JPH0128820B2 - - Google Patents
Info
- Publication number
- JPH0128820B2 JPH0128820B2 JP59013807A JP1380784A JPH0128820B2 JP H0128820 B2 JPH0128820 B2 JP H0128820B2 JP 59013807 A JP59013807 A JP 59013807A JP 1380784 A JP1380784 A JP 1380784A JP H0128820 B2 JPH0128820 B2 JP H0128820B2
- Authority
- JP
- Japan
- Prior art keywords
- slag
- dust
- sludge
- agglomerated
- dry
- 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
Links
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
Landscapes
- Processing Of Solid Wastes (AREA)
- Manufacture And Refinement Of Metals (AREA)
Description
本発明は反応熱源として各種金属製錬炉や溶解
炉から排出される高温の溶滓が持つ顕熱を用い、
ステンレス鋼等の特殊鋼のダスト、スラツジ類、
Niメツキスラツジ等の含Niダスト、スラツジ類
に含有されている有価金属、特にNi、次いでFe,
Crを濃縮回収する方法に関するものである。
特殊鋼製造に際して発生するダスト、スラツジ
類は酸化鉄を主成分とするが、数パーセントの
Ni,Crを含みながら低品位であり、しかもPb,
Zn,Cu,Cd,S,Fなどの有害成分も含むため
に、Ni,Cr原料としての活用も出来ずに産業廃
棄物として多類の費用をかけて処分されている。
またNiメツキスラツジもその性質上活用され
ることなく産業廃棄物として処分される。
一方製鉄業において発生する高炉、転炉、電気
炉、合金鉄用電気炉などの各種炉から排出される
溶滓は高温のまま排出されておりその莫大な熱エ
ネルギーは未利用のまま無駄に放冷されているの
が現状である。
そこで本願は上記の未利用熱エネルギーの利用
に着目し、ダスト、スラツジ類をこれらの高温溶
滓中に投入して、そのエネルギーにより有用成分
主としてNi,Fe,Crとしてをメタル再生回収す
ると共に、他の成分は完全に滓化せしめて無公害
化処理することを目的としたものである。
この種の研究としては本願出願人が以前に研究
出願した特願昭48−111306(溶滓を利用した製鋼
ダスト、スラツジからの有価金属回収方法)があ
り、この方法は還元剤を内装したダスト、スラツ
ジのプリケツトまたはペレツトを作り、転炉や電
気炉の溶滓鍋底にあらかじめ入れておいて、その
上から高温の溶滓を流入する方法であるが、この
方法によると製鋼操業の変化に対応したプリケツ
トまたはペレツトの装入適正量の調節が出来ず、
時として未反応ダスト、スラツジのプリケツトま
たはペレツトの残る欠点を有していることが確認
出来た。
そこで本願発明方法では上記の欠点を解消し、
さらに有価金属の回収を容易として有害成分の無
公害化処理をより完全ならしめようとする方法を
提供するものであり、その要旨とするところは、
第1工程:特殊鋼ダスト、スラツジ類と、該ダス
ト、スラツジ類中の金属化合物と反応するに必
要な量の炭素質還元剤とアルカリ金属炭酸塩と
を混合塊成化する。
第2工程:第1工程で得られた塊成化物を乾燥予
熱する。
第3工程:第2工程で得られた乾燥塊成化物を高
温溶滓と共に溶滓鍋内に装入し、該溶滓の持つ
顕熱により還元反応を生起せしめ、主として
Ni,Fe,Crの有価金属をメタル化させる。
第4工程:溶滓鍋内の物を冷却凝固し、次いで破
砕した後通常の選鉱手段でメタル化したNi,
Fe,Crを回収する。
上記の各工程より成る溶滓顕熱を利用したダス
ト、スラツジ類からの有価金属回収方法でありこ
の際に用いる炭素質還元剤として通常はコークス
粉や木炭粉等の炭素質還元剤を用い、又アルカリ
金属炭酸塩としては通常安価なNa2CO3やK2CO3
を用いる。
なお第1工程ではダスト、スラツジ類に炭素質
還元剤とアルカリ金属炭酸塩を共に添加混錬し
て、プリケツトまたはペレツト状に塊成化する
が、炭素質還元剤をの添加量はNi,Fe,Cr還元
に必要な理論量の1〜5倍、アルカリ金属炭酸塩
の添加量はNa2CO3やK2CO3を用いる場合炭素質
還元剤添加量の50%以上とすることが好ましく、
又炭素質還元剤の粒度は約5m/m以下が好まし
い。
次に第2工程は第1工程で得られた塊成化物に
含まれる水分を乾燥除去する工程で、水分による
溶滓顕熱の熱損失を防止する為にも重要である。
更に溶滓中に投入された塊成化物の破裂粉化を防
止する上からも効果を有する。
第3工程は高温の溶滓中に第2工程よりの塊成
化物を投入する工程で、溶滓鍋への溶滓の落下乱
流または高圧気体吹き込みや機械的撹拌による溶
の人工乱流によつて塊成化物を溶滓中に投入せし
め顕熱によるNi,Fe,Crの還元反応を促進する
工程であるが、Ni,Fe,Cr化合物は先ず温度の
上昇と共に塊成化物内で炭素質還元剤によつて還
元され、メタル粒子となる。次いで塊成化物に含
まれる脈石成分のスラダ化による軟化と共にメタ
ル粒子は成長して脈石成分と分離され独立のメタ
ル粒となる。この間に於いて添加したアルカリ金
属炭酸塩は熱分解によつてCoを発生し、還元促
進に寄与すると同時に、アルカリ金属酸化物とな
つて脈石成分の溶融軟化点を下げメタル粒の生長
に大きく影響し後工程での物理選鉱を容易とする
特徴がある。しかしながら塊成化物の投入量は溶
滓顕熱に応じた量が大切で、通常溶滓量の約30%
