JPH10130066A - Production of casting material using alumina based refractory waste material - Google Patents

Production of casting material using alumina based refractory waste material

Info

Publication number
JPH10130066A
JPH10130066A JP8299312A JP29931296A JPH10130066A JP H10130066 A JPH10130066 A JP H10130066A JP 8299312 A JP8299312 A JP 8299312A JP 29931296 A JP29931296 A JP 29931296A JP H10130066 A JPH10130066 A JP H10130066A
Authority
JP
Japan
Prior art keywords
waste material
refractory
metal oxide
refractory waste
alumina
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.)
Withdrawn
Application number
JP8299312A
Other languages
Japanese (ja)
Inventor
Koji Tsutsui
康志 筒井
Katsumi Uchinokura
克巳 内之倉
Seiji Aso
誠二 麻生
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Nippon Steel Corp
Original Assignee
Nippon 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 Nippon Steel Corp filed Critical Nippon Steel Corp
Priority to JP8299312A priority Critical patent/JPH10130066A/en
Publication of JPH10130066A publication Critical patent/JPH10130066A/en
Withdrawn legal-status Critical Current

Links

Abstract

PROBLEM TO BE SOLVED: To produce an alumina based casting material to which an alumina based refractory waste material obtained by a refractory waste material treatment without causing any deterioration of workability and durability is added in order to use the casting material using the alumina based refractory waste material used for a lining refractory of a vessel for molten metal. SOLUTION: The refractory waste material containing >=60% Al2 O3 is particle-sized into 1-50mm, dipped into a metallic alkoxide solution containing a sol solution of metal oxide or a precursor of the metal oxide to impregnate the surface of the refractory waste material with >=0.5wt.% metal oxide and dried. The treated refractory waste material of 5-30wt.% is added into the alumina based casting material. Since the metal oxide having heat resistance is impregnated into the particle-sized refractory waste material, the alumina based refractory waste material is effectively used as the coarse particle of the alumina based casting material.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、溶融金属用容器の
内張り耐火物にアルミナ系の耐火物廃材を用いた流し込
み材を使用するために、施工性、耐用性の低下が起こら
ない耐火物廃材処理方法および該方法によって得られた
アルミナ系の耐火物廃材を添加したアルミナ系の流し込
み材の製造方法に関する。
BACKGROUND OF THE INVENTION The present invention relates to a refractory waste material which does not cause deterioration in workability and durability because a cast material using an alumina-based refractory waste material is used for a refractory lining of a container for molten metal. The present invention relates to a treatment method and a method for producing an alumina-based cast material to which an alumina-based refractory waste material obtained by the method is added.

【0002】[0002]

【従来の技術】従来、使用済みの溶融金属用容器等にお
ける耐火物内張は、解体後は殆ど廃棄されており、その
一部が選別・破砕されて再利用されているに過ぎなかっ
た。また、ロングノズル、浸漬ノズル、スライディング
プレートなど鋳造に用いられる耐火物製の部材も同様に
殆どが廃棄されていた。このため、このような廃材の耐
火物へのリサイクルが社会的にも強く要望されていた。
2. Description of the Related Art Heretofore, refractory linings in used molten metal containers and the like have been almost discarded after being dismantled, and only a part of them has been sorted and crushed and reused. Also, most refractory members used for casting, such as long nozzles, immersion nozzles, and sliding plates, have been similarly discarded. For this reason, there has been a strong social demand for recycling such waste materials into refractories.

【0003】一方、上記耐火物内張の構造は、特に築炉
作業の機械化、省力化等の理由により、流し込み材によ
る施工が主流をなしてきている。なお、近年、熔銑鍋、
取鍋、RH、タンディッシュなど溶鉄処理容器に内張り
される耐火物の主流は、アルミナ系流し込み材となって
いる。
On the other hand, the construction of the refractory-lined structure is mainly performed by using a casting material, particularly for reasons such as mechanization and labor saving of furnace construction work. In recent years, hot metal pots,
The main flow of refractories lined in a molten iron processing vessel such as a ladle, RH, and tundish is an alumina-based pouring material.

