JPH1136007A - Method of discharging slag generated during stainless steel production and method of recycling slag - Google Patents
Method of discharging slag generated during stainless steel production and method of recycling slagInfo
- Publication number
- JPH1136007A JPH1136007A JP19234597A JP19234597A JPH1136007A JP H1136007 A JPH1136007 A JP H1136007A JP 19234597 A JP19234597 A JP 19234597A JP 19234597 A JP19234597 A JP 19234597A JP H1136007 A JPH1136007 A JP H1136007A
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- JP
- Japan
- Prior art keywords
- slag
- furnace
- coolant
- stainless steel
- smelting reduction
- 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.)
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Links
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Abstract
(57)【要約】
【課題】本発明は、脱炭炉や搬送容器からの排滓を容易
にするステンレス鋼製造時に発生するスラグの排滓方
法、及びその方法で排滓されたスラグの再利用方法を提
供することを目的としている。
【解決手段】転炉型溶融還元炉内の溶銑に、クロム原料
及び焼石灰を投入し、別途投入した炭材を酸化性ガスで
燃焼せしめて熱を発生させ、該クロム原料を溶融還元
し、次いで、生成した含クロム粗溶鋼を、別の転炉型脱
炭炉内に移行して脱炭精錬を行いステンレス鋼を製造す
るに際し、前記脱炭炉内で発生したスラグに、冷却材/
スラグの体積比が0.2以上となるように、スラグの冷
却材を投入し、該スラグの凝集を抑制しながら混合及び
冷却、固化させた後のスラグを搬送容器へ排滓する。
(57) [Summary] The present invention provides a method of discharging slag generated during the production of stainless steel, which facilitates the discharge of waste from a decarburization furnace or a transport container, and a method of recycling slag discharged by the method. It is intended to provide usage. SOLUTION: A chromium raw material and calcined lime are charged into hot metal in a converter type smelting reduction furnace, and a separately charged carbon material is burned with an oxidizing gas to generate heat, thereby melting and reducing the chromium raw material, Next, the produced chromium-containing crude molten steel is transferred to another converter type decarburizing furnace to perform decarburization refining to produce stainless steel, and the slag generated in the decarburizing furnace is supplied with a coolant /
A coolant for the slag is charged so that the volume ratio of the slag is 0.2 or more, and the slag after mixing, cooling, and solidifying is discharged to a transport container while suppressing aggregation of the slag.
Description
【0001】[0001]
【発明の属する技術分野】本発明は、ステンレス鋼製造
時に発生するスラグの排滓方法及び排滓スラグの再利用
方法に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for discharging slag generated during the production of stainless steel and a method for recycling slag.
【0002】[0002]
【従来の技術】最近、ステンレス鋼の製造コストを低減
するため、従来使用していた高価なフェロクロム合金、
あるいは還元ペレットに代え、安価なクロム鉱石を直接
使用することが行われるようになった。すなわち、特公
平4−38806号公報が開示したように、「機能の異
なる2基の転炉を用い、1基目の転炉で溶銑に粉状クロ
ム鉱石を投入し、該鉱石を炭材で溶融還元してステンレ
ス鋼製造用母溶湯を吹錬し、該母溶湯を2基目の転炉で
通常通りの脱炭精錬を行ってステンレス鋼を製造する方
法」である。その際、2基目の脱炭炉でも、酸化クロム
を含有したスラグが発生するので、このスラグから高価
なクロムを回収する必要がある。現在は、前記脱炭炉か
らスラグを搬送容器(取鍋)に排滓し、該容器を介して
最初の溶融還元炉へ戻し、再び溶融還元でステンレス鋼
用母溶湯中に回収する方法を採用している。2. Description of the Related Art Recently, expensive ferrochrome alloys conventionally used to reduce the manufacturing cost of stainless steel,
Alternatively, inexpensive chromium ore has been used directly instead of reduced pellets. That is, as disclosed in Japanese Patent Publication No. 4-38806, "using two converters having different functions, powdered chromium ore is charged into hot metal in the first converter, and the ore is made of carbonaceous material. A method of producing a stainless steel by melt-reducing and blowing a molten metal for producing stainless steel, and subjecting the molten metal to decarburization and refining as usual in a second converter. At that time, slag containing chromium oxide is generated even in the second decarburization furnace, and it is necessary to recover expensive chromium from this slag. At present, a method is adopted in which slag is discharged from the decarburization furnace into a transfer vessel (ladle), returned to the first smelting reduction furnace via the vessel, and then recovered again in the molten metal for stainless steel by smelting reduction. doing.
【0003】しかしながら、前記1基目の脱炭炉からの
スラグを受け入れた搬送容器内で、クロム酸化物が冷却
固化してしまい、スラグが大きな固形物となる。そのた
め、該脱炭炉から搬送容器へ排滓したり、あるいは該容
器から最初の溶融還元用炉へスラグを戻そうにも、凝集
したスラグが炉壁や容器壁に引っかかったり、へばり付
いて全量排出できない。また、この排出不良は、高価な
クロムの回収量減少になるばかりでなく、搬送容器内に
残留したスラグの処理というやっかいな問題を起こす。[0003] However, chromium oxide is cooled and solidified in the transfer container that receives the slag from the first decarburization furnace, and the slag becomes a large solid. For this reason, even if the slag is discharged from the decarburizing furnace to the transfer container, or the slag is returned from the container to the first smelting reduction furnace, the agglomerated slag is caught on the furnace wall or the container wall or sticks to the furnace wall. Not all emissions. In addition, this poor discharge not only reduces the amount of expensive chromium recovered, but also causes a troublesome problem of treating slag remaining in the transport container.