以下である。
次に本発明を合金鉄溶滓に応用した場合を第1
図を参酌し乍ら詳述する。
図中1は合金鉄用電気炉、2は合金鉄メタル用
の取鍋、3は溶滓鍋、4は溶滓、5は乾燥予熱さ
れたプリケツト、6はプリケツト投入用フイダ
ー、7はプリケツト乾燥予熱装置、8は製団機、
9は処理を完了した溶滓、10は選鉱装置を示
す。
合金鉄用電気炉1から出湯されたメタルと溶滓
はメタル用の取鍋2内で比重分離されて、溶滓4
のみが次の溶滓鍋3中に溢流落下して貯留され
る。一方ダスト、スラツジ類と炭素質還元剤,ア
ルカリ金属炭酸塩とを混合して、また必要によつ
ては製団用のバインダーを加えて、製団機8でプ
リケツトを作り、乾燥予熱装置7によつて乾燥予
熱されたプリケツト5はフイダー6に準備する。
しかし溶滓4が溶滓鍋3に落下する時に乾燥予
熱プリケツト5をフイダー6から同時に落下せし
めて溶滓鍋3内で良く混合し溶滓4の顕熱を充分
にプリケツトに伝達せしめて、プリケツト中Ni
やFe,Crの還元反応を促進する。プリケツト内
の温度が約900℃以上となると、あたかも密閉容
器に類似したプリケツト内で還元反応が起こり主
としてメタルNi,Fe,Crの生成を見るもので、
実際にはFe−Ni−Cr合金の生成となる。
次いで処理を完了した溶滓9は放流または溶滓
鍋3内で冷却凝固された後に、選鉱工程10に送
つて破砕、磁力選鉱、比重選鉱などによつてNi,
Fe,Crを主体とした還元メタル粒を回収する。
以下本発明の試験実施例を示す。
試験実施例
エル−式電気炉1tでフエロクロムスラグを再
溶解して作つた約600Kgの溶滓を第2図にて示す
ごとく鉄製の溶滓鍋3に流入して、次いで溶滓中
にランスパイプ11を挿入、高圧空気にて溶滓を
パプリングさせながら、あらかじめステンレス製
鋼ダストに外割りで粉コークス15重量部とソーダ
灰5重量部を内装して製団し充分に乾燥したプリ
ケツト50Kgを1分間に5Kgの投入速度で溶滓中に
挿入した後に約3時間放置し転倒凝固せしめて常
温に冷却後−3m/m以下に粉砕して磁力選鉱を
行つた結果は下記のごとくであつた。
The present invention uses sensible heat possessed by high-temperature slag discharged from various metal smelting furnaces and melting furnaces as a reaction heat source,
Dust and sludge of special steel such as stainless steel,
Valuable metals contained in Ni-containing dust and sludge, especially Ni, followed by Fe,
This invention relates to a method for concentrating and recovering Cr. The dust and sludge generated during the manufacture of special steel are mainly composed of iron oxide, but a few percent of the dust and sludge are
Although it contains Ni and Cr, it is of low quality, and it also contains Pb,
Because it contains harmful components such as Zn, Cu, Cd, S, and F, it cannot be used as a raw material for Ni or Cr, and is disposed of as industrial waste at great expense. Additionally, due to its nature, nickel metal is not utilized and is disposed of as industrial waste. On the other hand, the slag discharged from various furnaces such as blast furnaces, converters, electric furnaces, and electric furnaces for ferroalloys generated in the steel industry remains at a high temperature, and a huge amount of thermal energy is wasted unused. The current situation is that it is cold. Therefore, this application focuses on the use of the above-mentioned unused thermal energy, and puts dust and sludge into these high-temperature slags, and uses the energy to regenerate and recover useful components mainly Ni, Fe, and Cr as metals. The purpose of the other components is to completely turn them into slag and make them non-polluting. As for this type of research, there is a patent application No. 111306 (Sho 