【0004】また、浸漬ノズルなど耐火物製の鋳造用部
材、混銑車の内張り等の煉瓦は、主に炭素を含有するア
ルミナ系耐火物である。これらのアルミナ系耐火物の廃
材を再び耐火物の製造のために利用できれば申し分な
く、取り分け流し込み材の資源として活用できれば、上
記の要望に合致することとなり、このような観点から非
常に好都合である。
[0004] Refractory casting members such as immersion nozzles, and bricks such as lining of mixed iron wheels are alumina-based refractories mainly containing carbon. It is satisfactory if these alumina-based refractory waste materials can be used again for the production of refractories, and if they can be used as resources for casting materials, the above requirements will be met, which is very convenient from this viewpoint. .

【0005】しかしながら、これら廃材の流し込み材へ
の添加は、煉瓦への添加と異なり流動性、吸水性、破砕
性等が製品の特性に大きな影響を及ぼすため、添加条件
における制約が多く、十分な利用を図ることができな
い。さらに、廃材を粉砕して得られる粒塊自体が不均質
であり、しかも多孔性であるために吸水性が大きい。こ
のため、これらの廃材粒塊をそのまま流し込み材として
用いると、その大きな吸水性等のために、材質にムラが
生じたり、充填性不良等の品質の低下を招き、原料とし
て廃材を使用できる量に限界があり、十分な活用を図る
ことができなかった。
However, when these waste materials are added to the cast material, the flowability, water absorption, crushability and the like greatly affect the properties of the product, unlike the addition to the bricks. You cannot use it. Furthermore, the agglomerates themselves obtained by pulverizing the waste material are inhomogeneous and porous, so that they have high water absorption. For this reason, if these waste material agglomerates are used directly as a casting material, due to their large water absorption or the like, unevenness of the material occurs, or quality deterioration such as poor filling property is caused, and the waste material can be used as a raw material. There was a limit, and could not be fully utilized.

【0006】その対策として特開平6−345548号
公報では、耐火物廃材の粒塊を耐火物原料と配合する前
に、予めモルタルおよび水と混練して、粒塊表面をモル
タルで被覆させて後、流し込み材として利用することを
提示している。
As a countermeasure, Japanese Unexamined Patent Publication No. Hei 6-345548 discloses a method in which, before blending a remnant of refractory waste with a refractory raw material, kneading with a mortar and water in advance and coating the surface of the remnant with mortar. , It is suggested to be used as a pouring material.

【0007】[0007]

【発明が解決しようとする課題】しかしながら、この方
法は、粒径10mm以上の骨材にしか適用できなく、ま
た、通気性の高いモルタルでは廃材に含まれる炭素源の
強化を抑制できず、乾燥時に耐火物組織の劣化をもたら
す。その他にも、廃材の粒塊を被覆したモルタルと耐火
物原料間の過焼結による耐熱衝撃性の低下、モルタルと
耐火物原料間の低融点物の生成反応による耐食性の低下
の問題を有していた。本発明は、上記の問題を解消し、
アルミナ系の耐火物廃材をアルミナ系の流し込み材の粗
粒として有効に活用することを主な目的とする。
However, this method can be applied only to aggregates having a particle size of 10 mm or more, and a mortar having a high air permeability cannot suppress the strengthening of the carbon source contained in the waste material. Occasionally, the refractory structure deteriorates. In addition, there is a problem that the thermal shock resistance decreases due to oversintering between the mortar coated with the agglomerates of the waste material and the refractory raw material, and the corrosion resistance decreases due to a reaction of forming a low melting point between the mortar and the refractory raw material. I was The present invention solves the above problems,
The main purpose is to effectively utilize alumina-based refractory waste material as coarse particles of an alumina-based casting material.

【0008】[0008]