【0004】また、近年、ステンレス鋼のすべて鋼種に
高品質が求められ、それに応じて製鋼工程でも様々な精
錬方法が開発され、実用化されている。ところが、それ
ら精錬方法は、造滓材を従来より多量に使用するので、
精錬副産物であるスラグの処理が大きな問題となってい
る。そのため、造滓材使用量の低減やスラグの再使用方
法に関する技術開発が盛に行われるようになった。[0004] In recent years, high quality has been demanded for all types of stainless steel, and various refining methods have been developed and put to practical use in the steelmaking process accordingly. However, these refining methods use a larger amount of slag-making material than before,
The treatment of slag, a by-product of smelting, is a major problem. For this reason, technical development on the reduction of the amount of slag-making material used and the method of reusing slag has been actively carried out.
【0005】例えば、特公昭58−31362号公報
は、「前チャージの溶融スラグを炉内に残留させて、次
チャージの造滓材の一部として再利用する製鋼法」を提
案している。また、特公昭62−50543号公報は、
「ステンレス鋼製造時に発生する酸化クロムを含有する
スラグを、上底吹転炉型反応器内で安価な炭材を用いて
溶融還元することによりクロム分を還元回収する方法」
を開示している。For example, Japanese Patent Publication No. 58-31362 proposes a "steel making method in which molten slag of a previous charge is left in a furnace and reused as a part of a slag material of a next charge." Also, Japanese Patent Publication No. Sho 62-50543,
"A method for reducing and recovering chromium by melting and reducing slag containing chromium oxide generated during the production of stainless steel using an inexpensive carbon material in a top-bottom blower-type reactor"
Is disclosed.
【0006】しかしながら、特公昭58−31362号
公報記載の技術は、前チャージの溶融スラグを炉内に残
留させて、次チャージの造滓材の一部として再利用する
ので、次チャージでは炉内のスラグ量が増加することに
なる。吹錬に伴い溶鋼中のクロムは酸化されてスラグに
移行するが、該技術では、そのクロム酸化物を還元回収
するために、高価なFe−Siを多量に使用することに
なるという問題を有している。However, in the technique described in Japanese Patent Publication No. 58-31362, the molten slag of the previous charge is left in the furnace and reused as a part of the slag material of the next charge. Will increase the amount of slag. Chromium in molten steel is oxidized and transferred to slag with blowing, but this technique has a problem that a large amount of expensive Fe-Si is used to reduce and recover the chromium oxide. doing.
【0007】また、特公昭62−50543号公報記載
の技術を試行したが、通常の溶融還元よりも高温(例え
ば、1650℃以上)で酸素吹錬しないと、該スラグは
溶融しなかった。つまり、この技術には、溶融還元炉の
内張耐火物損耗を促進させ、炉寿命を低下させるという
問題が存在しているように思われた。Further, the technique described in Japanese Patent Publication No. Sho 62-50543 was tried, but the slag did not melt unless oxygen was blown at a higher temperature (for example, 1650 ° C. or higher) than ordinary smelting reduction. In other words, it seems that this technique has a problem of promoting the wear of the refractory lining of the smelting reduction furnace and shortening the furnace life.
【0008】[0008]
【発明が解決しようとする課題】本発明は、かかる事情
に鑑み、脱炭炉や搬送容器からの排滓を容易にするステ
ンレス鋼製造時に発生するスラグの排滓方法、及びその
方法で排滓されたスラグの再利用方法を提供することを
目的としている。SUMMARY OF THE INVENTION In view of such circumstances, the present invention provides a method of discharging slag generated during the production of stainless steel, which facilitates the discharge of waste from a decarburization furnace or a transport container, and a method of discharging slag generated by the method. The purpose of the present invention is to provide a method for reusing recycled slag.
【0009】[0009]
【課題を解決するための手段】発明者は、上記目的を達
成するため、脱炭炉や搬送容器から排滓し易いスラグの
状態を見いだすべく研究を行い、スラグを凝集させずに
冷却、固化し、粉粒状で、且つ所謂サラサラの状態にで
きれば良いとの結論を得た。そして、脱炭炉内で精錬終
了後のスラグをかかる状態にするための手段を鋭意検討
し、本発明を完成させた。Means for Solving the Problems In order to achieve the above object, the inventor conducted research to find a state of slag easily discharged from a decarburizing furnace or a transport container, and cooled and solidified without coagulating the slag. Then, it was concluded that it would be good if it could be made into a powdery and granular state, so-called smooth state. Means for making the slag after the completion of the refining in the decarburization furnace intensely studied, and completed the present invention.
【0010】すなわち、本発明は、転炉型溶融還元炉内
の溶銑に、クロム原料及び焼石灰を投入し、別途投入し
た炭材を酸化性ガスで燃焼せしめて熱を発生させ、該ク
ロム原料を溶融還元し、次いで、生成した含クロム粗溶
鋼を、別の転炉型脱炭炉内に移行して脱炭精錬を行いス
テンレス鋼を製造するに際し、前記脱炭炉内で発生した
スラグに、冷却材/スラグの体積比が0.2以上となる
ように、スラグの冷却材を投入し、該スラグの凝集を抑
制しながら混合及び冷却、固化させた後のスラグを搬送
容器へ排滓することを特徴とするステンレス鋼製造時に
発生するスラグの排滓方法である。That is, the present invention provides a chromium raw material in which a chromium raw material and calcined lime are charged into hot metal in a converter type smelting reduction furnace, and a separately charged carbon material is burned with an oxidizing gas to generate heat. Then, the resulting chromium-containing crude molten steel is transferred to another converter type decarburization furnace to perform decarburization refining to produce stainless steel, and slag generated in the decarburization furnace is produced. The slag coolant is supplied so that the volume ratio of the coolant / slag becomes 0.2 or more, and the slag after mixing, cooling, and solidifying while suppressing aggregation of the slag is discharged to a transport container. This is a method of discharging slag generated during the production of stainless steel.
【0011】また、本発明は、前記冷却材を、炭材とし
たり、あるいは焼石灰とすることを特徴とするステンレ
ス鋼製造時に発生するスラグの排滓方法である。さら
に、本発明は、前記冷却材の投入前に、脱炭炉で生成す
るスラグの塩基度(CaO/SiO2 )を1.8〜3.
