JPH033732B2 - - Google Patents
Info
- Publication number
- JPH033732B2 JPH033732B2 JP1830585A JP1830585A JPH033732B2 JP H033732 B2 JPH033732 B2 JP H033732B2 JP 1830585 A JP1830585 A JP 1830585A JP 1830585 A JP1830585 A JP 1830585A JP H033732 B2 JPH033732 B2 JP H033732B2
- Authority
- JP
- Japan
- Prior art keywords
- sludge
- roasting
- dust
- furnace
- special steel
- 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
- 239000000428 dust Substances 0.000 claims description 51
- 239000010802 sludge Substances 0.000 claims description 45
- 238000000034 method Methods 0.000 claims description 29
- 229910052751 metal Inorganic materials 0.000 claims description 20
- 239000002184 metal Substances 0.000 claims description 20
- 150000002739 metals Chemical class 0.000 claims description 19
- 229910000831 Steel Inorganic materials 0.000 claims description 18
- 239000010959 steel Substances 0.000 claims description 18
- 239000004449 solid propellant Substances 0.000 claims description 11
- 239000000463 material Substances 0.000 claims description 10
- 229910052742 iron Inorganic materials 0.000 claims description 9
- 229910052804 chromium Inorganic materials 0.000 claims description 8
- 229910052793 cadmium Inorganic materials 0.000 claims description 6
- 229910052745 lead Inorganic materials 0.000 claims description 6
- 229910052759 nickel Inorganic materials 0.000 claims description 6
- 239000000843 powder Substances 0.000 claims description 6
- 229910052725 zinc Inorganic materials 0.000 claims description 6
- 239000003638 chemical reducing agent Substances 0.000 claims description 5
- 229910000519 Ferrosilicon Inorganic materials 0.000 claims description 3
- 239000000446 fuel Substances 0.000 claims description 3
- 239000000126 substance Substances 0.000 claims description 3
- 239000011230 binding agent Substances 0.000 claims description 2
- 239000003795 chemical substances by application Substances 0.000 claims description 2
- 238000002485 combustion reaction Methods 0.000 claims description 2
- 230000000694 effects Effects 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 238000005192 partition Methods 0.000 description 3
- 230000035699 permeability Effects 0.000 description 2
- 238000011084 recovery Methods 0.000 description 2
- 239000010935 stainless steel Substances 0.000 description 2
- 229910001220 stainless steel Inorganic materials 0.000 description 2
- 239000004484 Briquette Substances 0.000 description 1
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- 229910000599 Cr alloy Inorganic materials 0.000 description 1
- 229910001030 Iron–nickel alloy Inorganic materials 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000003610 charcoal Substances 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 239000000571 coke Substances 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000010891 electric arc Methods 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000002440 industrial waste Substances 0.000 description 1
- 238000004898 kneading Methods 0.000 description 1
- 238000002844 melting Methods 0.000 description 1
- 230000008018 melting Effects 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 239000008188 pellet Substances 0.000 description 1
- 239000003039 volatile agent Substances 0.000 description 1
