JP3292271B2 - Waste brick treatment method for metal smelting furnace - Google Patents
Waste brick treatment method for metal smelting furnaceInfo
- Publication number
- JP3292271B2 JP3292271B2 JP11140295A JP11140295A JP3292271B2 JP 3292271 B2 JP3292271 B2 JP 3292271B2 JP 11140295 A JP11140295 A JP 11140295A JP 11140295 A JP11140295 A JP 11140295A JP 3292271 B2 JP3292271 B2 JP 3292271B2
- Authority
- JP
- Japan
- Prior art keywords
- waste
- smelting furnace
- bricks
- brick
- copper
- 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 - Lifetime
Links
- 239000011449 brick Substances 0.000 title claims description 70
- 239000002699 waste material Substances 0.000 title claims description 54
- 238000003723 Smelting Methods 0.000 title claims description 29
- 238000000034 method Methods 0.000 title claims description 19
- 229910052751 metal Inorganic materials 0.000 title claims description 15
- 239000002184 metal Substances 0.000 title claims description 14
- 239000010949 copper Substances 0.000 claims description 22
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims description 21
- 229910052802 copper Inorganic materials 0.000 claims description 21
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 8
- 238000002844 melting Methods 0.000 claims 1
- 230000008018 melting Effects 0.000 claims 1
- CPLXHLVBOLITMK-UHFFFAOYSA-N Magnesium oxide Chemical compound [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 description 20
- 238000010298 pulverizing process Methods 0.000 description 17
- 239000000395 magnesium oxide Substances 0.000 description 10
- 238000006703 hydration reaction Methods 0.000 description 7
- 239000002245 particle Substances 0.000 description 6
- 238000006243 chemical reaction Methods 0.000 description 5
- 238000000227 grinding Methods 0.000 description 5
- 239000000463 material Substances 0.000 description 5
- 239000000843 powder Substances 0.000 description 5
- 239000002893 slag Substances 0.000 description 4
- 229910000831 Steel Inorganic materials 0.000 description 3
- 230000000052 comparative effect Effects 0.000 description 3
- 238000002474 experimental method Methods 0.000 description 3
- 239000010959 steel Substances 0.000 description 3
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- 239000004566 building material Substances 0.000 description 2
- BBEAQIROQSPTKN-UHFFFAOYSA-N pyrene Chemical compound C1=CC=C2C=CC3=CC=CC4=CC=C1C2=C43 BBEAQIROQSPTKN-UHFFFAOYSA-N 0.000 description 2
- 229920006395 saturated elastomer Polymers 0.000 description 2
- 239000011822 basic refractory Substances 0.000 description 1
- DVRDHUBQLOKMHZ-UHFFFAOYSA-N chalcopyrite Chemical compound [S-2].[S-2].[Fe+2].[Cu+2] DVRDHUBQLOKMHZ-UHFFFAOYSA-N 0.000 description 1
- 229910052804 chromium Inorganic materials 0.000 description 1
- 239000011651 chromium Substances 0.000 description 1
- OMZSGWSJDCOLKM-UHFFFAOYSA-N copper(II) sulfide Chemical compound [S-2].[Cu+2] OMZSGWSJDCOLKM-UHFFFAOYSA-N 0.000 description 1
- 230000006378 damage Effects 0.000 description 1
- 230000003203 everyday effect Effects 0.000 description 1
- 239000011451 fired brick Substances 0.000 description 1
- GVEPBJHOBDJJJI-UHFFFAOYSA-N fluoranthrene Natural products C1=CC(C2=CC=CC=C22)=C3C2=CC=CC3=C1 GVEPBJHOBDJJJI-UHFFFAOYSA-N 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 239000002440 industrial waste Substances 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 238000005065 mining Methods 0.000 description 1
- 238000000465 moulding Methods 0.000 description 1
- 239000012466 permeate Substances 0.000 description 1
- 239000011802 pulverized particle Substances 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 229910052725 zinc Inorganic materials 0.000 description 1
Classifications
-
- Y02W30/54—
Landscapes
- Processing Of Solid Wastes (AREA)
- Disintegrating Or Milling (AREA)
- Manufacture And Refinement Of Metals (AREA)
Description
【0001】[0001]
【産業上の利用分野】本発明は、金属溶錬炉の修理又は
解体時等に発生する廃レンガを粉砕することにより処理
する方法に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating a waste smelter by pulverizing waste bricks generated when the furnace is repaired or dismantled.