0とすることを特徴とするステンレス鋼製造時に発生す
るスラグの排滓方法である。[0011] The present invention is also a method for discharging slag generated during the production of stainless steel, wherein the coolant is carbonaceous material or calcined lime. Further, according to the present invention, the basicity (CaO / SiO 2 ) of the slag generated in the decarburization furnace is set to 1.8 to 3.
This is a method for discharging slag generated during the production of stainless steel, characterized by being set to 0.
【0012】加えて、本発明は、前記のいずれかに記載
した方法で排滓したステンレス鋼製造時に発生したスラ
グを、前記転炉型溶融還元炉の溶銑に投入し、再度クロ
ム原料を溶融還元したり、その際の溶湯温度を1550
〜1650℃以下とすることを特徴とする排滓スラグの
再利用方法でもある。本発明によれば、脱炭炉内のスラ
グを粉粒状で、且つサラサラの状態になるので、該脱炭
炉や搬送容器からの排滓が円滑になる。その結果、脱炭
炉で生成したスラグ中の高価なクロムは、すべて回収さ
れるようになり、ステンレス鋼の製造コストの低減が達
成できる。また、本発明では、スラグの冷却材を、溶融
還元でも副原料として使用される炭材や焼石灰としたの
で、それらが排滓スラグの再利用方法において有効に使
用され、無駄にならない。さらに、溶融還元炉の内張耐
火物の損耗が抑制され、炉寿命の延長が達成できる。冷
材としては、特に、溶融還元炉の操業で必須であり、増
量に実質的に規制がないコークスを代表とする炭材が最
適である。一方、石灰も使用できるが、炭材より比重が
大きく実質的に炭材より多量に使用せねばならないこと
と、スラグと同時に固化した石灰は滓化が遅れることを
配慮すると、炭材よりも使用が限定される。従って、本
発明では、炭材と石灰とを適宜混合して使用するのが好
ましい。[0012] In addition, the present invention provides a method of smelting and reducing the chromium raw material again by charging the slag generated during the production of stainless steel discharged by any of the above methods into the hot metal of the converter type smelting reduction furnace. Or the melt temperature at that time is 1550
It is also a method of reusing waste slag characterized by being at most 161650 ° C. or lower. According to the present invention, since the slag in the decarburization furnace is in a granular state and in a smooth state, the waste from the decarburization furnace and the transport container is smooth. As a result, all of the expensive chromium in the slag generated in the decarburization furnace is recovered, and a reduction in the production cost of stainless steel can be achieved. In the present invention, since the slag coolant is a carbon material or calcined lime used as an auxiliary material even in smelting reduction, they are effectively used in the waste slag recycling method and are not wasted. Further, the wear of the refractory lining of the smelting reduction furnace is suppressed, and the furnace life can be extended. As the cold material, particularly, a carbon material, which is indispensable for the operation of the smelting reduction furnace and represented by coke, which has substantially no restriction on the increase, is most suitable. On the other hand, lime can be used, but given that it has a higher specific gravity than carbon and must be used in a larger amount than carbon, and that lime solidified at the same time as slag delays slagging, Is limited. Therefore, in the present invention, it is preferable to appropriately mix and use the carbonaceous material and the lime.
【0013】なお、本発明では、冷却材の投入量を冷却
材/スラグの体積比で求めたが、該スラグの体積は、嵩
比重を2.5t/m3 とし、冷却材の体積は、炭材や焼
石灰に固有の嵩比重を使用して計算している。例えば、
小塊コークス(粒度10〜25mm)や焼石灰(粒度5
〜20mm)を本発明の実施に用いる場合、それらの嵩
比重はそれぞれ0.5t/m3 及び1.0t/m3 であ
った。In the present invention, the input amount of the coolant is determined by the volume ratio of the coolant / slag, and the volume of the slag is set to a bulk specific gravity of 2.5 t / m 3 and the volume of the coolant is Calculated using the specific gravity of the bulk material of charcoal and calcined lime. For example,
Small coke (grain size 10 to 25 mm) and calcined lime (grain size 5
2020 mm) were used in the practice of the invention, their bulk specific gravities were 0.5 t / m 3 and 1.0 t / m 3 , respectively.
【0014】[0014]
【発明の実施の形態】以下、発明をなすに至った経緯を
まじえて、本発明の実施の形態を説明する。まず、発明
者は、2基目の脱炭炉内に生成したスラグを、粉粒状
で、且つサラサラした状態に冷却、固化することを種々
検討した。その中で、図1に示す結果が最も好ましいも
のであった。すなわち、図1は、スラグの冷却材として
脱炭炉内に投入するものを炭材(具体的にはコークス)
とし、その添加量を、生成スラグとの体積比で定めて種
々変更し、1基目の溶融還元炉に戻すことができるスラ
グ量(スラグ回収率=(戻しスラグ重量/生成スラグ重
量)×100で表わす)の変化を調べたものである。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The embodiments of the present invention will be described below, taking into account the circumstances leading to the invention. First, the inventor studied various ways to cool and solidify the slag generated in the second decarburization furnace into a granular and smooth state. Among them, the result shown in FIG. 1 was the most preferable. That is, Fig. 1 shows that the material to be charged into the decarburization furnace as the slag coolant is carbon material (specifically, coke).
The amount of slag that can be variously changed by determining the amount of addition based on the volume ratio with the generated slag and returned to the first smelting reduction furnace (slag recovery rate = (weight of returned slag / weight of generated slag) × 100) (Represented by).
【0015】図1から明らかなように、スラグ中に含ま
れるクロム酸化物の有無にかかわらず、冷却材/スラグ
の体積比が0.2を境にして、添加する冷却材の効果が
異なっている。つまり、冷却材/スラグの体積比が0.