【課題を解決するための手段】本発明は上記課題を解決
するためなされたもので、その手段は下記の通りであ
る。 (1) Al23 含有率60重量%以上の耐火物廃材
を1〜50mmに整粒し、次いで金属酸化物のゾル溶液
に浸漬させ、該耐火物廃材の表面に金属酸化物を0.5
重量%以上含浸させた後乾燥し、前記処理を施した耐火
物廃材を5〜30重量%アルミナ系流し込み材に添加す
ることを特徴とするアルミナ系の耐火物廃材を用いた流
し込み材の製造方法。 (2) Al23 含有率60重量%以上の耐火物廃材
を1〜50mmに整粒し、次いで金属酸化物のゾル溶液
に浸漬させ、次いで金属酸化物の前駆体を含む金属アル
コキシド溶液に浸漬させ、該耐火物廃材の表面に金属酸
化物を0.5重量%以上含浸させた後乾燥し、前記処理
を施した耐火物廃材を5〜30重量%アルミナ系流し込
み材に添加することを特徴とするアルミナ系の耐火物廃
材を用いた流し込み材の製造方法。
Means for Solving the Problems The present invention has been made to solve the above problems, and the means are as follows. (1) A refractory waste material having an Al 2 O 3 content of 60% by weight or more is sized to 1 to 50 mm, and then immersed in a metal oxide sol solution to form a metal oxide on the surface of the refractory waste material. 5
A method for producing a cast material using an alumina-based refractory waste material, wherein the impregnated refractory material is dried after being impregnated in an amount of not less than 5% by weight, and the treated refractory material is subjected to the above treatment. . (2) A refractory waste material having an Al 2 O 3 content of 60% by weight or more is sized to 1 to 50 mm, then immersed in a metal oxide sol solution, and then immersed in a metal alkoxide solution containing a metal oxide precursor. Immersing, impregnating the surface of the refractory waste material with a metal oxide in an amount of 0.5% by weight or more, drying the refractory waste material, and adding the treated refractory waste material to 5 to 30% by weight alumina-based casting material. A method for producing a casting material using a waste alumina-based refractory material.

【0009】[0009]

【発明の実施の形態】本発明者らは、従来技術の問題点
に鑑み、廃材表面に微細な粒子で、緻密で薄い層状の構
造を形成させればよいのではないかとの観点から、鋭意
研究を重ねたところ、アルミナ系の廃材を1〜50mm
に整粒し、アルミナ系の耐火物原料と配合する前に、予
め耐熱性を有する金属酸化物のゾル溶液、あるいは金属
酸化物の前駆体を含む金属アルコキシド溶液に含浸処理
して、乾燥した場合には、廃材の粒塊が流し込み材の粗
粒として、有効であることを見出したもので、その結果
耐火物廃材を活用させることができ、本発明を完成する
に至った。
DESCRIPTION OF THE PREFERRED EMBODIMENTS In view of the problems of the prior art, the present inventors have eagerly considered that a fine and thin layered structure may be formed with fine particles on the surface of waste material. After repeated research, 1-50mm of alumina waste material
Before being mixed with an alumina-based refractory raw material, before being impregnated with a heat-resistant metal oxide sol solution or a metal alkoxide solution containing a metal oxide precursor, and then dried. Have found that the agglomerates of the waste material are effective as coarse particles of the cast material, and as a result, the refractory waste material can be utilized, and the present invention has been completed.

【0010】すなわち、本発明はアルミナ系の廃材の処
理方法として、廃材を1〜50mmに整粒し、次いでA
23 、SiO2 、ZrSiO4 など耐熱性を有する
金属酸化物のゾル溶液に大気下あるいは真空下で廃材に
金属酸化物が0.5重量%以上に含浸するように、10
分間以上、好ましくは数時間浸漬させた後、200℃以
下で乾燥する。
That is, according to the present invention, as a method for treating alumina-based waste material, the waste material is sized to 1 to 50 mm, and then A
A sol solution of a heat-resistant metal oxide such as l 2 O 3 , SiO 2 , or ZrSiO 4 is impregnated with the waste material so that the metal oxide is impregnated to 0.5% by weight or more in air or under vacuum.
After immersion for more than a minute, preferably several hours, it is dried at 200 ° C. or less.

【0011】または、アルミナ系の廃材の処理方法とし
て、廃材を1〜50mmに整粒し、次いでAl23
SiO2 、ZrSiO4 など耐熱性を有する金属酸化物
の前駆体を含む金属アルコキシド溶液中に、大気下ある
いは真空下で廃材の表面に金属酸化物が0.5重量%以
上に含浸するように10分間以上、好ましくは数時間浸
漬させた後、200℃以下で乾燥する。このような処理
を施すことにより、アルミナ系の耐火物廃材の表面を金
属酸化物で被覆した1〜50mmの粗粒を得、これを母
材であるアルミナ系の流し込み材に5〜30重量%添加
するものである。
[0011] Alternatively, as a method of treating alumina-based waste material, the waste material is sized to 1 to 50 mm, and then Al 2 O 3 ,
In a metal alkoxide solution containing a precursor of a heat-resistant metal oxide such as SiO 2 or ZrSiO 4 , the surface of the waste material is impregnated with the metal oxide to 0.5% by weight or more under the atmosphere or under vacuum. After immersion for more than a minute, preferably several hours, it is dried at 200 ° C. or less. By performing such a treatment, coarse particles of 1 to 50 mm in which the surface of the alumina-based refractory waste material is coated with a metal oxide are obtained, and this is added to the alumina-based casting material as a base material in an amount of 5 to 30% by weight. It is to be added.