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
- Manufacture And Refinement Of Metals (AREA)
Description
〔産業上の利用分野〕
本発明は、特殊鋼の製造過程で発生する特殊鋼
ダスト、スラツジ類(以下、ダスト、スラツジ類
という)の処理方法に係り、特に該ダスト、スラ
ツジ類類を簡単な装置にて還元焙焼して冶金炉へ
投入し、有価金属を有効に回収する方法に関する
ものである。
〔従来技術〕
一般に、特殊鋼を製造する際に発生するダス
ト、スラツジ類には、Zn、Pb、Cd等の有害成分
を含む一方、Ni、Cr、Fe等の有価金属が含まれ
ていて、そのまま産業廃棄物として処理すること
が困難であるので、その処理方法が種々検討され
ている。
この一方法として、該ダスト、スラツジ類を塊
成化した後冶金炉に投入して再使用する方法が一
部において採用されている。
また、これらのダスト、スラツジ類を専用のア
ーク式電気炉によつて還元溶解を行い、Fe−Ni
−Cr合金の製造が行う方法も行われている。
〔従来技術の問題点〕
ところが、上記ダスト、スラツジ類を塊成化し
て冶金炉に投入して再使用する方法は、ダスト、
スラツジ類にZn、Pb、Cd等の有害成分を含んで
いるので、有害成分の処理にコスト高の弊害を有
し、更には有価金属の回収率も低いという問題点
があつた。
また、ダスト、スラツジ類を専用のアーク炉に
よつて還元溶解を行うという方法は、特別の装置
と高価な電気エネルギーとを使用するので、コス
ト高になるという問題点があつた。
本発明は、上記事情に鑑みてなされたもので、
簡単な装置を使用し、比較的安価にダスト、スラ
ツジ類から有害成分を除去すると共に、Ni、Fe
を含む有価金属を還元メタル化して冶金炉に再使
用することによつて有価金属の回収率の向上と、
ダスト、スラツジ類の無公害化処理を行う処理方
法を提供することを目的とする。
〔問題点を解決するための手段〕
上記目的に沿う本発明方法は、特殊鋼ダスト、
スラツジ類にこれらを還元焙焼するに必要な炭素
質固体燃料を含む環元剤と必要によりバインダー
とを加えて混練した後に所定の大きさに塊成化す
る第1工程と、第1工程によつて得られた塊成化
物を還元焙焼炉に装入した後、該塊成化物を含ま
れている炭素質燃料に着火して自燃させ、燃焼用
空気を調節することによつて、該塊成化物を赤熱
状態に焙焼し、Zn、Pb、Cd等の有害成分を還元
揮化させると共にNi、Cr、Fe等の有価金属を還
元メタル化させる第2工程と、第2工程で還元焙
焼された上記塊成化物を再酸化しない状態で冶金
炉に投入し、Ni、Cr、Fe等の有価金属を回収す
る第3工程と、第2工程および第3工程で揮化し
た揮発性物質を集塵機で吸引回収する第4工程か
ら構成され、ダスト、スラツジ類に加えた炭素質
固形燃料を自燃させて有害成分を揮化させると共
に、還元性雰囲気にして、ダスト、スラツジ類を
溶融することなく還元焙焼して有価金属をメタル
化し、冶金炉での有価金属の回収を容易ならしめ
ている。
ここに、第1工程において炭素質固体燃料を含
む還元剤とは、炭素質固形燃料単味のみから成る
ものの他、炭素質固形燃料に有価金属の回収を強
化する為に例えばNa2CO3、K2CO3、Ai粉または
フエロシリコン粉の一種以上を含む還元助剤を加
えたものも含むものである。また、上記炭素質固
形燃料には、主としてコークス、石炭等が使用さ
れるが、その使用量は少なくとも上記塊成化物を
赤熱状態に加熱し、含有金属成分を還元するに必
要な理論量以上は必要であつて、通常ダスト、ス
ラツジ類に対し約7〜30重量%である。
ところで、上記還元助剤には、通常、前記した
Na2CO3、K2CO3を使用するが、その添加量は通
常ダスト、スラツジ類に対し1〜10重量%で充分
であり、難還元性の有価金属を回収するときに
は、更にAi粉またはフエロシリコン粉を使用す
ることが好ましい。
また、所定の大きさに塊成化するとは、通常は
ブリケツト化またはペレツト化することをいう
が、その目的とする処は、該処理されたダスト、
スラツジ類を還元焙焼炉に装入した場合に通気性
を確保する為に行うものであるから、例えば、上
記ダスト、スラツジ類に炭素質固形燃料を含む還
元剤と、必要により所定量のバインダーとを加え
て混練し、適当な大きさに造粒あるいは造塊化し
て塊成化することも可能である。
〔実施例〕
続いて、添付した図面を参照しつつ、本発明方
法に係る特殊鋼ダスト、スラツジ類の処理方法の
一実施例について、その処理手順と作用とを詳し
く説明する。
まず、特殊鋼ダスト、スラツジ類にこれらを還
元焙焼するに必要な炭素質固形燃料を有する還元
剤を加えて混練し、図示しない製団機によつて塊
成化する(第1工程)。この塊成化されたダスト、
スラツジ類1を装入ホツパー2に貯留した後、装
入ホツパー2の下部の開口部に付設されたフイダ
ー3で還元焙焼炉(以下、焙焼炉という)4の上
部に設けられている投入ホツパー5から焙焼炉4
に上記塊成化されたダスト、スラツジ類を充填す
る。
この焙焼炉4は、多段式で上段焙焼帯6と下段
焙焼帯7とからなり、焙焼炉4の中段部即ち上段
焙焼帯6の下部には水平方向に開閉できる火格子
8を有し、上段焙焼帯6に装入されたダスト、ス
ラツジ類が下段焙焼帯7に移行できるようになつ
ていると共に、下段焙焼帯7の下部にも開閉でき
る火格子9を有して下段焙焼帯7で処理されたダ
スト、スラツジ類が下部ホツパー10に落下する
ようになつている。また上部焙焼炉体6及び下部
焙焼炉体7の内部には夫々中仕切板11及び12
が設けられて、ダスト、スラツジ類の焙焼が均一
に行われるようになつている。
一方、上記焙焼炉4の炉頂部13には、図示し
ない集塵装置に接続されて、その途中に風量調節
弁14が設けられているダクト15が接続されて
いる。
この焙焼炉4に、上記工程を経て塊成化処理を
したダスト、スラツジ類を装入して、下部の該ダ
スト、スラツジ類に着火した後に、図示しない集
塵装置を駆動すると共に、焙焼炉4の内部が還元
性雰囲気を保持しえるように、前記風量調節弁1
4を調節する。
この後、焙焼が上部に進行して下段焙焼帯7全
体が高温火層になつて、中段の火格子8を通して
上段焙焼帯6の中頃まで火層が上昇した時点で、
炉底部の火格子9を開いて焙焼されたダスト、ス
ラツジ類を下部ホツパー10に落下させると共に
下部の切換ダンパー16を操作して密閉コンテナ
17中に入れた後、密閉コンテナ17の上部密閉
蓋18を閉じて投入したダスト、スラツジ類を冷
却する。このように、焙焼処理されたダスト、ス
ラツジ類である焙焼鉱を一度に纒めて密閉コンテ
ナ17に投入するので、再酸化を受け難く、次工
程の冶金炉への赤熱高温装入も容易に行えるもの
である。
次いで、炉底部の火格子9を閉じた後に、中段
の火格子8を開いて、上段焙焼帯6の塊成化され
たダスト、スラツジ類を下段焙焼帯7に移し、こ
の後上記火格子8を閉じて新たな塊成化されたダ
スト、スラツジ類を上段焙焼帯6に投入して焙焼
を続ける。
以上の操作を繰り返すことによつて、上記焙焼
炉4で連続的に塊成化されたダスト、スラツジ類
の焙焼を行うものである。
ここで、焙焼層厚が厚すぎると焙焼速度が遅
く、しかもクリンカーを造る虞があり、連続操作
を阻害するので、一段の焙焼層厚を1000mm以下と
し、焙焼速度を助長させる為、上段焙焼帯6の底
部に設けられている火格子8から上段焙焼帯6内
に適当に空気が入るようにすることが好ましい。
また、中仕切板11,12は塊成物層の通気性を