2未満にすると、冷却固化後にスラグの凝集が促進し、
スラグの搬送容器に引っかかったり、あるいはへばり付
き、脱炭炉で生成したスラグを溶融還元炉に全量戻すこ
とができなくなった。As is clear from FIG. 1, regardless of the presence or absence of chromium oxide contained in the slag, the effect of the added coolant differs at a coolant / slag volume ratio of 0.2. I have. That is, the volume ratio of the coolant / slag is 0.1.
When it is less than 2, slag aggregation is promoted after cooling and solidifying,
The slag was caught or stuck in the slag transport container, and the slag generated in the decarburization furnace could not be returned to the smelting reduction furnace in its entirety.
【0016】また、発明者は、使用できる冷却材の種類
を種々変更し、前記と同様の検討を行った。その結果、
炭材以外にも、溶融還元炉でCr鉱石の造滓材として使
用する焼石灰、MgOクリンカー、砂利や、レンガ屑、
ダスト、高炉滓等の産業廃棄物や製鉄所発生物等でも、
図1とほぼ同等の結果が得られた。そこで、発明者は、
これらの調査結果を本発明として具現化したのである。
なお、冷却材/スラグの体積比が0.2以上であれば、
上記効果が得られるので、該体積比には上限を設けてい
ない。しかし、0.2以上を超えると、その効果は飽和
するので、実際の操業では経済性の観点から該冷却材の
使用量を定めれば良い。また、冷却材としては、スラグ
を溶融還元炉に戻し、再利用することを妨げないもので
あることが重要である。The inventor made various changes in the types of coolants that can be used, and made the same study as described above. as a result,
In addition to charcoal, calcined lime, MgO clinker, gravel, brick debris,
Even industrial waste such as dust and blast furnace slag, and waste generated from steelworks,
Almost the same results as in FIG. 1 were obtained. Therefore, the inventor
These findings were embodied as the present invention.
If the volume ratio of the coolant / slag is 0.2 or more,
Since the above effects can be obtained, there is no upper limit on the volume ratio. However, if it exceeds 0.2 or more, the effect is saturated, so that the amount of the coolant to be used in actual operation may be determined from the viewpoint of economy. It is also important that the coolant does not prevent the slag from being returned to the smelting reduction furnace and reused.
【0017】さらに、発明者は、脱炭炉で生成するスラ
グの塩基度(=CaO/SiO2 )についての調査を行
った。理由は、脱炭炉と溶融還元炉の間でスラグをリサ
イクルするので、スラグ・ボリューム・アップに起因し
た脱炭炉でのCr酸化ロスの増加を抑制するためと、ス
ラグの排送容器のサイズを抑えるためである。その結
果、脱炭炉内でスラグの塩基度を3.0以下に制限する
のが妥当であると結論した。一方、脱炭炉内で脱炭精錬
の終了後に行う酸化クロムのFe−Siによる還元で、
溶鋼からの脱硫をも期待するには、前記スラグの塩基度
は1.8以上が必要となるので、本発明では、脱炭炉で
生成されるスラグの塩基度を1.8〜3.0の範囲にす
ることが好ましい。Further, the inventor investigated the basicity (= CaO / SiO 2 ) of the slag generated in the decarburization furnace. The reason is that slag is recycled between the decarburizing furnace and the smelting reduction furnace, so that the increase in Cr oxidation loss in the decarburizing furnace caused by the increase in slag volume and the size of the slag discharge container It is to suppress. As a result, it was concluded that it was appropriate to limit the slag basicity to 3.0 or less in the decarburization furnace. On the other hand, by the reduction of chromium oxide by Fe-Si performed after the decarburization refining in the decarburization furnace,
In order to expect desulfurization from molten steel, the basicity of the slag must be 1.8 or more. Therefore, in the present invention, the basicity of the slag generated in the decarburization furnace is set to 1.8 to 3.0. It is preferable to be within the range.
【0018】次に、発明者は、上記本発明に係る排滓方
法で得たスラグの溶融還元炉内での最適な再利用方法に
ついて検討した。理由は、特公昭62−50543号公
報記載の従来技術では、通常の溶融還元よりも高温(例
えば、1650℃以上)で酸素吹錬しないと、該スラグ
は溶融しなかった。つまり、スラグの再利用時には、溶
融還元炉の内張耐火物の損耗が促進し、炉寿命を低下さ
せるという問題が存在しているからである。Next, the inventor studied an optimal method of reusing the slag obtained by the above-described waste disposal method according to the present invention in a smelting reduction furnace. The reason is that in the prior art described in Japanese Patent Publication No. Sho 62-50543, the slag did not melt unless oxygen was blown at a higher temperature (for example, 1650 ° C. or higher) than ordinary smelting reduction. That is, when the slag is reused, there is a problem that the wear of the refractory lining of the smelting reduction furnace is promoted and the furnace life is shortened.
【0019】まず、発明者は、脱炭炉内で生成した溶融
スラグを、上記した本発明に係る排滓方法を採用して溶
融還元炉に戻し、再度クロム鉱石の溶融還元を行い、そ
の時の溶湯温度と溶融還元終了時のスラグ中のトータル
Cr濃度(以下、T.Crとする)との関係を調査し
た。その結果は、図2から明らかなように、脱炭炉から
のスラグにクロムが10wt%含有していても、溶湯温
度を1650℃程度にすれば、溶融還元吹錬終了時のス
ラグ中のT.Crを通常の溶融還元スラグと同レベルの
0.5wt%以下にできることがわかった。これは、上
記した本発明に係る排滓方法で、冷却材として投入した
炭材、造滓剤が有効に利用され、クロム鉱石の溶融還元
を円滑にしたためと思われる。First, the inventor returns the molten slag generated in the decarburization furnace to the smelting reduction furnace by employing the above-described waste method according to the present invention, and performs smelting reduction of chromium ore again. The relationship between the molten metal temperature and the total Cr concentration in the slag at the end of the smelting reduction (hereinafter referred to as T.Cr) was investigated. As is clear from FIG. 2, even if the slag from the decarburizing furnace contains 10 wt% of chromium, if the temperature of the molten metal is set to about 1650 ° C., the T . It has been found that Cr can be reduced to 0.5 wt% or less, which is the same level as ordinary smelting reduction slag. This is considered to be because the carbon material and the slag-making agent charged as the coolant were effectively used in the above-described slag discharge method according to the present invention, and the smelting reduction of chromium ore was smoothly performed.