【0002】[0002]
【従来の技術】金属溶錬炉から発生する廃レンガを再利
用するためには廃レンガを粉砕することが必要になる。2. Description of the Related Art In order to reuse waste bricks generated from a metal smelting furnace, it is necessary to grind the waste bricks.
【0003】例えば、銅製錬において自溶炉、反射炉及
び転炉等で使用されているマグネシア−クロム焼成レン
ガ(通称「マグクロレンガ」)は、これらの炉の修理・
解体時には、多量の廃レンガの発生源となるが、炉内で
高温の溶湯と接触しているためにマット(銅−鉄硫化
物)や金属銅を多量に含んでいる。一方、加熱炉などの
廃レンガにはこのようなマットや金属銅が含浸していな
いので、廃レンガは炉材メーカーにおいて機械的に粉砕
された後にスタンプ材として再利用されている。しか
し、溶錬炉の廃レンガはマットや金属銅を含浸している
ため、銅含有率は10〜20重量%にも達し、粉砕法に
より得られた粉末又は塊材も多量のマット等を含有して
いるので、これらを炉材としての再利用することができ
ない。For example, magnesia-chromium fired bricks (commonly referred to as “magcro bricks”) used in flash smelting furnaces, reverberatory furnaces, converters, and the like in copper smelting are used for repair and repair of these furnaces.
At the time of dismantling, it is a source of a large amount of waste bricks, but contains a large amount of mat (copper-iron sulfide) and metallic copper because it is in contact with the high-temperature molten metal in the furnace. On the other hand, waste bricks such as a heating furnace are not impregnated with such mats and metallic copper, and thus the waste bricks are mechanically pulverized by a furnace material manufacturer and then reused as a stamp material. However, since the waste brick of the smelting furnace is impregnated with mats and metallic copper, the copper content reaches 10 to 20% by weight, and the powder or lump obtained by the pulverization method also contains a large amount of mats and the like. Therefore, they cannot be reused as furnace materials.
【0004】一方マットや金属銅は有価物であるため、
マットや金属銅を含浸した廃レンガを機械的に粉砕して
再度溶錬炉に繰返し溶解させることにより、廃レンガ中
の銅分を溶湯に回収することが一般に行われている。し
かし、マットや金属銅を含んだ廃レンガは粉砕性が悪い
上、溶錬炉に繰返して溶解することが可能な粒度、好ま
しくは10mm以下に廃レンガを粉砕するには、2〜3
段の機械粉砕及び分級の操作が必要となる。このため粉
砕コストが高くなる。[0004] On the other hand, mats and metallic copper are valuable materials,
It is common practice to mechanically pulverize waste bricks impregnated with mats and metallic copper and then repeatedly melt them in a smelting furnace to recover the copper content in the waste bricks into molten metal. However, waste bricks containing matte and metallic copper have poor pulverizability, and have a particle size that can be repeatedly melted in a smelting furnace, preferably, to a size of 10 mm or less, it takes 2-3
Operation of mechanical grinding and classification of the stage is required. For this reason, the grinding cost increases.
【0005】鉄鋼製錬において使用済みとなったマグネ
シアレンガの再利用法が例えば特開平6−116617
号公報で提案されている。この方法では、使用済みマグ
ネシアレンガを粉砕機械(ジョークラッシャ)により2
0mm以下に粉砕し、これをMgOを主成分とする耐火
物を内張りした溶鋼製錬炉に繰り返して、溶解させるこ
とにより、スラグ中のMgO濃度を調整している。A method of recycling magnesia bricks used in steel smelting is disclosed in, for example, Japanese Patent Application Laid-Open No. Hei 6-116617.
No. pp. 139 to 163. In this method, used magnesia bricks are crushed by a crushing machine (jaw crusher).