【0012】以下、さらに本発明について詳細に説明す
る。本発明方法によれば、内部まで、Al23 、Si
2 、ZrSiO4 など耐熱性を有する金属酸化物を含
浸したアルミナ系の廃材を得ることができる。すなわ
ち、廃材はクラシャー等の通常の粉砕機により粉砕し、
篩い分けして粒径が1〜50mmの粒塊とする。好まし
くは、さらに1〜5mm、5〜10mm、10〜20m
m、20〜40mmに細かく篩い分け、各粒度の配合割
合を母材である流し込み材の粒度構成と近似したものと
した方がよい。粒径が1mm以下の場合には、金属酸化
物を含浸したアルミナ系の廃材を流し込み材に添加する
と、異常反応または異常膨張が起こる恐れがあるので好
ましくない。粒径が50mm以上の場合には、施工時に
粒子の偏析が起きたり、粗粒間に充填される細粒の組織
が緩やかになって構造体としても安定性が低下する恐れ
があるので好ましくない。
Hereinafter, the present invention will be described in more detail. According to the method of the present invention, Al 2 O 3 , Si
An alumina-based waste material impregnated with a heat-resistant metal oxide such as O 2 or ZrSiO 4 can be obtained. That is, the waste material is crushed by a normal crusher such as a crusher,
The mixture is sieved to obtain granules having a particle size of 1 to 50 mm. Preferably, further 1-5 mm, 5-10 mm, 10-20 m
It is better to sieve finely to 20 to 40 mm, and to make the mixing ratio of each particle size approximate to the particle size configuration of the casting material as the base material. When the particle size is 1 mm or less, it is not preferable to add an alumina-based waste material impregnated with a metal oxide to the casting material because an abnormal reaction or abnormal expansion may occur. When the particle size is 50 mm or more, the segregation of the particles may occur at the time of construction or the structure of the fine particles filled between the coarse particles may become loose and the stability as a structure may be reduced, which is not preferable. .

【0013】また、使用する廃材はAl23 含有率6
0重量%以上のアルミナ系耐火物であり、Al23
有率60重量%以下では、含浸したAl23 、SiO
2 、ZrSiO4 などの金属酸化物と廃材自身が、溶
鉄、溶融スラグと接する高温雰囲気下において、低融点
物質を形成して、耐用性の低下が顕著に現れてくる恐れ
があるからである。さらに、廃材は乾燥処理を行って十
分に乾燥したものを用いるのが望ましい。水気を帯び、
濡れたものは、処理溶液が内部まで含浸しにくくなるか
らである。
The waste material used has an Al 2 O 3 content of 6
It is an alumina-based refractory of 0% by weight or more, and an Al 2 O 3 content of 60% by weight or less impregnated with Al 2 O 3 and SiO 2.
2. Because the metal oxide such as ZrSiO 4 and the waste material themselves may form a low-melting substance in a high-temperature atmosphere in contact with the molten iron and the molten slag, and the durability may be significantly reduced. Further, it is desirable to use a waste material which has been sufficiently dried by performing a drying treatment. Watery,
This is because the wet solution makes it difficult for the processing solution to impregnate the inside.

【0014】次いで、上記廃材を耐熱性を有する金属酸
化物のゾル溶液、または金属酸化物の前駆体を含む金属
アルコキシド溶液に浸漬する。ここで、金属酸化物は、
廃材を混入する流し込み材の使用用途で決める。例え
ば、高温スラグと接する部位には耐食性を有するAl2
3 を、酸化雰囲気の部位には施工体の表面をガラス化
し空気の遮断の働きをするSiO2 を、両方の環境に有
る場合はAl23 とSiO2 と中間の特性を有するZ
rSiO4 を適用することが望ましい。
Next, the waste material is immersed in a sol solution of a metal oxide having heat resistance or a metal alkoxide solution containing a precursor of the metal oxide. Here, the metal oxide is
Determined by the intended use of the pouring material that mixes the waste material. For example, a portion in contact with high-temperature slag is Al 2 having corrosion resistance.
The O 3, Z is the site of an oxidizing atmosphere having an Al 2 O 3 and SiO 2 and the intermediate characteristic when the SiO 2 which acts as blocking air vitrifying the surface of the construction member, is in the both environments
It is desirable to apply rSiO 4 .