均一にし、焙焼炉4内の焙焼が均一に行われるよ
うにする為のものであるが、焙焼炉径が500mm以
下の小型炉では特に必要としない。
以上の工程によつて、第1工程によつて得られ
た塊成化物を還元焙焼炉に装入した後、該塊成化
物に含まれている炭素質燃料に着火して自燃さ
せ、燃焼用空気を調節することによつて、該塊成
化物を赤熱状態に焙焼し、Zn、Pb、Cd等の有害
成分を還元揮化させると共にNi、Cr、Fe等の有
価金属を還元メタル化させる(第2工程)と共
に、再酸化しない状態にしておく。
次に、上記工程によつて還元メタル化したNi、
Cr、Fe等の有価金属を冶金炉に投入して、Ni、
Cr、Fe等の有価金属を回収する(第3工程)。
また、上記工程によつて揮化したZn、Pb、Cd
等の揮発性物質は炉頂部に設けられているダクト
15等によつて集塵装置に吸引されて回収される
(第4工程)。
なお、上記方法においては、焙焼炉に二段式の
ものを使用しているいるが、本発明はこれに限定
されるものではなく、一段式あるいは三段式以上
の炉体から成る焙焼炉でも本発明方法を適用する
ことが可能である。
〔実施例〕
続いて、本発明の作用効果を確認する為に行つ
た実験をその実施例と共に説明する。
炉頂部が集塵装置に連結し、炉体の断面が1300
mm×1300mmで高さが1400mmの角型シヤフト炉に、
炉底部と中段部に火格子を設けて、両火格子の間
隔を700mmとした焙焼炉を造り、特殊鋼ダストの
一例であるステンレス鋼電気炉ダスト100重量部
に対し、コークス粉15重量部と、Na2CO3を3重
量部とを混練して、50mm×40mm×30mmの豆炭状に
塊成化したブリケツトを充填した後、ガスバーナ
ーを用いて炉底部のブリケツトに着火し、炉断面
積1m2当たり約10m3/分の弱風量で吸引しながら
焙焼を行つた。
この後、下段のブリケツト全体が火層になり、
上段のブリケツトの約2/3まで火層が上昇した処
で下段の焙焼処理ブリケツトである焙焼鉱を排出
し、次いで上段のブリケツトを下段に移し、上段
に新たなブリケツトを充填して焙焼を続けて、前
記ステンレス鋼電気炉ダストの還元焙焼を行つ
た。
次に、上記方法によつて得られた焙焼鉱と焙焼
前のブリケツトを各々100Kgづつ1tエール式電気
炉で溶解処理して、還元焙焼効果を明らかにした
結果を第1表に示す。
[Industrial Field of Application] The present invention relates to a method for treating special steel dust and sludge (hereinafter referred to as dust and sludge) generated during the manufacturing process of special steel, and particularly to a method for treating special steel dust and sludge (hereinafter referred to as dust and sludge). The present invention relates to a method for effectively recovering valuable metals by reducing and roasting them in an apparatus and feeding them into a metallurgical furnace. [Prior art] Generally, dust and sludge generated during the production of special steel contain harmful components such as Zn, Pb, and Cd, while also containing valuable metals such as Ni, Cr, and Fe. Since it is difficult to treat it directly as industrial waste, various treatment methods are being studied. As one method for this, a method has been adopted in some cases in which the dust and sludge are agglomerated and then fed into a metallurgical furnace for reuse. In addition, these dusts and sludge are reduced and melted in a special electric arc furnace to produce Fe-Ni.
- A method for producing Cr alloys is also used. [Problems with the prior art] However, the method of agglomerating the dust and sludge and putting it into a metallurgical furnace for reuse is difficult.
Since the sludge contains harmful components such as Zn, Pb, and Cd, there is a problem in that the treatment of the harmful components is costly, and the recovery rate of valuable metals is also low. Further, the method of reducing and melting dust and sludge using a special arc furnace has the problem of high costs because special equipment and expensive electrical energy are used. The present invention was made in view of the above circumstances, and
Uses simple equipment to remove harmful components from dust and sludge at a relatively low cost, and also removes Ni and Fe.
Improve the recovery rate of valuable metals by converting them into reduced metals and reusing them in metallurgical furnaces.
The purpose of the present invention is to provide a treatment method for making dust and sludge pollution-free. [Means for solving the problems] The method of the present invention that meets the above objectives uses special steel dust,