The MgO concentration in the slag is adjusted by pulverizing the slag to 0 mm or less and repeating this in a molten steel smelting furnace lined with a refractory containing MgO as a main component and dissolving it.
【0006】また、特開平6−92701号公報による
と、廃レンガを建築材料としてリサイクルするために、
20〜120mm程度の丸状物に粉砕する方法を提示し
ているが、この方法でもパイレン、ジョークラッシャ及
び角取り装置などの機械により廃レンガを粉砕してい
る。According to Japanese Patent Application Laid-Open No. 6-92701, in order to recycle waste bricks as building materials,
A method of pulverizing into a round material having a size of about 20 to 120 mm is proposed. In this method, waste brick is pulverized by a machine such as a pyrene, a jaw crusher, and a squaring device.
【0007】以上のように、廃レンガを再使用処理する
ために粉砕する必要がある場合、粉砕機械を使って粉砕
することが一般的に行われている方法である。[0007] As described above, when it is necessary to pulverize waste bricks for reuse treatment, pulverization using a pulverizing machine is a commonly practiced method.
【0008】[0008]
【発明が解決しようとする課題】溶錬炉を解体又は修理
する際に発生する廃レンガの寸法は成型されたときの寸
法のものからこれより大きい塊まで様々である。そし
て、数百mm大の廃レンガも多く発生するので、これを
例えば20mm以下に粉砕しようとすると、2〜3段の
粉砕機及び分級設備が必要であるので設備費が大きく、
また2〜3段粉砕・分級は容易な作業ではない。よっ
て、より簡単に細かく粉砕する方法が望まれている。The size of waste bricks generated when disassembling or repairing a smelting furnace varies from the size at the time of molding to the size of a larger block. And, since many waste bricks of several hundred mm in size are also generated, if this is to be crushed to, for example, 20 mm or less, a two-to-three-stage crusher and a classifying facility are required, so the equipment cost is large,
In addition, pulverization and classification in two or three stages is not an easy task. Therefore, a method of pulverizing more easily and finely is desired.
【0009】また、銅の溶錬炉から発生する廃レンガ中
の銅分は網目状にレンガの内部に浸透しているので、廃
レンガから確実に銅分を回収するには、廃レンガを溶錬
炉に繰り返した際に、レンガ部分に速やかに溶解できる
ように、粉砕粒度を可能な限り細かくすることが望まし
い。しかしながら、粉砕粒度をより細かくするために
は、さらに粉砕・分級段数が増加し、設備数及びランニ
ングコストが増大するという問題があった。[0009] Further, since the copper content in the waste brick generated from the copper smelting furnace permeates into the brick in a mesh-like manner, in order to reliably recover the copper content from the waste brick, the waste brick is melted. It is desirable to make the pulverized particle size as small as possible so that it can be quickly dissolved in the brick portion when it is repeated in a smelting furnace. However, in order to further reduce the pulverization particle size, there is a problem that the number of pulverization / classification stages further increases, and the number of facilities and running costs increase.
【0010】[0010]
【課題を解決するための手段】本発明は、上述の問題点
を解決する方法であって、金属溶錬炉の使用済み廃レン
ガを2気圧以上の水蒸気と接触せしめることにより粉砕
することを特徴とする金属溶錬炉の廃レンガ処理方法を
提供する。以下、本発明の構成を説明する。According to the present invention, there is provided a method for solving the above-mentioned problems, wherein a used waste brick of a metal smelting furnace is pulverized by bringing it into contact with steam of 2 atm or more. The present invention provides a method for treating a waste brick of a metal smelting furnace. Hereinafter, the configuration of the present invention will be described.