【0015】本発明の一つの好ましい態様によれば、整
粒した廃材は、網篭に移し金属酸化物のゾル溶液、また
は金属酸化物の前駆体を含む金属アルコキシド溶液が入
っている容器に入れて浸漬する。雰囲気は、大気下でも
差し支えないし、真空状態を保った処理タンク内に容器
ごと入れて真空下で浸漬しても差し支えない。この状態
を1時間程度持続させて金属酸化物の含浸処理を行う。
廃材によっては、10分強の短い含浸処理でも差し支え
ないこともある。
According to one preferred embodiment of the present invention, the sized waste material is transferred to a mesh basket and placed in a container containing a metal oxide sol solution or a metal alkoxide solution containing a metal oxide precursor. And soak. The atmosphere may be in the atmosphere, or the container may be placed in a processing tank maintained in a vacuum state and immersed in a vacuum. This state is maintained for about one hour to perform the metal oxide impregnation treatment.
Depending on the waste material, a short impregnation treatment of just over 10 minutes may be sufficient.

【0016】ただし、廃材の表面に含浸した金属酸化物
が0.5重量%以上でない場合は、さらに浸漬時間を延
ばす。この理由は含浸した金属酸化物が0.5重量%未
満の場合、廃材の吸水性を防止できず、施工性の低下、
それに伴う、耐火物特性の低下をもたらしたり、特に炭
素を含有する廃材では、流し込み施工した後の乾燥、予
熱時に炭素の酸化が起こり、耐用性が大幅に低下する恐
れがある。含浸処理後、容器から網篭を取り出して水切
りをし、150℃程度の温度で乾燥を行う。200℃超
の温度で乾燥した場合には、廃材表面に被覆した金属酸
化物の層状の皮膜が水蒸気圧の影響で破れて、廃材の吸
水性の防止が薄れ、また炭素を含有する廃材では廃材自
身の耐酸化性の向上が見られなくなってしまう恐れがあ
る。
However, when the metal oxide impregnated on the surface of the waste material is not 0.5% by weight or more, the immersion time is further extended. The reason for this is that if the impregnated metal oxide is less than 0.5% by weight, the water absorption of the waste material cannot be prevented, and the workability deteriorates.
As a result, the refractory properties may be reduced, and especially in the case of waste materials containing carbon, carbon may be oxidized at the time of drying and preheating after casting, and the durability may be significantly reduced. After the impregnation, the net basket is taken out of the container, drained, and dried at a temperature of about 150 ° C. When dried at a temperature higher than 200 ° C., the layered film of the metal oxide coated on the surface of the waste material is broken by the influence of the water vapor pressure, and the prevention of water absorption of the waste material is diminished. There is a possibility that the oxidation resistance of itself will not be improved.

【0017】次に、上記の金属酸化物により被覆された
粒塊からなる廃材を流し込み材と、加水混練する。この
流し込み材は、例えば、アルミナ原料、アルミナスピネ
ル原料、ハイアルミナセメント等と解膠剤等の添加剤と
から構成される。また、本発明の流し込み材は、所望の
用途・特性、用いる廃材等によって異なり一様でない
が、整粒し、上記の方法によって処理された廃材を母材
である流し込み材に5〜30%重量添加するものであ
る。処理された廃材が5重量%未満の場合には、施工
性、特性の向上効果が明確に見られず、また廃材の処理
費用を考慮すると流し込み材の価格に優位性がないから
である。また、処理された廃材が30重量%超の場合に
は、含浸した金属酸化物自身の影響が見られるようにな
り、施工不良が起きたり、溶鉄・スラグに対する耐食
性、高温強度などの特性の低下が顕著になるからであ
る。
Next, the waste material composed of the agglomerates covered with the above-mentioned metal oxide is subjected to water kneading with the pouring material. The pouring material is composed of, for example, an alumina raw material, an alumina spinel raw material, high alumina cement, and an additive such as a deflocculant. The cast material of the present invention varies depending on the desired use / characteristics, the used waste material, etc., but is not uniform. However, the waste material which has been sized and treated by the above method is added to the cast material as a base material by 5 to 30% by weight. It is to be added. If the treated waste material is less than 5% by weight, the effect of improving the workability and characteristics is not clearly seen, and the cost of the cast material is not superior in consideration of the disposal cost of the waste material. Further, when the treated waste material exceeds 30% by weight, the influence of the impregnated metal oxide itself can be seen, resulting in poor construction or deterioration in properties such as corrosion resistance to molten iron and slag and high-temperature strength. This is because remarkable.