A first step in which a ring-forming agent containing a carbonaceous solid fuel necessary for reducing and roasting the sludge and a binder if necessary is added, kneaded, and then agglomerated into a predetermined size; After charging the agglomerated material thus obtained into a reduction roasting furnace, the carbonaceous fuel containing the agglomerated material is ignited to self-combust, and the combustion air is adjusted. The second step involves roasting the agglomerated material to a red-hot state, reducing and volatilizing harmful components such as Zn, Pb, and Cd, and reducing and converting valuable metals such as Ni, Cr, and Fe into metals. A third step in which the roasted agglomerates are charged into a metallurgical furnace without being reoxidized to recover valuable metals such as Ni, Cr, and Fe, and the volatiles volatilized in the second and third steps. The fourth step consists of collecting the substances by suction with a dust collector, and the carbonaceous solid fuel added to the dust and sludge is self-combusted to volatilize harmful components, and at the same time, the dust and sludge are melted in a reducing atmosphere. This method converts valuable metals into metals by reducing and roasting them without any heat loss, making it easy to recover valuable metals in metallurgical furnaces. Here, the reducing agent containing carbonaceous solid fuel in the first step is not only one consisting only of carbonaceous solid fuel, but also a reducing agent containing carbonaceous solid fuel such as Na 2 CO 3 , It also includes a reduction aid containing one or more of K 2 CO 3 , Ai powder, or ferrosilicon powder. In addition, coke, coal, etc. are mainly used as the carbonaceous solid fuel, and the amount used is at least the theoretical amount required to heat the agglomerate to a red-hot state and reduce the metal components contained therein. It is usually about 7 to 30% by weight based on dust and sludge. By the way, the above-mentioned reducing aid usually includes the above-mentioned
Na 2 CO 3 and K 2 CO 3 are used, but the amount added is normally 1 to 10% by weight based on dust and sludge, and when recovering valuable metals that are difficult to reduce, Ai powder or Preferably, ferrosilicon powder is used. Furthermore, agglomerating into a predetermined size usually means turning into briquettes or pellets, but the purpose of this is to form the treated dust into
This is done to ensure air permeability when the sludge is charged into a reduction roasting furnace. It is also possible to agglomerate by adding and kneading and granulating or agglomerating into an appropriate size. [Example] Next, with reference to the attached drawings, the processing procedure and operation of an example of the method for treating special steel dust and sludge according to the method of the present invention will be described in detail. First, a reducing agent containing a carbonaceous solid fuel necessary for reducing and roasting the special steel dust and sludge is added and kneaded, and the mixture is agglomerated using a compacting machine (not shown) (first step). This agglomerated dust,