48-111306) (method for recovering valuable metals from steelmaking dust and sludge using molten slag), which was previously filed by the applicant. In this method, sludge briquettes or pellets are made and placed in the bottom of the slag pot of a converter or electric furnace, and then high-temperature slag is poured over the top of the slag.This method can accommodate changes in steelmaking operations. It is not possible to adjust the appropriate amount of charged prickets or pellets.
It has been confirmed that the process sometimes has the disadvantage of remaining unreacted dust, sludge prickets or pellets. Therefore, the method of the present invention solves the above drawbacks,
Furthermore, the present invention provides a method that facilitates the recovery of valuable metals and makes the pollution-free treatment of harmful components more complete. A carbonaceous reducing agent and an alkali metal carbonate in an amount necessary to react with the metal compound in the dust or sludge are mixed and agglomerated. Second step: Dry and preheat the agglomerated product obtained in the first step. 3rd step: The dry agglomerated material obtained in the 2nd step is charged into a slag pot together with the high temperature slag, and a reduction reaction is caused by the sensible heat of the slag, mainly
Metalizes valuable metals such as Ni, Fe, and Cr. 4th step: The material in the slag pot is cooled and solidified, then crushed and metalized using normal ore beneficiation methods.
Recover Fe and Cr. This is a method of recovering valuable metals from dust and sludge using the sensible heat of the slag, which consists of each of the above steps.The carbonaceous reducing agent used in this process is usually coke powder, charcoal powder, etc. In addition, Na 2 CO 3 and K 2 CO 3 are usually inexpensive as alkali metal carbonates.
Use. In the first step, a carbonaceous reducing agent and an alkali metal carbonate are added and kneaded to dust and sludge, and agglomerated into pellets or pellets. , 1 to 5 times the theoretical amount required for Cr reduction, and the amount of alkali metal carbonate added is preferably 50% or more of the amount of carbonaceous reducing agent added when Na 2 CO 3 or K 2 CO 3 is used.
Further, the particle size of the carbonaceous reducing agent is preferably about 5 m/m or less. Next, the second step is a step of drying and removing moisture contained in the agglomerated material obtained in the first step, and is also important for preventing heat loss of sensible heat of the slag due to moisture.