【0011】本発明において廃レンガは金属の溶錬炉に
通常使用される塩基性耐火レンガであり、特にMgO及
び/又はCaOを主成分とし、より好ましくはマグクロ
レンガ、マグネシアレンガである。MgO及びCaOは
水との反応により水和反応(通称「スレーキング)を起
こすことが知られている。本発明においては、MgO等
を含む廃レンガでは水和反応がその塊の内部で起こっ
て、局部的に体積が膨張することを利用して、解体され
たままの廃レンガを粉状に破壊する。この反応と体積膨
張を廃レンガの破壊に有効に利用するためには水蒸気雰
囲気は圧力が2気圧以上であることが必要である。この
ように加圧条件で水蒸気処理を行うことにより強制的に
スレーキングを進行させ、廃レンガを細かく粉砕するこ
とができる。In the present invention, the waste brick is a basic refractory brick usually used in a metal smelting furnace, particularly a main brick containing MgO and / or CaO, and more preferably a magcro brick or a magnesia brick. It is known that MgO and CaO cause a hydration reaction (commonly referred to as “slaking”) by reaction with water.In the present invention, in a waste brick containing MgO or the like, the hydration reaction occurs inside the lump, Utilizing the local expansion of the volume, the dismantled waste bricks are broken into powder.To effectively utilize this reaction and volume expansion for the destruction of the waste bricks, the water vapor atmosphere has to be pressurized. By performing the steam treatment under the pressurized condition, the slaking is forcibly progressed, and the waste brick can be finely pulverized.
【0012】水蒸気の温度は100℃以上310℃以下
が好ましく、望ましくは150℃以上250℃以下であ
る。これらを飽和水蒸気圧力に換算すると1.0気圧以
上、100気圧以下望ましくは4.9気圧以上40気圧
以下である。一般的に言って、水蒸気圧力は高いほうが
水和反応の速度が大きく、粉砕が短時間で完了する。一
方、水蒸気圧を高くすると、反応装置の密閉性及び耐圧
性確保のために装置製作費用が高くなるので、必要以上
に圧力を高めるのは好ましくない。したがって好ましい
水蒸気圧力は上記範囲である。本発明が特徴とする水蒸
気による処理はオートクレーブ内で行うことが好まし
い。この場合標準的処理時間は8〜12時間である。[0012] The temperature of the steam is preferably from 100 ° C to 310 ° C, and more preferably from 150 ° C to 250 ° C. When these are converted into saturated steam pressures, they are 1.0 atm or more and 100 atm or less, preferably 4.9 atm or more and 40 atm or less. Generally speaking, the higher the steam pressure, the faster the hydration reaction, and the pulverization is completed in a short time. On the other hand, if the water vapor pressure is increased, the production cost of the apparatus increases in order to ensure the hermeticity and pressure resistance of the reaction apparatus. Therefore, it is not preferable to increase the pressure more than necessary. Therefore, the preferable steam pressure is in the above range. The treatment with steam, which is a feature of the present invention, is preferably performed in an autoclave. In this case the standard processing time is between 8 and 12 hours.
【0013】廃レンガは銅の溶錬炉のみならず鉄鋼その
他の金属の溶錬炉から発生するものであっても本方法に
より処理をすることが可能である。銅の溶錬炉の廃レン
ガは一般に有価成分として、Cu:10〜15重量%、
Au:30ppm,Ag:0.01重量%,Pb0.1
重量%,Zn:0.1%などを含有している。これらの
成分を含有する廃レンガは本発明法により粉砕した後に
銅の溶錬炉に繰り返して、有価金属を回収する。The waste brick can be treated by the present method not only from a copper smelting furnace but also from a steel or other metal smelting furnace. Waste bricks of copper smelting furnaces are generally valuable components of Cu: 10 to 15% by weight,
Au: 30 ppm, Ag: 0.01% by weight, Pb0.1
%, Zn: 0.1%, etc. Waste bricks containing these components are pulverized according to the method of the present invention, and thereafter repeatedly used in a copper smelting furnace to recover valuable metals.