【0020】また、これらの再利用操業時において溶融
還元炉の耐火物溶損状況を調査し、その結果を図3に示
す。図3から明らかなように、溶融還元時の溶湯温度が
1650℃を超えると、溶融還元炉の耐火物損耗(溶湯
温度1550℃の時の耐火物損耗速度を1とした指数で
表示)が激しくなることがわかる。また、1550℃未
満では、戻しスラグのT.Crが多い場合、溶融還元で
スラグ中に残るT.Crが多くなり、溶融還元が不十分
だからである。Further, during these recycling operations, the refractory erosion of the smelting reduction furnace was investigated, and the results are shown in FIG. As is clear from FIG. 3, when the temperature of the molten metal during the smelting reduction exceeds 1650 ° C., the refractory wear of the smelting reduction furnace (indicated by an index with the refractory wear rate at 1550 ° C. being 1) becomes severe. It turns out that it becomes. If the temperature is lower than 1550 ° C., the T.G. If there is a large amount of Cr, T.C. This is because Cr is increased and smelting reduction is insufficient.
【0021】そこで、発明者は、本発明に係る排滓方法
で得たスラグの溶融還元炉での再利用に際しては、溶湯
温度を1550〜1650℃の範囲とした。なお、脱炭
炉内で生成するスラグ中のT.Crは、できれば7wt
%以下に抑えることが好ましいようだ。Therefore, the inventor set the temperature of the molten metal in the range of 1550 to 1650 ° C. when reusing the slag obtained by the waste disposal method according to the present invention in the smelting reduction furnace. In addition, T.C. in slag generated in the decarburization furnace was used. Cr should be 7wt% if possible
% Seems to be preferable.
【0022】[0022]
【実施例】2基の転炉型反応容器を用い、ステンレス鋼
を製造し、その操業に本発明に係る排滓方法及び排滓ス
ラグの再利用方法を採用した。 (実施例1)2基目の脱炭炉を上底吹機能を有する16
0t転炉(K−BOP)とし、そこに1基目の溶融還元
炉で溶製した含クロム粗溶鋼を120t装入し、粗脱炭
を行った。その際、焼石灰やFe−Cr合金鉄を投入
し、粗脱炭終了後のステンレス溶鋼にトン当り13.1
kg/tのFe−Siを投入して、脱炭中に生成したス
ラグ中の酸化物を還元すると共に、溶鋼の脱硫を行っ
た。EXAMPLE Stainless steel was manufactured using two converter type reaction vessels, and the waste disposal method and the waste slag recycling method according to the present invention were employed for the operation. (Embodiment 1) A second decarburization furnace is provided with an upper-bottom blowing function.
A 0t converter (K-BOP) was set therein, and 120 ton of chromium-containing crude molten steel melted in the first smelting reduction furnace was charged therein, and crude decarburization was performed. At that time, calcined lime or Fe-Cr alloy iron was charged, and 13.1 per ton was added to the molten stainless steel after the rough decarburization.
kg / t of Fe-Si was charged to reduce oxides in the slag generated during the decarburization and desulfurize the molten steel.
【0023】脱炭精錬で生成したスラグの内訳は、Ca
O=10.4ton、SiO2 =5.2ton、Al2
O3 =1.0ton、MgO=1.6tonで、合計の
スラグ重量は18.2tonである。この合計重量を嵩
比重2.5t/m3 で除し、生成スラグの体積を7.2
8Nm3 とした。そして、本発明に係る排滓方法を採用
するため、冷却材として嵩比重0.5t/m3 のコーク
スを2.0ton使用することにした。つまり、冷却材
/スラグの体積比は0.55であった。The breakdown of the slag produced by the decarburization refining is Ca
O = 10.4 ton, SiO 2 = 5.2 ton, Al 2
O 3 = 1.0 ton, MgO = 1.6 ton, and the total slag weight is 18.2 ton. This total weight was divided by a bulk specific gravity of 2.5 t / m 3 to reduce the volume of the produced slag to 7.2.
8 Nm 3 . Then, in order to employ the waste disposal method according to the present invention, 2.0 tons of coke having a bulk specific gravity of 0.5 t / m 3 was used as a coolant. That is, the volume ratio of the coolant / slag was 0.55.
【0024】脱炭終了後、前記の生成スラグに、この体
積比に従いコークス粉を投入し、炉を揺動させてスラグ
と十分に混合して冷却、固化させた。その結果、スラグ
は、適度なサイズで、且つサラサラした状態になった。
そこで、該スラグを排送容器(取鍋)に排滓したとこ
ろ、ほぼ生成スラグの全量が円滑に回収できた。次に、
該排滓スラグを、1基目の溶融還元炉に装入し、別途装
入されている溶銑、クロム鉱石、焼石灰、炭材と共に溶
融還元を行った。その際、溶湯の温度は、1550℃に
なるように調整したところ、90分の吹錬時間で操業が
終了した。 (実施例2)2基目の脱炭炉を上底吹機能を有する16
0t転炉(K−BOP)とし、そこに1基目の溶融還元
炉で溶製した含クロム粗溶鋼を123t装入し、粗脱炭
を行った。その際、焼石灰やFe−Cr合金鉄を投入
し、粗脱炭終了後のステンレス溶鋼にトン当り10.3
kg/tのFe−Siを投入して、脱炭中に生成したス
ラグ中の酸化物を還元すると共に、溶鋼の脱硫を行っ
た。After the decarburization was completed, coke powder was charged into the produced slag in accordance with this volume ratio, and the furnace was shaken to sufficiently mix with the slag, and was cooled and solidified. As a result, the slag was in an appropriate size and smooth.