Furthermore, it is also effective in preventing the agglomerated material introduced into the slag from bursting into powder. The third step is a step in which the agglomerates from the second step are introduced into the hot slag, resulting in turbulent flow of the slag falling into the slag pot or artificial turbulence of the melt caused by high-pressure gas blowing or mechanical stirring. Therefore, this is a process in which the agglomerates are introduced into the slag to promote the reduction reaction of Ni, Fe, and Cr by sensible heat, but the Ni, Fe, and Cr compounds first become carbonaceous within the agglomerates as the temperature rises. It is reduced by a reducing agent and becomes metal particles. Next, as the gangue component contained in the agglomerate is softened by sludging, the metal particles grow and are separated from the gangue component to become independent metal grains. The alkali metal carbonate added during this period generates Co through thermal decomposition, contributing to the promotion of reduction, and at the same time becomes an alkali metal oxide, lowering the melting softening point of gangue components and greatly promoting the growth of metal grains. It has the characteristic of making physical beneficiation easier in the subsequent process. However, it is important that the amount of agglomerate added is in accordance with the sensible heat of the slag, and is usually about 30% of the amount of slag.
It is as follows. Next, the first case where the present invention is applied to ferroalloy slag will be described.
The details will be explained with reference to the figures. In the figure, 1 is an electric furnace for ferroalloy metal, 2 is a ladle for ferroalloy metal, 3 is a slag ladle, 4 is a molten slag, 5 is a dry preheated pricket, 6 is a feeder for feeding the pricket, and 7 is a pricket dryer. Preheating device, 8 is a dough making machine,
9 shows the slag that has been processed, and 10 shows the ore processing device. The metal and molten slag tapped from the electric furnace 1 for ferroalloy are separated by specific gravity in the metal ladle 2, and the molten slag 4
Only the slag overflows and falls into the next slag pot 3 and is stored there. On the other hand, dust and sludge are mixed with a carbonaceous reducing agent and an alkali metal carbonate, and if necessary, a binder for making a dough is added to make a preket in a dough making machine 8. The dried and preheated pricket 5 is then prepared in the feeder 6. However, when the slag 4 falls into the slag ladle 3, the dry preheated pricket 5 is simultaneously dropped from the feeder 6 to mix well in the slag ladle 3 and sufficiently transfer the sensible heat of the slag 4 to the pricket. Medium Ni
It promotes the reduction reaction of Fe, Cr. When the temperature inside the pricket reaches about 900℃ or higher, a reduction reaction occurs inside the pricket, which is similar to a closed container, and mainly produces metals Ni, Fe, and Cr.
In reality, an Fe-Ni-Cr alloy is formed. Next, the treated slag 9 is discharged or cooled and solidified in the slag ladle 3, and then sent to the beneficiation step 10, where Ni, Ni, ore is removed by crushing, magnetic beneficiation, specific gravity beneficiation, etc.
Collect reduced metal particles mainly composed of Fe and Cr. Test examples of the present invention will be shown below. Test Example Approximately 600 kg of slag made by remelting ferrochrome slag in a 1 ton L-type electric furnace flows into an iron slag ladle 3 as shown in Figure 2, and then into the slag. Insert the lance pipe 11, and while pumping the slag with high-pressure air, add 50 kg of slag that has been thoroughly dried by pre-mixing 15 parts by weight of coke powder and 5 parts by weight of soda ash inside the stainless steel dust. After inserting it into the slag at a rate of 5 kg per minute, it was left to stand for about 3 hours, allowed to solidify by falling over, cooled to room temperature, crushed to below -3 m/m, and subjected to magnetic beneficiation. The results were as follows. .
【表】
※ %は全て重量%である。
上記の結果より溶滓中に投入されたプリケツト
主成分の磁着メタルの回収率を計算してみると、
Ni回収率=18Kg×0.0535/50Kg×0.0203×100=94.87(
%)
Fe回収率=18Kg×0.7446/50Kg×0.3002×100=89.29(
%)
Cr回収率=18Kg×0.1407/50Kg×0.0574×100=88.24(
%)
となり、然も回収されたメタルの粒度分布は下記
のごとく、粗大粒子のメタル回収となつた。[Table] * All percentages are by weight.