【0014】[0014]
【作用】上記の水和反応は、MgOの場合MgO+H2
O→Mg(OH)2 と表される。常温・常圧下では、こ
の水和反応は緩やかに進行するため、マグクロレンガ等
では、完全に粉砕するのに数日以上かかる。またマグク
ロレンガは常温の水に浸漬した場合では、14日間かけ
てもレンガに全く変化が生じない。さらに、105℃の
水蒸気(飽和水蒸気圧力≒1気圧)に20時間曝して
も、ようやく亀裂が生じる程度である。しかし、この水
和反応において水蒸気圧力を高めれば、反応速度が大き
くなり、短い時間で粉砕することが可能となる。以上M
gOについて説明したが、CaOの場合も同様に短時間
粉砕が可能である。以下、実施例によりさらに詳しく本
発明を説明する。The above hydration reaction is performed in the case of MgO with MgO + H 2
O → Mg (OH) 2 . At normal temperature and normal pressure, this hydration reaction proceeds slowly, and it takes several days or more to completely pulverize with a magcro brick or the like. When the magcro brick is immersed in water at room temperature, no change occurs in the brick even after 14 days. Further, even when exposed to steam at 105 ° C. (saturated steam pressure ≒ 1 atm) for 20 hours, cracks are finally generated. However, if the water vapor pressure is increased in this hydration reaction, the reaction rate increases, and it becomes possible to pulverize in a short time. More than M
Although gO has been described, similarly for CaO, short time pulverization is possible. Hereinafter, the present invention will be described in more detail with reference to examples.
【0015】[0015]
実施例1 銅溶錬炉のマグクロ廃レンガを、A:金属銅浸入レンガ
及びB:銅硫化物(鉄分も含有)浸入レンガの2種類に
分別し、実験に供した。実験用のオ−トクレ−ブ(内容
積1.0リットル)を用いて、表1に示す3つの条件で
廃レンガA及びBの処理実験を行った。Example 1 Waste magcro bricks of a copper smelting furnace were separated into two types of bricks: A: metal copper infiltrated bricks and B: copper sulfide (including iron) infiltrated bricks, and subjected to an experiment. Using the experimental autoclave (internal volume 1.0 liter), treatment experiments of waste bricks A and B were performed under the three conditions shown in Table 1.
【0016】[0016]
【表1】 温度(℃) 水蒸気圧(気圧) 保持時間(Hr ) 条件 i 225 28 7.0 条件 ii 200 17 7.0 条件 iii 150 5 7.0 Table 1 Temperature (° C) Water vapor pressure (atmospheric pressure) Retention time (Hr) Condition i 225 28 7.0 Condition ii 200 17 7.0 Condition iii 150 5 7.0
【0017】その結果得られた粉砕程度を表2に示す。Table 2 shows the degree of pulverization obtained as a result.
【0018】[0018]
【表2】 廃レンガA 廃レンガB 条件 i 全壊(粉状) 全壊(粉状) 条件 ii 全壊(粉状) 全壊(一部粒状) 条件 iii 半壊(粒状) 半壊(粒状) [Table 2] Waste brick A Waste brick B Condition i Completely destroyed (powder) Completely destroyed (powder) Condition ii Completely destroyed (powder) Completely destroyed (partially granular) Conditions iii Semi-destructed (granular) Semi-destructed (granular)
【0019】以上の結果から条件iii 以上の高温・高圧
であれば廃レンガを十分効率的に粉砕できることがわか
った。From the above results, it was found that the waste brick could be pulverized sufficiently efficiently at a high temperature and a high pressure under the condition iii.
【0020】実施例2 銅溶錬炉から発生したマグクロ廃レンガで大半の大きさ
が120mm×150mm×250mm程度の長方体状
であり、最も小さいものでも1辺の長さが100mmの
立方体より大きい廃レンガを実操業用のオートクレーブ
(内容積3.8m3 )を用いて水蒸気処理した。実験条
件は、水蒸気圧力(最大)15.9気圧、最大圧力での
保持時間10時間であった。その結果、処理後の廃レン
ガも粒度分布を測定した結果を表3に示す。Example 2 Most of the waste magcro brick generated from a copper smelting furnace has a rectangular shape of about 120 mm × 150 mm × 250 mm, and the smallest one is smaller than a cube having a side length of 100 mm. The large waste brick was steam-treated using an autoclave (3.8 m 3 in volume) for actual operation. The experimental conditions were a steam pressure (maximum) of 15.9 atmospheres and a holding time at the maximum pressure of 10 hours. As a result, the results of measuring the particle size distribution of the treated waste bricks are shown in Table 3.
