理する方法であり、処理コストが高く、しかも大量の排滓スラグを処理する方法ではないため、多量に発生する含クロム鋼スラグの処理方法としては不向きであった。   For this reason, various studies have been made on methods for treating such chromium oxide-containing slag. For example, as a method for preventing elution of hexavalent chromium from exhaust slag, many techniques such as Patent Document 1, Patent Document 2, and Patent Document 3 are disclosed. However, both of these methods are a method of reducing slag discharged outside the furnace at a high temperature and a method of processing the slag by adding Ba salt or the like, which has a high processing cost and a large amount of waste. Since it is not the method of processing slag, it was unsuitable as a processing method of chromium-containing steel slag generated in large quantities.

また、特許文献4および特許文献5には、含クロム鋼スラグの再資源化処理を溶解−精錬工程で行なうことが提案されている。しかし、これらの方法は、排滓後のスラグ冷却過程も十分に制御しないと資源として再利用できない場合があり、スラグ処理方法として、なお不十分であった。
特開昭48-71371号公報 特開昭52-152651号公報 特開平5-345658号公報 特開平8-302418号公報 特開平8-295917号公報
Further, Patent Document 4 and Patent Document 5 propose that the recycling treatment of chromium-containing steel slag is performed in a melting-refining process. However, these methods may not be reused as resources unless the slag cooling process after evacuation is sufficiently controlled, and are still insufficient as a slag treatment method.
JP-A-48-71371 Japanese Patent Laid-Open No. 52-152651 JP-A-5-345658 JP-A-8-302418 Japanese Patent Laid-Open No. 8-29517

そこで、本発明は、従来技術が抱えている上述した実情に鑑み、含クロム鋼の炉外精錬に当たり、この精錬時に多量に発生するスラグに対し、該スラグ中に含まれるクロムを三価の状態に固定する含クロム鋼精錬スラグの処理方法について提案する。   Therefore, in view of the above-mentioned situation that the prior art has, the present invention is a trivalent state of chromium contained in the slag with respect to the slag generated in large quantities during the refining of chromium-containing steel. This paper proposes a method for treating smelting slag containing chromium.

発明者らは、含クロム鋼精錬スラグを、再資源化する上で最大の課題が、このスラグ中に含まれる三価のクロム酸化物の一部がさらに酸化され、六価のクロム酸化物に変化することにあるという認識の下で、その課題解決のために鋭意研究を行なった。その結果、三価のクロム酸化物は、大気中の酸素およびスラグ中に含まれる遊離酸素イオンとの反応によって酸化され、六価のクロム酸化物に変化することをつきとめ、そして、この遊離酸素イオンの最大の供給源が、未滓化CaOであることも突き止めた。   The inventors have the biggest problem in recycling chromed steel refining slag, and some of the trivalent chromium oxide contained in this slag is further oxidized to form hexavalent chromium oxide. Under the recognition that there is a change, we conducted diligent research to solve the problem. As a result, it was found that trivalent chromium oxide was oxidized by reaction with free oxygen ions contained in atmospheric oxygen and slag, and changed into hexavalent chromium oxide. It has also been determined that the largest source of is undehydrated CaO.

本発明は、このような知見の下に開発されたものであって、含クロム鋼をAODまたはVODで炉外精錬する時に発生するスラグについて、このスラグの塩基度をCaO/SiO>1.2に調整することによって、クロムの還元を導いて、三価のクロム酸化物Crが濃度を3.0wt%以下にし、その後、精錬後の含クロム溶鋼を、排滓後のスラグが大気にさらされる面積を示す、スラグ湯面面積(Sm)とスラグ容積(Vm)との比(S/Vm−1)が4以下である容器中に排滓することを特徴とする含クロム鋼精錬スラグの処理方法である。 The present invention has been developed based on such knowledge, and the basicity of slag generated when refining chromium-containing steel by AOD or VOD is set to CaO / SiO 2 > 1. By adjusting to 2, the reduction of chromium is led, the concentration of the trivalent chromium oxide Cr 2 O 3 is 3.0 wt% or less, and then the refined chromium-containing molten steel is replaced with the slag after being discharged. The slag surface area (Sm 2 ) and the slag volume (Vm 3 ) ratio (S / Vm −1 ), which indicates the area exposed to the atmosphere, is discharged into a container having 4 or less. It is the processing method of chromium steel refining slag.

なお、本発明において、クロムの還元処理はその還元後のCr濃度で5wt%以下にすること、排滓時の溶鋼温度を1550℃以上にすること、および上記スラグを不活性ガス雰囲気下において冷却すること、が望ましい。 In the present invention, the reduction treatment of chromium is 5 wt% or less in the Cr 2 O 3 concentration after the reduction, the molten steel temperature at the time of exhausting is 1550 ° C. or more, and the slag is treated with an inert gas atmosphere. It is desirable to cool down.