Based on the above results, we calculated the recovery rate of the magnetic metal, which is the main component of the briquettes, put into the slag. Ni recovery rate = 18Kg x 0.0535/50Kg x 0.0203 x 100 = 94.87 (
%) Fe recovery rate = 18Kg x 0.7446/50Kg x 0.3002 x 100 = 89.29 (
%) Cr recovery rate = 18Kg x 0.1407/50Kg x 0.0574 x 100 = 88.24 (
%), and the particle size distribution of the recovered metal was as shown below, indicating that the recovered metal was coarse particles.
【表】
以上の試験実施例のごとく、現在産業廃棄物と
して処分され、その活用が困難であつたダスト、
スラツジ類も、本発明によればNi,Fe,Crの選
択濃縮回収が可能であり極めて有利である。
しかも従来無駄にされていた溶滓顕熱を有効に
活用すると共に、公害問題上深刻化しているダス
ト、スラツジ類の無公害化処理がNi,Fe,Crの
回収と同時に実施し得ることは産業上極めて意義
が大きい。[Table] As shown in the test examples above, dust that is currently disposed of as industrial waste and has been difficult to utilize,
According to the present invention, sludges are also extremely advantageous because Ni, Fe, and Cr can be selectively concentrated and recovered. Furthermore, it is possible to effectively utilize the sensible heat of the slag that was wasted in the past, and to decontaminate dust and sludge, which are becoming increasingly serious pollution problems, at the same time as collecting Ni, Fe, and Cr. This is extremely significant.
第1図は本願方法の工程説明図、第2図は本発
明を開発した試験実施例の説明図。
図中、1:電気炉、2:メタル用取鍋、3:溶
滓鍋、4:溶滓、5:乾燥プリケツト、6:プリ
ケツト投入フイダー、7:プリケツト乾燥予熱装
置、8:製団機、9:処理後の溶滓、10:選鉱
工程、11:高圧空気ランスパイプ。
FIG. 1 is an explanatory diagram of the process of the present method, and FIG. 2 is an explanatory diagram of a test example in which the present invention was developed. In the figure, 1: electric furnace, 2: ladle for metal, 3: slag ladle, 4: slag, 5: drying pricket, 6: pricket input feeder, 7: pricket drying preheating device, 8: slag making machine, 9: Slag after treatment, 10: Mineral beneficiation process, 11: High pressure air lance pipe.
Claims (1)
スト、スラツジ類からの有価金属回収方法。 第1工程:ダスト、スラツジ類と、該ダスト、ス
ラツジ類中の金属化合物と反応するに必要な量
の炭素質還元剤とアルカリ金属炭酸塩とを混合
塊成化する。 第2工程:第1工程で得られた塊成化物を乾燥予
熱する。 第3工程:第2工程で得られた乾燥塊成化物を高
温溶滓と共に溶滓鍋内に装入し、該溶滓の持つ
顕熱により還元反応を生起せしめ、主として
Ni,Fe,Crの有価金属をメタル化させる。 第4工程:溶滓鍋内の物を冷却凝固し、次いで破
砕した後通常の選鉱手段でメタル化したNi,
Fe,Crを回収する。 2 第1工程で用いるアルカリ金属炭酸塩、
Na2CO3あるいはK2CO3であることを特徴とする
特許請求の範囲第1項記載の方法。 3 第3工程で溶滓鍋内に、乾燥塊成化物と高温
溶滓とを装入するに際しそれらを同時に装入する
ことを特徴とする特許請求の範囲第1項若しくは
2項のいずれかに記載の方法。[Claims] 1. A method for recovering valuable metals from dust and sludge using the sensible heat of slag, which comprises the following steps. First step: Dust and sludge are mixed and agglomerated with a carbonaceous reducing agent and alkali metal carbonate in amounts necessary to react with the metal compounds in the dust and sludge. Second step: Dry and preheat the agglomerated product obtained in the first step. 3rd step: The dry agglomerated material obtained in the 2nd step is charged into a slag pot together with the high temperature slag, and a reduction reaction is caused by the sensible heat of the slag, mainly
Metalizes valuable metals such as Ni, Fe, and Cr. 4th step: The material in the slag pot is cooled and solidified, then crushed and metalized using normal ore beneficiation methods.