After storing sludge 1 in a charging hopper 2, a feeder 3 attached to an opening at the bottom of the charging hopper 2 is used to charge the sludge 1 installed at the top of a reduction roasting furnace (hereinafter referred to as a roasting furnace) 4. From hopper 5 to roasting furnace 4
is filled with the agglomerated dust and sludge. This roasting furnace 4 is a multi-stage type and consists of an upper roasting zone 6 and a lower roasting zone 7. In the middle part of the roasting furnace 4, that is, at the bottom of the upper roasting zone 6, there is a grate 8 that can be opened and closed horizontally. It is designed so that the dust and sludge charged in the upper roasting zone 6 can be transferred to the lower roasting zone 7, and also has a grate 9 that can be opened and closed at the bottom of the lower roasting zone 7. The dust and sludge processed in the lower roasting zone 7 fall into the lower hopper 10. In addition, inside the upper roasting furnace body 6 and the lower roasting furnace body 7, partition plates 11 and 12 are provided, respectively.
is provided to ensure uniform roasting of dust and sludge. On the other hand, a duct 15 is connected to the top part 13 of the roasting furnace 4, and is connected to a dust collector (not shown), and has an air volume control valve 14 in the middle thereof. After charging the dust and sludge that have been agglomerated through the above steps into the roasting furnace 4 and igniting the dust and sludge in the lower part, a dust collector (not shown) is driven and the roasting furnace 4 is heated. In order to maintain a reducing atmosphere inside the kiln 4, the air volume control valve 1 is
Adjust 4. After this, the roasting progresses upwards, and the entire lower roasting zone 7 becomes a high-temperature fire layer, and when the fire layer rises to the middle of the upper roasting zone 6 through the middle fire grate 8,
After opening the grate 9 at the bottom of the furnace and allowing the roasted dust and sludge to fall into the lower hopper 10 and placing them into the sealed container 17 by operating the lower switching damper 16, the upper sealed lid of the sealed container 17 is opened. 18 is closed to cool the introduced dust and sludge. In this way, since the roasted ore, which is the roasted dust and sludge, is collected at once and charged into the sealed container 17, it is less susceptible to re-oxidation and can be charged at high temperature to the metallurgical furnace in the next process. It is easy to do. Next, after closing the grate 9 at the bottom of the furnace, the middle grate 8 is opened to transfer the agglomerated dust and sludge from the upper roasting zone 6 to the lower roasting zone 7, and then the fire The grate 8 is closed and new agglomerated dust and sludge are introduced into the upper roasting zone 6 to continue roasting. By repeating the above operations, the agglomerated dust and sludge are continuously roasted in the roasting furnace 4. Here, if the thickness of the roasting layer is too thick, the roasting speed will be slow and there is a risk of clinker formation, which will hinder continuous operation, so the thickness of the roasting layer of one stage should be 1000 mm or less to accelerate the roasting speed. It is preferable that air be appropriately introduced into the upper roasting zone 6 through the grate 8 provided at the bottom of the upper roasting zone 6.