以上述べたように、本発明によれば、含クロム鋼の炉外精錬に当たり、この精錬時に多量に発生するスラグ中に含まれるクロム酸化物のほとんどを、三価に固定することができ、資源としての有効利用が可能となった。   As described above, according to the present invention, in the refining of chromium-containing steel, most of the chromium oxide contained in the slag generated in large quantities during this refining can be fixed to trivalent, Effective use is possible.

上述したとおり、ステンレス鋼のような含クロム鋼の炉外精錬においては、精錬工程の脱炭用の酸素吹き込み期において、溶鋼中のクロムが酸化され、Crが生成する。このCrは、還元剤として添加されるSiやAlなどの酸化物およびフラックスとして添加されるCaOやMgOなどと共にクロム酸化物を含む精錬スラグを生成する。 As described above, in the out-of-furnace refining of chromium-containing steel such as stainless steel, chromium in the molten steel is oxidized and Cr 2 O 3 is generated in the oxygen blowing period for decarburization in the refining process. This Cr 2 O 3 generates refined slag containing chromium oxide together with oxides such as Si and Al added as a reducing agent and CaO and MgO added as a flux.

上記含クロム精錬スラグに関し、発明者らは、まず、スラグ中に含まれる遊離酸素イオンを主因とする六価のクロム酸化物の生成機構について研究を行なった。その結果、含クロム精錬スラグ中に遊離のCaOおよびCrが存在すると、精錬の高温期で生成したCaO・Crが生成し、これがその後のスラグ冷却過程において、未滓化CaOから発生する遊離酸素イオンによって酸化され、下記(1)式に示す相変態を起こし、六価のクロム酸化物であるCaCrOを生成することを知見した。
2CaO+2CaO・Cr+3O → 4CaCrO・・・(1)
With respect to the chromium-containing refining slag, the inventors first studied the mechanism of formation of hexavalent chromium oxide mainly caused by free oxygen ions contained in the slag. As a result, when free CaO and Cr 2 O 3 are present in the chromium-containing refining slag, CaO · Cr 2 O 3 formed in the high temperature phase of refining is generated, and this is the undehydrated CaO in the subsequent slag cooling process. It has been found that it is oxidized by free oxygen ions generated from the above and undergoes a phase transformation represented by the following formula (1) to produce CaCrO 4 which is a hexavalent chromium oxide.
2CaO + 2CaO · Cr 2 O 3 + 3O 2 → 4CaCrO 4 (1)

そこで、発明者らは、六価のクロム酸化物が生成しないようにするには、上記(1)式の酸化反応を防止する方法が有効であるとの考えの下で、上記酸化反応の次のような抑制機構に想到した。即ち、前記炉外精錬スラグの塩基度CaO/SiO(以下、単にC/Sと略記する。)を、1.2以上に調整すると、溶鋼中に含まれるSi等が還元剤として働き、スラグ中の三価のクロム酸化物Crが還元され、メタルのCrとして回収されることがわかった。その結果、スラグ中のCr濃度が低下し、六価のクロム酸化物の生成が抑制されるようになる。とくに限定する必要はないが、還元後の含クロム溶鋼中のCr濃度は、3.0wt%以下とする。より好ましくは、1.2wt%以下とする。また、Crの還元を促進させる目的で還元剤を添加する場合には、Crよりも酸素との親和力の強いSi、AlおよびMn等を添加することが好ましい。 Therefore, the inventors have considered that the method of preventing the oxidation reaction of the above formula (1) is effective in preventing the formation of hexavalent chromium oxide, and the following of the above oxidation reaction. I came up with a suppression mechanism like That is, when the basicity CaO / SiO 2 (hereinafter simply abbreviated as C / S) of the out-of-furnace slag is adjusted to 1.2 or more, Si contained in the molten steel acts as a reducing agent, and slag It was found that the trivalent chromium oxide Cr 2 O 3 therein was reduced and recovered as metal Cr. As a result, the Cr 2 O 3 concentration in the slag is reduced, and the production of hexavalent chromium oxide is suppressed. Not particularly need to be limited to, Cr 2 O 3 concentration in the chromium-containing molten steel after reduction is less 3.0 wt%. More preferably, it is 1.2 wt% or less. In addition, when a reducing agent is added for the purpose of promoting the reduction of Cr 2 O 3 , it is preferable to add Si, Al, Mn, etc. having a stronger affinity for oxygen than Cr.