Recover Fe and Cr. 2 Alkali metal carbonate used in the first step,
The method according to claim 1, characterized in that Na 2 CO 3 or K 2 CO 3 is used. 3. According to either claim 1 or 2, wherein the dry agglomerated material and the high-temperature slag are charged simultaneously into the slag pot in the third step. Method described.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP59013807A JPS60159130A (en) | 1984-01-27 | 1984-01-27 | Method for recovering valuable metal from dust, sludge or the like |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP59013807A JPS60159130A (en) | 1984-01-27 | 1984-01-27 | Method for recovering valuable metal from dust, sludge or the like |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS60159130A JPS60159130A (en) | 1985-08-20 |
| JPH0128820B2 true JPH0128820B2 (en) | 1989-06-06 |
Family
ID=11843537
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP59013807A Granted JPS60159130A (en) | 1984-01-27 | 1984-01-27 | Method for recovering valuable metal from dust, sludge or the like |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS60159130A (en) |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5324001B2 (en) * | 1973-10-02 | 1978-07-18 |
-
1984
- 1984-01-27 JP JP59013807A patent/JPS60159130A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS60159130A (en) | 1985-08-20 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN103114201B (en) | Agglomeration method for iron containing dust slime of iron and steel plants | |
| CN108676942A (en) | The materials such as a kind of iron content and/or zinc lead bronze tin cooperate with processing recovery method with molten steel slag | |
| CN103627835A (en) | Method for treating nickel smelting furnace slag | |
| CN1067439C (en) | Treatment method for high zinc containing iron dust | |
| CN103451451A (en) | Ferro-nickel alloy production technology with laterite nickel ore processed through oxygen enrichment hot air shaft furnace | |
| CN115261540A (en) | Method for recovering iron and tailings in red mud | |
| CN105087864A (en) | Method for directly producing titanium carbide from vanadium titano-magnetite | |
| KR100560236B1 (en) | Method of producing stainless steel by re-using waste material of stainless steel producing process | |
| CN106367554A (en) | Method for extracting iron and valuable metal from secondary resources and producing slag wool | |
| CN111394647A (en) | Vanadium-containing pig iron and method for preparing vanadium-containing pig iron by smelting vanadium-containing steel slag | |
| CN101875986A (en) | A method for treating iron-containing dust in iron and steel plants using a melter-gasifier | |
| US4434001A (en) | Method for manufacturing metal from fine-grain metal-oxide material | |
| JP2001073021A (en) | Flux for refining metal and production thereof | |
| JP2004285473A (en) | Method for recovering valuable metals from waste containing V, Mo and Ni | |
| JPH01228586A (en) | Treatment of ni-cd battery waste | |
| JPS6337173B2 (en) | ||
| JPH0375615B2 (en) | ||
| CN215288923U (en) | Stainless steel dust and sludge system for cooperatively treating ferronickel smelting electric furnace | |
| JPH0128820B2 (en) | ||
| CN120624855B (en) | Method and system for recovering rare earth elements from NdFeB waste and preparing iron-based alloys | |
| JPS6318650B2 (en) | ||
| CN100494423C (en) | Method for recovery of valuable metals from waste containing V, Mo and Ni | |
| CN111850307A (en) | Process method for extracting zinc ash by utilizing metallurgical solid waste pyrogenic process molten flue gas | |
| JPS60159129A (en) | Method for recovering valuable metal from special steel dust, sludge or the like | |
| JP4767611B2 (en) | Reduction method of iron oxide |