【0018】[0018]

【実施例】以下に実施例および比較例を示し、本発明の
特徴とするところを一層明確にする。 (実施例A)表1に示すような組成を用いた流し込み材
による成形体を製造した。ここで用いた炭素含有耐火物
廃材は、使用したAl23 含有量85重量%のアルミ
ナ系タンディッシュSNプレートを回収し、粉砕・篩い
分けして得たものである。この篩い分けした1〜40m
mの廃材の処理方法として、シリカゾル溶液およびジル
コンアルコキシド溶液に所定の時間浸漬した後、150
℃で乾燥を行った。廃材無添加の比較例1に対し未処理
の廃材を添加した場合、同じ量の混練水分の比較例2で
は施工不良が発生し、水分量を増加した比較例3では見
掛け気孔率が顕著に上昇し、圧縮強度の低下が見られ、
耐火物の物性低下が起きている。それに対して、廃材の
処理を施した実施例1,2,3,4ともシリカゾル溶液
およびジルコンアルコキシド溶液、大気下および真空下
含浸に関係なく、廃材無添加の比較例1と同等の施工性
と耐火物の物性を有していることが明白である。ただ
し、含浸時間が短かった比較例4では、廃材処理の効果
が小さく施工不良が発生した。これは、SiO2 分の含
浸量が0.5%未満であったからである。
EXAMPLES Examples and comparative examples are shown below to further clarify the features of the present invention. (Example A) A molded article was produced from a casting material using a composition as shown in Table 1. The carbon-containing refractory waste used here was obtained by collecting and grinding and sieving an alumina-based tundish SN plate having an Al 2 O 3 content of 85% by weight. This sieved 1-40m
m was immersed in a silica sol solution and a zircon alkoxide solution for a predetermined period of time.
Drying was performed at ° C. When the untreated waste material was added to Comparative Example 1 where no waste material was added, construction failure occurred in Comparative Example 2 with the same amount of kneading water, and apparent porosity increased remarkably in Comparative Example 3 in which the water content was increased. And a decrease in compressive strength is seen,
The physical properties of the refractory have been reduced. On the other hand, in Examples 1, 2, 3 and 4 in which the waste material was treated, regardless of the silica sol solution and the zircon alkoxide solution, the impregnation under the atmosphere and under vacuum, the workability was equivalent to that of Comparative Example 1 with no waste material added. It is clear that it has the properties of refractories. However, in Comparative Example 4 in which the impregnation time was short, the effect of waste material treatment was small, and construction failure occurred. This is because the impregnation amount of SiO 2 was less than 0.5%.

【0019】[0019]

【表1】 [Table 1]

【0020】(実施例B)表2に示すような組成を用い
た流し込み材による成形体を製造した。ここで用いた炭
素含有耐火物廃材は、使用したAl23 含有量85重
量%のアルミナ系タンディッシュSNプレートである。
また、廃材の処理方法は、大気下でシリカゾル溶液およ
びジルコンアルコキシド溶液に浸漬した。廃材無添加の
比較例1に対して、廃材の処理を施した実施例1,2,
3,4とも処理溶液に関係なく、廃材添加量が5〜30
%の範囲では、施工性、材料物性、耐火物特性とも低下
は見られない。従って、溶鉄処理槽に適用した場合、比
較例1と同等の耐用性が期待できる。それに対して、廃
材添加量が少ない比較例2では、廃材処理の効果が定か
でなく、また廃材添加量が多い比較例3では、施工不良
が発生した。実施例2と4を別々に溶鋼と接する取鍋の
壁部に一体施工を行った。ともに施工に問題なく、良好
な施工構造体が得られた。乾燥後も亀裂、剥離もなく、
実稼働に入れた。適用した結果は、比較例1と同じ炉寿
命が保たれ、損傷速度も同等であり、良好な耐用性が得
られた。
(Example B) A molded article was prepared from a casting material using a composition as shown in Table 2. The carbon-containing refractory waste used here is an alumina-based tundish SN plate having an Al 2 O 3 content of 85% by weight.
Further, as a method of treating the waste material, the waste material was immersed in a silica sol solution and a zircon alkoxide solution in the atmosphere. Examples 1, 2 and 2 in which the waste material was applied to Comparative Example 1 in which no waste material was added
Regardless of the processing solution, the amount of waste material added is 5 to 30 for both 3 and 4.
In the range of%, there is no decrease in workability, material properties, and refractory properties. Therefore, when applied to a molten iron treatment tank, the same durability as Comparative Example 1 can be expected. On the other hand, in Comparative Example 2 in which the amount of waste material added was small, the effect of the waste material treatment was uncertain, and in Comparative Example 3 in which the amount of waste material added was large, poor construction occurred. Examples 2 and 4 were separately integrated into a ladle wall in contact with molten steel. In both cases, there was no problem in the construction, and a good construction structure was obtained. No cracks or peeling after drying,
Put into production. As a result of the application, the same furnace life as Comparative Example 1 was maintained, the damage rate was equal, and good durability was obtained.