Then, when the slag was discharged into a discharge container (a ladle), almost all of the generated slag could be recovered smoothly. next,
The waste slag was charged into a first smelting reduction furnace, and smelting reduction was performed together with separately charged hot metal, chrome ore, calcined lime, and carbonaceous material. At that time, when the temperature of the molten metal was adjusted to 1550 ° C., the operation was completed in a blowing time of 90 minutes. (Embodiment 2) A second decarburization furnace is provided with a top-bottom blowing function.
A 0t converter (K-BOP) was used, and 123t of chromium-containing crude molten steel melted in the first smelting reduction furnace was charged therein, and crude decarburization was performed. At that time, calcined lime and Fe-Cr alloy iron were charged, and 10.3 / ton was added to the molten stainless steel after rough decarburization.
kg / t of Fe-Si was charged to reduce oxides in the slag generated during the decarburization and desulfurize the molten steel.
【0025】脱炭精錬で生成したスラグの内訳は、Ca
O=9.2ton、SiO2 =4.6ton、Al2 O
3 =0.7ton、MgO=1.4tonで、合計のス
ラグ重量は15.9tonである。この合計重量を嵩比
重2.5t/m3 で除し、生成スラグの体積を6.36
Nm3 とした。そして、本発明に係る排滓方法を採用す
るため、冷却材として嵩比重1.0t/m3 の焼石灰を
4.0ton使用することにした。つまり、冷却材/ス
ラグの体積比は0.63であった。The slag produced by the decarburization refining is composed of Ca
O = 9.2 ton, SiO 2 = 4.6 ton, Al 2 O
3 = 0.7 ton, MgO = 1.4 ton, and the total slag weight is 15.9 ton. This total weight was divided by a bulk specific gravity of 2.5 t / m 3 to reduce the volume of the produced slag to 6.36.
Nm 3 . Then, in order to adopt the waste disposal method according to the present invention, 4.0 ton of calcined lime having a bulk specific gravity of 1.0 t / m 3 was used as a coolant. That is, the volume ratio of the coolant / slag was 0.63.
【0026】脱炭終了後、前記の生成スラグに、この体
積比に従い焼石灰粉を投入し、炉を揺動させてスラグと
十分に混合して冷却、固化させた。その結果、スラグ
は、適度なサイズで、且つサラサラした状態になった。
そこで、該スラグを排送容器(取鍋)に排滓したとこ
ろ、ほぼ生成スラグの全量が円滑に回収できた。次に、
該排滓スラグを、1基目の溶融還元炉に装入し、別途装
入されている溶銑、クロム鉱石、焼石灰、炭材と共に溶
融還元を行った。その際、溶湯の温度は、1600℃に
なるように調整したところ、85分の吹錬時間で操業が
終了した。 (比較例1)2基目の脱炭炉を上底吹機能を有する16
0t転炉(K−BOP)とし、そこに1基目の溶融還元
炉で溶製した含クロム粗溶鋼を125t装入し、粗脱炭
を行った。その際、焼石灰やFe−Cr合金鉄を投入
し、粗脱炭終了後のステンレス溶鋼にトン当り14.3
kg/tのFe−Siを投入して、脱炭中に生成したス
ラグ中の酸化物を還元すると共に、溶鋼の脱硫を行っ
た。After the decarburization was completed, calcined lime powder was charged into the produced slag in accordance with this volume ratio, and the furnace was shaken to sufficiently mix with the slag, and was cooled and solidified. As a result, the slag was in an appropriate size and smooth.
Then, when the slag was discharged into a discharge container (a ladle), almost all of the generated slag could be recovered smoothly. next,
The waste slag was charged into a first smelting reduction furnace, and smelting reduction was performed together with separately charged hot metal, chrome ore, calcined lime, and carbonaceous material. At that time, the temperature of the molten metal was adjusted to 1600 ° C., and the operation was completed in a blowing time of 85 minutes. (Comparative Example 1) A second decarburization furnace was equipped with a top-bottom blowing function.
A 0t converter (K-BOP) was set therein, and 125t of chromium-containing crude molten steel melted in the first smelting reduction furnace was charged therein, and crude decarburization was performed. At that time, calcined lime and Fe-Cr alloy iron were charged, and 14.3 per ton was added to the molten stainless steel after the rough decarburization.
kg / t of Fe-Si was charged to reduce oxides in the slag generated during the decarburization and desulfurize the molten steel.
【0027】脱炭精錬で生成したスラグの内訳は、Ca
O=12.6ton、SiO2 =6.3ton、Al2
O3 =1.2ton、MgO=1.9tonで、合計の
スラグ重量は22.0tonである。この合計重量を嵩
比重2.5t/m3 で除し、生成スラグの体積を8.8
Nm3 とした。そして、冷却材として嵩比重0.5t/
m3 のコークスを0.5ton使用することにした。つ
まり、冷却材/スラグの体積比は0.11である。The slag produced by the decarburization refining is composed of Ca
O = 12.6 ton, SiO 2 = 6.3 ton, Al 2
O 3 = 1.2 ton, MgO = 1.9 ton, and the total slag weight is 22.0 ton. The total weight was divided by the bulk specific gravity of 2.5 t / m 3 to reduce the volume of the produced slag to 8.8.
Nm 3 . And the bulk specific gravity 0.5t /
0.5 tons of m 3 coke was used. That is, the coolant / slag volume ratio is 0.11.