【0021】[0021]
【表3】 粒度 廃レンガA 廃レンガB +30mm − 5 −30/+10mm 7 8 −10/+3mm 15 11 −3mm 78 76 [Table 3] Particle size Waste brick A Waste brick B +30 mm −5 −30 / + 10 mm 78 −10 / + 3 mm 15 11 −3 mm 78 76
【0022】比較例1 常温の水に廃レンガA及びBを浸漬し、毎日外観と圧壊
強度を調べた。その結果、廃レンガA、Bともに14日
経過してもこれらの性質は全く変化が生じなかった。Comparative Example 1 Waste bricks A and B were immersed in water at room temperature, and the appearance and crushing strength were examined every day. As a result, these properties did not change at all even after 14 days in both of the waste bricks A and B.
【0023】比較例2 円筒容器内(内容積5リットル)に廃レンガ(80mm
角)を入れ、容器へ水蒸気(水蒸気圧=1気圧)を流し
続けた。その間、容器内の温度は100〜105℃で推
移した。20時間経過した後、容器から廃レンガを取り
出して調べたところ、幅1mm長さ3mm程度の亀裂が
発生した程度で、圧壊強度は変化しなかった。Comparative Example 2 A waste brick (80 mm) was placed in a cylindrical container (with an inner volume of 5 liters).
Corner), and steam (steam pressure = 1 atm) was continuously flowed into the container. During that time, the temperature in the container changed between 100 and 105 ° C. After elapse of 20 hours, the waste brick was taken out of the container and examined. As a result, a crack having a width of about 1 mm and a length of about 3 mm was generated, and the crushing strength did not change.
【0024】比較例3 粉砕機1:ジョークラッシャ(出力75kW)及び粉砕
機2:ハンマークラッシャ(出力55kW)を用いて、
機械による粉砕についても実験を行った。 実験条件 廃レンガ(B)の元々の大きさは200〜400m
m, 粉砕機1で1段目、粉砕機2で2段目の粉砕を行っ
た。 各粉砕機では噛み込み等のトラブルが起きない範囲
で、出来るだけ細かく粉砕した。その結果を表4(粉砕
後の寸法に対する割合(重量%))に示す。Comparative Example 3 Using a crusher 1: a jaw crusher (output: 75 kW) and a crusher 2: a hammer crusher (output: 55 kW)
Experiments were also conducted on mechanical grinding. Experimental conditions The original size of the waste brick (B) is 200-400m
m, the first stage was crushed by the crusher 1 and the second stage was crushed by the crusher 2. Each pulverizer was pulverized as finely as possible without causing troubles such as biting. The results are shown in Table 4 (ratio to weight after grinding (% by weight)).
【0025】[0025]
【表4】 粉砕機1処理後 粉砕機2処理後 +100mm − −* −100/+80mm 4.8 −* −80/+50mm 22.2 −* −50/+30mm 38.7 38.5 −30/+10mm 25.9 41.4 −10/+5mm 4.3 8.3 −5mm 4.1 11.8 備考 *:粉砕機2では構造上50mmアンダーしか排出されない。[Table 4] After treatment with crusher 1 After treatment with crusher 2 +100 mm − − * −100 / + 80 mm 4.8 − * −80 / + 50 mm 22.2 − * −50 / + 30 mm 38.7 38.5 −30 / + 10 mm 25.9 41.4 -10 / + 5 mm 4.3 8.3 -5 mm 4.1 11.8 Remarks *: In the crusher 2, only 50 mm under is discharged due to its structure.
【0026】表4を実施例2の表3と比較すると、粉砕
後の粒度が粗いことが判る。機械による粉砕法で、実施
例2(高圧水蒸気によるスレーキング)と同等の粒度に
粉砕しようとすると、さらに追加で1〜2段の粉砕が必
要となる。Comparison of Table 4 with Table 3 of Example 2 shows that the particle size after grinding is coarse. If it is attempted to grind to a particle size equivalent to that of Example 2 (slaking with high-pressure steam) by a mechanical pulverization method, one or two additional pulverizations are required.