In addition, the partition plates 11 and 12 are used to make the agglomerate layer uniform in air permeability and to ensure uniform roasting in the roasting furnace 4, but the diameter of the roasting furnace is 500 mm or less. This is not particularly necessary for small-sized reactors. Through the above steps, after charging the agglomerated material obtained in the first step into a reduction roasting furnace, the carbonaceous fuel contained in the agglomerated material is ignited and combusts by itself. By adjusting the air, the agglomerated material is roasted to a red-hot state, and harmful components such as Zn, Pb, and Cd are reduced and volatilized, and valuable metals such as Ni, Cr, and Fe are reduced and converted into metals. (second step) and keep it in a state where it will not be re-oxidized. Next, Ni reduced and metalized by the above process,
Valuable metals such as Cr and Fe are put into a metallurgical furnace to produce Ni,
Collect valuable metals such as Cr and Fe (third step). In addition, Zn, Pb, and Cd volatilized by the above process
The volatile substances are sucked into the dust collector and collected by the duct 15 provided at the top of the furnace (fourth step). In the above method, a two-stage roasting furnace is used, but the present invention is not limited to this. It is also possible to apply the method of the invention in a furnace. [Example] Next, experiments conducted to confirm the effects of the present invention will be described together with examples thereof. The top of the furnace is connected to the dust collector, and the cross section of the furnace body is 1300mm.
Square shaft furnace with mm x 1300mm and height 1400mm.
A roasting furnace was constructed with a grate installed at the bottom and middle of the furnace, with a spacing of 700 mm between the two grate, and 15 parts by weight of coke powder was added to 100 parts by weight of stainless steel electric furnace dust, which is an example of special steel dust. and 3 parts by weight of Na 2 CO 3 and filled with briquettes that were agglomerated into 50 mm x 40 mm x 30 mm charcoal shapes, the briquettes at the bottom of the furnace were ignited using a gas burner, and the furnace was slit. Roasting was performed while suctioning at a weak air flow rate of about 10 m 3 /min per 1 m 2 of area. After this, the entire lower briquette becomes a fire layer,
When the fire layer has risen to about 2/3 of the briquettes in the upper tier, the roasted ore from the briquettes in the lower tier is discharged, then the briquettes in the upper tier are moved to the lower tier, and the briquettes in the upper tier are filled with new briquettes and roasted. The roasting was continued to perform reduction roasting of the stainless steel electric furnace dust. Next, 100 kg each of the roasted ore obtained by the above method and the briquettes before roasting were melted in a 1 ton Yale electric furnace to clarify the reduction roasting effect. The results are shown in Table 1. .
【表】【table】
本発明方法は以上のように構成されていて、特
殊鋼ダスト、スラツジ類を処分するに当たり、所
定量の炭素質固形燃料を加えて焙焼処理した後に
冶金炉への再使用を行うので、有効に特殊鋼ダス
ト、スラツジ類の無公害化処処理ができると共
に、特殊鋼ダスト、スラツジ類中の有害成分の除
去と有価金属の有効回収が容易に出来ることとな
つた。
また、本発明方法はその焙焼方法が電力を特に
必要としない簡易な方法によつて行なわれている
ので、特殊鋼ダスト、スラツジ類の処理が安価に
できることとなつた。
The method of the present invention is configured as described above, and when disposing of special steel dust and sludge, a predetermined amount of carbonaceous solid fuel is added and roasted before being reused in a metallurgical furnace, making it effective. In addition to making it possible to treat special steel dust and sludge to make them non-polluting, it has also become possible to easily remove harmful components and effectively recover valuable metals from special steel dust and sludge. Furthermore, since the roasting method of the present invention is carried out by a simple method that does not particularly require electric power, special steel dust and sludge can be treated at low cost.
第1図は本発明方法の一実施例を説明する為の
概略説明図である。
〔符号の説明〕1……ダスト、スラツジ類、2…
…装入ホツパー、3……フイダー、4……焙焼
炉、6……上段焙焼帯、7……下段焙焼帯、8,
9……火格子、11,12……中仕切板、15…
…ダクト、17……密閉コンテナ。
FIG. 1 is a schematic explanatory diagram for explaining one embodiment of the method of the present invention. [Explanation of symbols] 1...Dust, sludge, 2...
...Charging hopper, 3... Feeder, 4... Roasting furnace, 6... Upper roasting zone, 7... Lower roasting zone, 8,
9... Grate, 11, 12... Partition plate, 15...
...Duct, 17... Sealed container.