なお、排滓時の温度不足や攪拌不足等によりCaOが滓化不良となった場合にも、未滓化CaOの周辺が局部的に高C/Sになるため、SiOによるCaOの滓化効果が小さくなって、六価のクロム酸化物が生成しやすくなる。そのため、とくに限定されないが、排滓前の溶鋼温度は1550℃以上とすることが好ましい。より好ましくは、1570℃以上である。また、スラグ中に含まれる三価のクロム酸化物Cr自体の濃度を低減するためには、Crよりも酸素との親和力の強いSi、AlおよびMn等の還元剤を添加することが好ましい。 Even when the CaO becomes slag formation failure due to a temperature insufficient or stirring shortage during Haikasu, since the periphery of the non-slag formation CaO becomes locally high C / S, the CaO by SiO 2 slag formation The effect is reduced, and hexavalent chromium oxide is easily generated. Therefore, although it is not particularly limited, it is preferable that the molten steel temperature before waste is 1550 ° C. or higher. More preferably, it is 1570 degreeC or more. Further, in order to reduce the concentration of the trivalent chromium oxide Cr 2 O 3 itself contained in the slag, it is possible to add a reducing agent such as Si, Al and Mn, which has a stronger affinity for oxygen than Cr. preferable.

次に、大気中の酸素を主因とする六価のクロム酸化物の生成機構について説明する。排滓後にスラグが大気にさらされる面積を、できるだけ小さくすれば、上記(1)式に示す反応を抑制し、六価のクロム酸化物の生成を抑制できることに想到した。   Next, the production mechanism of hexavalent chromium oxide mainly caused by atmospheric oxygen will be described. It has been conceived that the reaction shown in the above formula (1) can be suppressed and the production of hexavalent chromium oxide can be suppressed by reducing the area of the slag exposed to the atmosphere as much as possible after evacuation.

すなわち、スラグ湯面面積(S)とスラグ容積(V)の比率(S/V)を表1に示すところから明らかなとおり1.8以上4以下に調整すると、スラグ容量に対して、大気にさらされる面積が十分に小さく、上記(1)式による反応が進むようなことがなく、たとえスラグ中に三価クロム化合物Crが含有されていても、三価のまま固定され、六価のクロム酸化物の生成を阻止することができる。ここで、S/Vを4以下に限定した理由は、S/Vが4より大きい場合、スラグ容積に対して大気にさらされる面積が大きく、条件によっては六価のクロム酸化物が生成する場合があるためである。 That is, when the ratio (S / V) of the slag hot water surface area (S) to the slag volume (V) is adjusted to 1.8 or more and 4 or less as is apparent from Table 1, the slag capacity is reduced to the atmosphere. The exposed area is sufficiently small so that the reaction according to the above formula (1) does not proceed. Even if the trivalent chromium compound Cr 2 O 3 is contained in the slag, the trivalent chromium compound is fixed as it is. Formation of valent chromium oxide can be prevented. Here, the reason why S / V is limited to 4 or less is that when S / V is larger than 4, the area exposed to the atmosphere is large with respect to the slag volume, and depending on conditions, hexavalent chromium oxide is generated. Because there is.

さらに、大気による酸化を防ぐため、排滓スラグをスラグポット等の容器に受け、不活性ガス雰囲気下にて冷却することが好ましい。具体的には、不活性ガスの吹き付けや、不活性ガスで満たされた容器内で冷却することなどが挙げられる。不活性ガスの種類としては、とくに限定されないが、アルゴン、窒素、ヘリウムおよび二酸化炭素等が好適である。なお、容器を不活性ガスで満たし、密閉するため、スラグポット上に蓋をすることが好ましい。   Furthermore, in order to prevent oxidation by the atmosphere, it is preferable that the waste slag is received in a container such as a slag pot and cooled in an inert gas atmosphere. Specific examples include blowing an inert gas and cooling in a container filled with an inert gas. The type of the inert gas is not particularly limited, but argon, nitrogen, helium, carbon dioxide and the like are preferable. In order to fill and seal the container with an inert gas, it is preferable to cover the slag pot.

含クロム鋼原料のAOD法またはVOD法による炉外精錬時に生成するスラグの塩基度および冷却条件を種々に変化させ、精錬スラグを作製した。なお、実機での操業において極端に各条件を変更すると、操業上の不具合を引き起こす場合があるため、一部(比較例)については、実験室にて少量のスラグを作製した。   Refined slag was produced by variously changing the basicity and cooling conditions of the slag produced during out-of-furnace refining of chromium-containing steel raw materials by the AOD method or VOD method. In addition, when each condition is changed extremely in operation with an actual machine, there may be a problem in operation. For some (comparative example), a small amount of slag was produced in the laboratory.