【0028】脱炭終了後、前記の生成スラグに、この体
積比に従い焼石灰粉を投入し、炉を揺動させてスラグと
十分に混合して冷却、固化させた。しかし、スラグは、
凝集固化し、大きなサイズとなり、あるいは耐火物に張
り付き、円滑な排滓ができなかった。そのため、該スラ
グを排送容器(取鍋)に排滓したところ、生成スラグの
大部分が回収できずに炉内に残留した。After the decarburization was completed, calcined lime powder was charged into the produced slag in accordance with this volume ratio, and the furnace was shaken to sufficiently mix with the slag, and was cooled and solidified. However, slag is
Coagulation and solidification resulted in a large size, or stuck to a refractory, preventing smooth discharge. Therefore, when the slag was discharged into a discharge vessel (a ladle), most of the generated slag could not be collected and remained in the furnace.
【0029】次に、該排滓スラグを、1基目の溶融還元
炉に装入し、別途装入されている溶銑、クロム鉱石、焼
石灰、炭材と共に溶融還元を行った。その際、溶湯の温
度は、1550℃になるように調整したところ、吹錬時
間が102分にもなった。これら2つの本発明の実施例
及び比較例での成績を、表1〜4に示す。表1及び2
は、それぞれ脱炭炉からの出鋼した溶湯成分及びスラグ
の組成であり、表3は、該スラグを溶融還元炉へ戻した
際の再利用量の比較、そして表4は、溶融還元炉で再度
溶融還元を行って得たスラグの組成である。Next, the waste slag was charged into a first smelting reduction furnace, and was subjected to smelting reduction together with separately charged hot metal, chrome ore, calcined lime, and carbonaceous material. At that time, when the temperature of the molten metal was adjusted to 1550 ° C., the blowing time was as long as 102 minutes. The results of these two examples of the present invention and comparative examples are shown in Tables 1 to 4. Tables 1 and 2
Is the composition of the molten metal component and slag from the decarburizing furnace, respectively. Table 3 shows a comparison of the amount of recycled slag when returned to the smelting reduction furnace. This is the composition of the slag obtained by performing smelting reduction again.
【0030】表3より明らかなように、比較例1は、脱
炭炉の生成スラグのうち80%しか回収できていない。
また、実施例1の再利用後の溶融還元炉で生じたスラグ
は、T.Crが0.4%であり、従来のスラグの再利用
を行わない溶融還元炉の操業で得ていたスラグと同程度
である。このことは、再利用で順調な溶融還元が行われ
たことを示唆している。さらに、実施例2の脱炭炉で生
成したスラグは、T.Crが5.3%と高いが、その再
利用時に溶湯温度を従来より若干高い1600℃とする
ことで、溶融還元炉での生成スラグ中のT.Crを0.
3%に低下でき、従来のスラグ再利用なし時の溶融還元
炉生成スラグと同程度の還元が達成されていた。As is clear from Table 3, in Comparative Example 1, only 80% of the slag produced in the decarburization furnace was recovered.
Further, the slag generated in the smelting reduction furnace after reuse in Example 1 is T. slag. Cr is 0.4%, which is about the same as slag obtained by operation of a conventional smelting reduction furnace that does not reuse slag. This suggests that the smelting reduction was performed smoothly by reuse. Further, the slag generated in the decarburization furnace of Example 2 Although the Cr content is as high as 5.3%, the T.C. in the slag produced in the smelting reduction furnace is set by setting the temperature of the molten metal to 1600 ° C., which is slightly higher than before, when reusing it. Cr is set to 0.
The slag could be reduced to 3%, and the same reduction as the slag generated in the conventional smelting reduction furnace without slag reuse was achieved.
【0031】[0031]
【表1】 [Table 1]
【0032】[0032]
【表2】 [Table 2]
【0033】[0033]
【表3】 [Table 3]
【0034】[0034]
【表4】 [Table 4]
【0035】[0035]
【発明の効果】以上述べたように、本発明により、2基
の転炉型反応容器を用い、安価なクロム鉱石の直接的な
溶融還元と該溶融還元で得た溶湯の脱炭でステンレス鋼
を製造するに際し、脱炭炉で生成したスラグが円滑に排
滓され、溶融還元炉で再利用できるようになった。ま
た、その排滓時、スラグの冷却材に、溶融還元炉で使用
する炭材、焼石灰等を有効に利用するようにしたので、
溶融還元炉でスラグを再利用する際の操業温度を、それ
ほど高くする必要がなかった。As described above, according to the present invention, stainless steel is produced by direct smelting reduction of inexpensive chromium ore and decarburization of the melt obtained by the smelting reduction using two converter type reaction vessels. During the production of slag, the slag generated in the decarburization furnace was smoothly discharged, and could be reused in the smelting reduction furnace. In addition, at the time of its disposal, the carbon material used in the smelting reduction furnace, calcined lime, etc. were effectively used as the coolant for the slag,
It was not necessary to increase the operating temperature when recycling the slag in the smelting reduction furnace.
【図1】脱炭炉の生成スラグに投入する冷却材量を説明
する図であり、冷却材/スラグの体積比と該スラグの溶
融還元炉での再利用率との関係を示す。BRIEF DESCRIPTION OF DRAWINGS FIG. 1 is a diagram for explaining an amount of coolant to be supplied to slag produced in a decarburization furnace, and shows a relationship between a volume ratio of coolant / slag and a recycling rate of the slag in a smelting reduction furnace.
【図2】脱炭炉の生成スラグを再利用した溶融還元時の
溶湯温度とその溶融還元終了時のスラグ中T.Crとの
関係を示す図である。FIG. 2 shows the temperature of molten metal during smelting reduction using slag produced in a decarburization furnace and the T.C. It is a figure showing the relation with Cr.
【図3】溶融還元時の溶湯温度と炉耐火物の損耗状況と
の関係を示す図である。FIG. 3 is a diagram showing a relationship between a molten metal temperature during smelting reduction and a wear state of a furnace refractory.