【0021】[0021]

【表2】 [Table 2]

【0022】(実施例C)表3に示すような組成を用い
た流し込み材による成形体を製造した。廃材は、取鍋に
用いたろう石煉瓦、混銑車に用いたアルミナ−炭化珪素
−炭素煉瓦、タンディッシュSNプレートに使用したア
ルミナ質の耐火物であり、いずれも廃材に含まれるAl
23 含有率が異なる。また、廃材の処理方法は、シリ
カゾル溶液に浸漬した。廃材無添加の比較例1に対し
て、廃材の処理を施した実施例1,2,3とも廃材の種
類に関係なく、同等の施工性を有し、耐火物の物性も差
がみられない。しかしながら、廃材に含まれるAl2
3 含有率が高い程、耐食性、耐熱スポール性の特性が向
上する傾向があり、Al23 含有率が最も低い実施例
1では、比較例1に比べ、特性の低下が顕著である。こ
れは、含浸した金属酸化物と廃材自身が、高温雰囲気下
において、低融点物質を形成したためであり、このよう
に、耐用性を落とさずに、廃材を有効活用するには、廃
材自身のAl23 含有率に注意する必要があり、60
重量%以上の廃材を選択しなければならない。
(Example C) A molded article was prepared from a cast material having a composition as shown in Table 3. The waste materials are the limestone brick used for the ladle, the alumina-silicon carbide-carbon brick used for the mixed iron wheel, and the alumina refractory used for the tundish SN plate.
2 O 3 content is different. The waste material was treated by immersing it in a silica sol solution. In comparison with Comparative Example 1 in which no waste material was added, Examples 1, 2 and 3, in which the waste material was treated, had the same workability regardless of the type of the waste material, and there was no difference in the physical properties of the refractory. . However, Al 2 O contained in waste materials
(3) The higher the content, the more the corrosion resistance and the heat-resistant spall properties tend to be improved. In Example 1, in which the content of Al 2 O 3 is the lowest, the characteristics are significantly reduced as compared with Comparative Example 1. This is because the impregnated metal oxide and the waste material themselves formed a low-melting substance in a high-temperature atmosphere. Thus, in order to effectively utilize the waste material without deteriorating its durability, it is necessary to use the aluminum of the waste material itself. It is necessary to pay attention to the 2 O 3 content,
You must select more than weight percent waste.

【0023】[0023]

【表3】 [Table 3]

【0024】[0024]

【発明の効果】本発明の処理方法によれば、予め整粒し
た耐火物廃材の内部まで、耐熱性を有する金属酸化物を
含浸させることができ、アルミナ系の耐火物廃材をアル
ミナ系の流し込み材の粗粒として有効に利用することが
できる。すなわち、廃材自身の表面が金属酸化物により
被覆されるので、廃材の吸水性を低下ないし喪失させ、
かつ廃材自身の強度を向上させることができる。この結
果、廃材を添加した流し込み材は、施工性の低下、特性
・物性の低下が起きず、実炉への適用においても良好な
耐用性を得ることができる。
According to the treatment method of the present invention, metal oxides having heat resistance can be impregnated up to the inside of refractory waste material that has been sized in advance, and alumina-based refractory waste material can be poured into alumina. It can be effectively used as coarse particles of wood. That is, since the surface of the waste material itself is coated with the metal oxide, the water absorption of the waste material is reduced or lost,
In addition, the strength of the waste material itself can be improved. As a result, the cast material to which the waste material is added does not cause a decrease in workability, a decrease in properties and physical properties, and can provide good durability even when applied to an actual furnace.