作製した各精錬スラグについて、六価のクロムの溶出量を土壌環境基準の検定方法である環境庁告示46号に基づいて測定した。さらに、スラグ組成については、蛍光X線回折により、また、未滓化CaOの有無については、サンプリングした試料のミクロ観察によって特定した。その結果を表1に示す。   About each produced refined slag, the elution amount of hexavalent chromium was measured based on the environmental agency notification No. 46 which is the verification method of a soil environmental standard. Furthermore, the slag composition was specified by fluorescent X-ray diffraction, and the presence or absence of undehydrated CaO was specified by micro-observation of the sampled sample. The results are shown in Table 1.

Figure 2008081845
Figure 2008081845

表1に示されている実験結果によれば、六価のクロムの溶出が検出されていないため、スラグ中のクロムが三価に固定されていることがわかる。しかしながら、比較例では、少なくとも1つ以上が、本発明で規定する範囲を外れているため、ごく微量の六価クロムが溶出している。   According to the experimental results shown in Table 1, since elution of hexavalent chromium is not detected, it can be seen that chromium in the slag is fixed to trivalent. However, in the comparative example, since at least one or more is out of the range defined in the present invention, a very small amount of hexavalent chromium is eluted.

Claims (4)

含クロム鋼をAODまたはVODで炉外精錬する時に発生するスラグについて、このスラグの塩基度をCaO/SiO>1.2に調整することによって、クロムの還元を導いて、三価のクロム酸化物Crが濃度を3.0wt%以下にし、その後、精錬後の含クロム溶鋼を、排滓後のスラグが大気にさらされる面積を示す、スラグ湯面面積(Sm)とスラグ容積(Vm)との比(S/Vm−1)が4以下である容器中に排滓することを特徴とする含クロム鋼精錬スラグの処理方法。 For slag generated when refining chromium-containing steel with AOD or VOD, by adjusting the basicity of this slag to CaO / SiO 2 > 1.2, the reduction of chromium was led to trivalent chromium oxidation. The slag hot water surface area (Sm 2 ) and slag volume indicate the area in which the product Cr 2 O 3 has a concentration of 3.0 wt% or less, and the smelted chromium-containing molten steel is then exposed to the atmosphere. A method for treating chrome-containing steel refining slag, characterized in that it is discharged into a container having a ratio (S / Vm -1 ) to (Vm 3 ) of 4 or less. クロムの還元処理は、その還元後のCr濃度で1.2wt%以下にすることである請求項1に記載の含クロム鋼精錬スラグの処理方法。 The method for treating chromium-containing steel refining slag according to claim 1, wherein the reduction treatment of chromium is to reduce the Cr 2 O 3 concentration after the reduction to 1.2 wt% or less. 排滓時の溶鋼温度を1550℃以上にすることを特徴とする請求項1または2に記載の含クロム鋼精錬スラグの処理方法。 The method for treating a chrome-containing steel refining slag according to claim 1 or 2, wherein the molten steel temperature at the time of waste is set to 1550 ° C or higher. 上記スラグを、不活性ガス雰囲気下において冷却することを特徴とする請求項1〜3のいずれか1に記載の含クロム鋼精錬スラグの処理方法。 The said slag is cooled in inert gas atmosphere, The processing method of chromium-containing steel refining slag of any one of Claims 1-3 characterized by the above-mentioned.
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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2011174166A (en) * 2009-10-01 2011-09-08 Kobe Steel Ltd Method for reusing oxidized slag and recycling slag
JP2016196389A (en) * 2015-04-06 2016-11-24 株式会社神戸製鋼所 Method for suppressing hexavalent chromium elution from slag

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Publication number Priority date Publication date Assignee Title
JPS63140044A (en) * 1986-12-02 1988-06-11 Nisshin Steel Co Ltd Treatment of slag generated in refining of stainless steel
JP2001335823A (en) * 2000-05-30 2001-12-04 Sumitomo Metal Ind Ltd Detoxification method of stainless steel slag
JP2002053351A (en) * 2000-08-07 2002-02-19 Sumitomo Metal Ind Ltd Detoxifying stainless slag and its manufacturing method

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63140044A (en) * 1986-12-02 1988-06-11 Nisshin Steel Co Ltd Treatment of slag generated in refining of stainless steel
JP2001335823A (en) * 2000-05-30 2001-12-04 Sumitomo Metal Ind Ltd Detoxification method of stainless steel slag
JP2002053351A (en) * 2000-08-07 2002-02-19 Sumitomo Metal Ind Ltd Detoxifying stainless slag and its manufacturing method

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2011174166A (en) * 2009-10-01 2011-09-08 Kobe Steel Ltd Method for reusing oxidized slag and recycling slag
JP2016196389A (en) * 2015-04-06 2016-11-24 株式会社神戸製鋼所 Method for suppressing hexavalent chromium elution from slag

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