Claims (1)
ジ類の処理方法。 第1工程:特殊鋼ダスト、スラツジ類にこれら
を還元焙焼するに必要な炭素質固体燃料を含む環
元剤と必要によりバインダーとを加えて混練した
後に所定の大きさに塊成化する。 第2工程:第1工程によつて得られた塊成化物
を還元焙焼炉に装入した後、該塊成化物に含まれ
ている炭素質燃料に着火して自燃させ、燃焼用空
気を調節することによつて、該塊成化物を赤熱状
態に焙焼し、Zn、Pb、Cd等の有害成分を還元揮
化させると共にNi、Cr、Fe等の有価金属を還元
メタル化させる。 第3工程:第2工程で還元焙焼された上記塊成
化物を再酸化しない状態で冶金炉に投入し、Ni、
Cr、Fe等の有価金属を回収する。 第4工程:第2工程および第3工程で揮化した
揮発性物質を集塵機で吸引回収する。 2 第1工程で用いる還元剤が炭素質固体燃料単
味から成る特許請求の範囲第1項記載の特殊鋼ダ
スト、スラツジ類の処理方法。 3 第1工程で用いる還元剤が炭素質固体燃料と
還元助剤とからなる特許請求の範囲第1項記載の
特殊鋼ダスト、スラツジ類の処理方法。 4 還元助剤が、Na2CO3、K2CO3、AI粉または
フエロシリコン粉の少なくとも一種以上を含むも
のから成る特許請求の範囲第3項記載の特殊鋼ダ
スト、スラツジ類の処理方法。 5 第2工程で使用する還元焙焼炉が複数の焙焼
帯から構成される多段式焙焼炉である特許請求の
範囲第1項、第2項、第3項、第4項または第5
項に記載の特殊鋼ダスト、スラツジ類の処理方
法。[Claims] 1. A method for treating special steel dust and sludge comprising the following steps. First step: Special steel dust and sludge are mixed with a ring agent containing a carbonaceous solid fuel necessary for reducing and roasting them, and a binder if necessary, and then agglomerated into a predetermined size. 2nd step: After charging the agglomerated material obtained in the 1st step into a reduction roasting furnace, the carbonaceous fuel contained in the agglomerated material is ignited to self-combust, and combustion air is released. By adjusting the temperature, the agglomerated material is roasted to a red-hot state, and harmful components such as Zn, Pb, and Cd are reduced and volatilized, and valuable metals such as Ni, Cr, and Fe are reduced and metalized. Third step: The agglomerated material that has been reduced and roasted in the second step is put into a metallurgical furnace without being reoxidized, and Ni,
Collect valuable metals such as Cr and Fe. Fourth step: The volatile substances volatilized in the second and third steps are collected by suction using a dust collector. 2. The method for treating special steel dust and sludge according to claim 1, wherein the reducing agent used in the first step is a carbonaceous solid fuel. 3. The method for treating special steel dust and sludge according to claim 1, wherein the reducing agent used in the first step comprises a carbonaceous solid fuel and a reducing aid. 4. The method for treating special steel dust and sludge as set forth in claim 3, wherein the reducing aid contains at least one of Na 2 CO 3 , K 2 CO 3 , AI powder, or ferrosilicon powder. . 5 Claims 1, 2, 3, 4, or 5, wherein the reduction roasting furnace used in the second step is a multistage roasting furnace composed of a plurality of roasting zones.
Method for treating special steel dust and sludge as described in Section 1.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP60018305A JPS61177337A (en) | 1985-01-31 | 1985-01-31 | Treatment of special steel dust sludge |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP60018305A JPS61177337A (en) | 1985-01-31 | 1985-01-31 | Treatment of special steel dust sludge |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS61177337A JPS61177337A (en) | 1986-08-09 |
| JPH033732B2 true JPH033732B2 (en) | 1991-01-21 |
Family
ID=11967898
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP60018305A Granted JPS61177337A (en) | 1985-01-31 | 1985-01-31 | Treatment of special steel dust sludge |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS61177337A (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR20030048809A (en) * | 2001-12-13 | 2003-06-25 | 주식회사 포스코 | Method for Treating Iron Contained Waste Dust Generated from The Steel Works with Corex Process |
| FR2835000B1 (en) * | 2002-01-21 | 2004-11-05 | Delachaux Sa | PROCESS FOR THE MANUFACTURE OF METAL ELEMENTS USING A CRUCIBLE |
| JP2009209411A (en) * | 2008-03-04 | 2009-09-17 | Nippon Yakin Kogyo Co Ltd | Method for reducing valuable metal raw material |
-
1985
- 1985-01-31 JP JP60018305A patent/JPS61177337A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS61177337A (en) | 1986-08-09 |
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