───────────────────────────────────────────────────── フロントページの続き (72)発明者 森岡 宏泰 千葉県千葉市中央区川崎町1番地 川崎製 鉄株式会社千葉製鉄所内 (72)発明者 岸本 康夫 千葉県千葉市中央区川崎町1番地 川崎製 鉄株式会社千葉製鉄所内 (72)発明者 北野 嘉久 千葉県千葉市中央区川崎町1番地 川崎製 鉄株式会社千葉製鉄所内 ──────────────────────────────────────────────────続 き Continuing on the front page (72) Inventor Hiroyasu Morioka 1 Kawasaki-cho, Chuo-ku, Chiba-shi, Chiba Chiba Works, Ltd. (72) Inventor Yasuo Kishimoto 1 Kawasaki-cho, Chuo-ku, Chiba-shi, Chiba Kawasaki (72) Inventor Yoshihisa Kitano 1 Kawasaki-cho, Chuo-ku, Chiba-shi, Chiba Chiba Works Chiba Works
Claims (6)
料及び焼石灰を投入し、別途投入した炭材を酸化性ガス
で燃焼せしめて熱を発生させ、該クロム原料を溶融還元
し、次いで、生成した含クロム粗溶鋼を、別の転炉型脱
炭炉内に移行して脱炭精錬を行いステンレス鋼を製造す
るに際し、 前記脱炭炉内で発生したスラグに、冷却材/スラグの体
積比が0.2以上となるように、スラグの冷却材を投入
し、該スラグの凝集を抑制しながら混合及び冷却、固化
させた後のスラグを搬送容器へ排滓することを特徴とす
るステンレス鋼製造時に発生するスラグの排滓方法。1. A chromium raw material and calcined lime are charged into hot metal in a converter-type smelting reduction furnace, and the carbon material separately charged is burned with an oxidizing gas to generate heat, thereby melting and reducing the chromium raw material. Then, the chromium-containing crude molten steel thus produced is transferred to another converter type decarburizing furnace to perform decarburization refining to produce stainless steel. In the slag generated in the decarburizing furnace, coolant / A slag coolant is supplied so that the volume ratio of the slag is 0.2 or more, and the slag after mixing, cooling, and solidifying while suppressing aggregation of the slag is discharged to a transport container. Of slag generated during the production of stainless steel.
する請求項1記載のステンレス鋼製造時に発生するスラ
グの排滓方法。2. The method of claim 1, wherein the coolant is a carbonaceous material.
とする請求項1記載のステンレス鋼製造時に発生するス
ラグの排滓方法。3. The method of claim 1, wherein the coolant is calcined lime.
るスラグの塩基度(CaO/SiO2 )を1.8〜3.
0とすることを特徴とする請求項1〜3いずれかに記載
のステンレス鋼製造時に発生するスラグの排滓方法。4. The basicity (CaO / SiO 2 ) of slag generated in a decarburization furnace before charging the coolant is 1.8 to 3.
4. The method of claim 1, wherein the slag generated during the production of stainless steel is set to zero.
滓したステンレス鋼製造時に発生したスラグを、前記転
炉型溶融還元炉の溶銑に投入し、再度クロム原料を溶融
還元することを特徴とする排滓スラグの再利用方法。5. The slag generated during the production of stainless steel discharged by the method according to any one of claims 1 to 4, is charged into the hot metal of the converter-type smelting reduction furnace, and the chromium raw material is melt-reduced again. A method of recycling waste slag characterized by the following.
〜1650℃以下とすることを特徴とする請求項5記載
の排滓スラグの再利用方法。6. The molten metal temperature in the smelting reduction furnace is set to 1550.
The method for recycling waste slag according to claim 5, wherein the temperature is set to 1650C or lower.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP19234597A JP3744133B2 (en) | 1997-07-17 | 1997-07-17 | Method for removing slag generated during the manufacture of stainless steel and method for reusing waste slag |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP19234597A JP3744133B2 (en) | 1997-07-17 | 1997-07-17 | Method for removing slag generated during the manufacture of stainless steel and method for reusing waste slag |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH1136007A true JPH1136007A (en) | 1999-02-09 |
| JP3744133B2 JP3744133B2 (en) | 2006-02-08 |
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ID=16289740
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| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
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Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH11264011A (en) * | 1998-03-17 | 1999-09-28 | Kawasaki Steel Corp | How to use slag effectively |
| JP2007254899A (en) * | 2007-06-25 | 2007-10-04 | Jfe Steel Kk | Method for reforming steelmaking slag |
| WO2012132789A1 (en) * | 2011-03-31 | 2012-10-04 | 日新製鋼株式会社 | Method for manufacturing stainless steel |
| KR101353196B1 (en) * | 2011-12-05 | 2014-01-20 | 주식회사 포스코 | Method for controlling carbon in converter and manufacturing method of steel comprising thereof |
| JP2018095951A (en) * | 2016-12-08 | 2018-06-21 | ポスコPosco | Reduction method for reducing agent during refining stainless steel |
-
1997
- 1997-07-17 JP JP19234597A patent/JP3744133B2/en not_active Expired - Fee Related
Cited By (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH11264011A (en) * | 1998-03-17 | 1999-09-28 | Kawasaki Steel Corp | How to use slag effectively |
| JP2007254899A (en) * | 2007-06-25 | 2007-10-04 | Jfe Steel Kk | Method for reforming steelmaking slag |
| WO2012132789A1 (en) * | 2011-03-31 | 2012-10-04 | 日新製鋼株式会社 | Method for manufacturing stainless steel |
| CN103476953A (en) * | 2011-03-31 | 2013-12-25 | 日新制钢株式会社 | Method for manufacturing stainless steel |
| TWI491735B (en) * | 2011-03-31 | 2015-07-11 | Nisshin Steel Co Ltd | Method for producing stainless steel |
| KR101353196B1 (en) * | 2011-12-05 | 2014-01-20 | 주식회사 포스코 | Method for controlling carbon in converter and manufacturing method of steel comprising thereof |
| JP2018095951A (en) * | 2016-12-08 | 2018-06-21 | ポスコPosco | Reduction method for reducing agent during refining stainless steel |
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| Publication number | Publication date |
|---|---|
| JP3744133B2 (en) | 2006-02-08 |
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