【0027】[0027]
【発明の結果】従来は、廃レンガを溶錬炉に繰り返す際
に前処理として、機械的粉砕を行なっていたが、本発明
では、化学反応すなわち酸化物の水和反応を利用して粉
砕するので、容易に細かく粉砕できる。細かく粉砕する
ことにより、廃レンガに含まれている有価物の回収が容
易となる。すなわち、細かく粉砕された廃レンガは、繰
り返された溶錬炉において確実に溶解し、銅分などの有
価物が溶湯に回収されレンガ分はスラグに移行する。As a result, mechanical pulverization has been conventionally performed as a pretreatment when waste bricks are repeated in a smelting furnace. However, in the present invention, pulverization is performed using a chemical reaction, that is, a hydration reaction of oxides. Therefore, it can be easily crushed finely. By finely crushing, it becomes easy to collect valuable resources contained in the waste brick. That is, the finely ground waste brick is reliably melted in the repeated smelting furnace, valuables such as copper are recovered in the molten metal, and the brick is transferred to slag.
【0028】また、有価物の回収目的以外にも、産業廃
棄物として埋め立て等の処分が難しい廃レンガを溶錬炉
でスラグに溶解させ廃棄可能とする場合や、建築材料と
してリサイクルする場合などにも廃レンガの前処理(粉
砕)方法として有効である。In addition to the purpose of recovering valuable resources, there are cases where waste bricks which are difficult to dispose of as landfills as industrial waste can be dissolved in slag in a smelting furnace and discarded, or when recycled as building materials. This is also effective as a pretreatment (crushing) method for waste bricks.
───────────────────────────────────────────────────── フロントページの続き (72)発明者 広瀬 哲夫 大分県北海部郡佐賀関町3の3382 日鉱 金属株式会社佐賀関製錬所内 ────────────────────────────────────────────────── ─── Continued on the front page (72) Inventor Tetsuo Hirose 3382 Nippon Mining & Metals Co., Ltd., Saganoseki Smelter & Refinery, 3 Sagaseki-cho, North Sea District County, Oita Prefecture
Claims (3)
ら、該溶錬炉を修理又は解体した際に発生した使用済み
廃レンガを、予め機械的に破砕することなく、2気圧以
上の水蒸気と接触させることにより粉砕することを特徴
とする金属溶錬炉の廃レンガ処理方法。1. At least 2 atm of used waste brick generated when a smelting furnace is repaired or dismantled is mechanically crushed from bricks in contact with molten metal in a copper smelting furnace without mechanical crushing in advance. A method for treating waste bricks in a metal smelting furnace, comprising crushing by contacting with water vapor.
ことを特徴とする請求項1記載の金属溶錬炉の廃レンガ
処理方法。2. The method according to claim 1, wherein the contact treatment is performed in an autoclave.
れた廃レンガを銅の溶錬炉で溶解し有価物を回収するこ
とを特徴とする金属溶錬炉の廃レンガ処理方法。3. A method for treating waste bricks in a metal smelting furnace, comprising melting waste bricks crushed by the method according to claim 1 in a copper smelting furnace and collecting valuable resources.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP11140295A JP3292271B2 (en) | 1995-05-10 | 1995-05-10 | Waste brick treatment method for metal smelting furnace |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP11140295A JP3292271B2 (en) | 1995-05-10 | 1995-05-10 | Waste brick treatment method for metal smelting furnace |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH08299835A JPH08299835A (en) | 1996-11-19 |
| JP3292271B2 true JP3292271B2 (en) | 2002-06-17 |
Family
ID=14560249
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP11140295A Expired - Lifetime JP3292271B2 (en) | 1995-05-10 | 1995-05-10 | Waste brick treatment method for metal smelting furnace |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP3292271B2 (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP5488098B2 (en) * | 2010-03-24 | 2014-05-14 | 住友金属鉱山株式会社 | Treatment method for acid-resistant waste bricks |
| KR20240031377A (en) * | 2021-08-27 | 2024-03-07 | 제이에프이 스틸 가부시키가이샤 | How to recycle magnesia carbon bricks |
-
1995
- 1995-05-10 JP JP11140295A patent/JP3292271B2/en not_active Expired - Lifetime
Also Published As
| Publication number | Publication date |
|---|---|
| JPH08299835A (en) | 1996-11-19 |
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