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 Al23 含有率60重量%以上の耐火
物廃材を1〜50mmに整粒し、次いで金属酸化物のゾ
ル溶液に浸漬させ、該耐火物廃材の表面に金属酸化物を
0.5重量%以上含浸させた後乾燥し、前記処理を施し
た耐火物廃材を5〜30重量%アルミナ系流し込み材に
添加することを特徴とするアルミナ系の耐火物廃材を用
いた流し込み材の製造方法。
1. A refractory waste material having an Al 2 O 3 content of 60% by weight or more is sized to 1 to 50 mm, and then immersed in a metal oxide sol solution to deposit a metal oxide on the surface of the refractory waste material. A cast material using an alumina-based refractory waste material, wherein the impregnated refractory material is dried after impregnated by 0.5% by weight or more, and the treated refractory waste material is added to a 5-30% by weight alumina-based cast material. Manufacturing method.
【請求項2】 Al23 含有率60重量%以上の耐火
物廃材を1〜50mmに整粒し、次いで金属酸化物のゾ
ル溶液に浸漬させ、次いで金属酸化物の前駆体を含む金
属アルコキシド溶液に浸漬させ、該耐火物廃材の表面に
金属酸化物を0.5重量%以上含浸させた後乾燥し、前
記処理を施した耐火物廃材を5〜30重量%アルミナ系
流し込み材に添加することを特徴とするアルミナ系の耐
火物廃材を用いた流し込み材の製造方法。
2. A refractory waste material having an Al 2 O 3 content of 60% by weight or more is sized to 1 to 50 mm, then immersed in a metal oxide sol solution, and then a metal alkoxide containing a metal oxide precursor. After being immersed in a solution, the surface of the refractory waste material is impregnated with 0.5% by weight or more of a metal oxide, dried, and the treated refractory waste material is added to 5 to 30% by weight alumina-based casting material. A method for producing a casting material using an alumina-based refractory waste material.
JP8299312A 1996-10-24 1996-10-24 Production of casting material using alumina based refractory waste material Withdrawn JPH10130066A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP8299312A JPH10130066A (en) 1996-10-24 1996-10-24 Production of casting material using alumina based refractory waste material

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP8299312A JPH10130066A (en) 1996-10-24 1996-10-24 Production of casting material using alumina based refractory waste material

Publications (1)

Publication Number Publication Date
JPH10130066A true JPH10130066A (en) 1998-05-19

Family

ID=17870914

Family Applications (1)

Application Number Title Priority Date Filing Date
JP8299312A Withdrawn JPH10130066A (en) 1996-10-24 1996-10-24 Production of casting material using alumina based refractory waste material

Country Status (1)

Country Link
JP (1) JPH10130066A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100478141B1 (en) * 2000-12-20 2005-03-22 재단법인 포항산업과학연구원 Injection repair composition for blast furnace by using spent refractories
KR100505110B1 (en) * 2000-12-22 2005-07-29 재단법인 포항산업과학연구원 Unshaped refractories composition
KR100666083B1 (en) 2005-07-19 2007-01-09 삼성물산 주식회사 The mortar composition with recycled alumina for refractory lining
CN105218119A (en) * 2015-10-29 2016-01-06 长兴云峰炉料有限公司 A kind of remelted pig iron pouring refractories
CN111018548A (en) * 2019-11-27 2020-04-17 天津炜润达新材料科技有限公司 Recycling method of waste refractory material

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100478141B1 (en) * 2000-12-20 2005-03-22 재단법인 포항산업과학연구원 Injection repair composition for blast furnace by using spent refractories
KR100505110B1 (en) * 2000-12-22 2005-07-29 재단법인 포항산업과학연구원 Unshaped refractories composition
KR100666083B1 (en) 2005-07-19 2007-01-09 삼성물산 주식회사 The mortar composition with recycled alumina for refractory lining
CN105218119A (en) * 2015-10-29 2016-01-06 长兴云峰炉料有限公司 A kind of remelted pig iron pouring refractories
CN111018548A (en) * 2019-11-27 2020-04-17 天津炜润达新材料科技有限公司 Recycling method of waste refractory material

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