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JPH0128821B2 - - Google Patents
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JPH0128821B2 - - Google Patents

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Publication number
JPH0128821B2
JPH0128821B2 JP59036823A JP3682384A JPH0128821B2 JP H0128821 B2 JPH0128821 B2 JP H0128821B2 JP 59036823 A JP59036823 A JP 59036823A JP 3682384 A JP3682384 A JP 3682384A JP H0128821 B2 JPH0128821 B2 JP H0128821B2
Authority
JP
Japan
Prior art keywords
slag
dust
sludge
fuel
roasting
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
Application number
JP59036823A
Other languages
Japanese (ja)
Other versions
JPS60181247A (en
Inventor
Takashi Oshiumi
Kazuaki Tanigawa
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 Jiryoku Senko Co Ltd
Original Assignee
Nippon Jiryoku Senko Co Ltd
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 Jiryoku Senko Co Ltd filed Critical Nippon Jiryoku Senko Co Ltd
Priority to JP59036823A priority Critical patent/JPS60181247A/en
Publication of JPS60181247A publication Critical patent/JPS60181247A/en
Publication of JPH0128821B2 publication Critical patent/JPH0128821B2/ja
Granted legal-status Critical Current

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Manufacture And Refinement Of Metals (AREA)

Description

【発明の詳細な説明】[Detailed description of the invention]

一般に製鋼工場より発生するダスト、スラツジ
類は、酸化鉄を主成分とするが、他にZn,Pb,
Cd,Ni,Cr,Cu等の有害金属化合物を含み、し
かもP,S,Cl等も含む微粉であるために、鉄資
源としての利用が出来ず、一方産業廃棄物として
の処分にも困難性を有し、その処分に多額の費用
を要しているのが実態である。 一方製鋼工場から発生する溶滓は、莫大なる顕
熱エネルギーを持つたまま無駄に放冷されている
のが現状である。 本発明はこれらに注目して溶滓の顕熱を反応エ
ネルギーとして利用し、製鋼ダスト、スラツジ類
を溶滓中に完全に滓化させ、有害成分の溶出を防
ぎ、無公害化処理を完全ならしめることを目的と
したものである。 この種の研究としては本件出願人が既に出願し
た、特願昭48−111306号(特開昭50−61304号)、
特願昭50−53680号(特開昭51−129802)、特願昭
50−69268号(特開昭51−145528号)等があるが、
これらの方法はすべて還元剤を内装したダスト、
スラツジのブリケツトまたはペレツトを作り、溶
滓と直接反応させて処理する方法であるために、
溶滓の温度が急速に低下して、不完全な反応とな
り、処理後のスラグに未溶解ダスト、スラツジ類
が残ることが、時々見られる欠点を有しているこ
とが確認出来た。 本発明方法は上記の欠点を解消し、更にダス
ト、スラツジ類の処理量増大と有害成分の無公害
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、ダス
ト、スラツジ類を高温の溶滓に投入滓化せしめる
に先立つて、予備焙焼を行い、揮発性成分の大部
分を除去して、集塵機で捕捉回収し、一方焙焼物
は高温のまま溶滓中に投入する方法であつて、
Zn,Pb,Cd,Cl等の揮発性成分は、予備焙焼と
溶滓反応との二段工程での完全除去となり、更に
高温状態での溶滓反応によつて、ダスト、スラツ
ジ類の滓化反応を完全ならしめるところに特徴が
ある。 なお第1工程で用いる燃料としては、通常はコ
ークス粉、石炭粉等を用い、助剤は使用しないが
特にZn,Pb等含有量の多い場合にはCaCl2等を
用い、またNi,Cr,Mo,W,V等を含み溶滓反
応後にメタルとして回収する場合には、還元力を
有する燃料として、アルミニユーム粉、フエロシ
リコン粉等を用い、助剤として鉄粉等を使用す
る。 なお、その使用量は、ダスト、スラツジ類の種
類によつて異なるが、少くとも水分、揮発性物質
の揮化等の反応に必要な理論量は必要である。 また第2工程では、通常焼結機方式の焙焼炉に
充填したダスト、スラツジ混合物に、溶滓の副射
熱又は補助バーナーによつて着火し、充填層内を
強制通気することによつて全体を焙焼せしめ、揮
化物質の除去を行うと共に、焙焼物の昇温を行う
が、ロータリーキルン等による焙焼方式でもその
焙焼効果が良好であれば、何んら焙焼方法に制限
を加えるものではない。 第3工程では高温の焙焼物を溶滓中に投入する
に際し、溶滓を気体によるバブリング等によつて
撹拌しながら投入することが、均一に溶解滓化さ
せ得る方法として好ましい。 次に図面に示す説明図を参照しながら本願方法
を詳述する。 図中は製鋼ダスト、スラツジ類、は燃料及
び助剤、は混合機、は混合物ホツパー、は
混合物、は混合物フイダー、は移動式焙焼
炉、は焙焼炉充填層、は吸気用フード、は
吸気制御用バルブ、は点火バーナー、は集塵
用ダンパー、は吸気用ダクト、は集塵ダク
ト、は集塵機、は集塵機ブロアー、は集塵
フード、は焙焼物、は溶滓、は溶滓鍋、
は気体ランス、は溶滓発生炉を示す。 溶滓発生炉からの溶滓を受けた溶滓鍋を
移動式焙焼炉の真下にセツトして、一方製鋼ダ
スト、スラツジ類は、コークス粉等の燃料と
混合機によつて混合され、混合物となつてホ
ツパーに入り、次いでフイダーによつて移動
式焙焼炉に充填され、吸気用フードを通じて
集塵機ブロアーで吸気すると共に、点火バーナ
ーによつて充填層の下部に着火せしめ、吸気
制御用バルブで吸気風量を調節して高温に焙焼
される。 この間、焙焼によつて揮化する物質は集塵機
によつて効率良く回収され、移動式焙焼炉で焙
焼の完了した充填層は反転して、焙焼物を溶
滓中に高温のまま落下投入する。また溶滓
を、気体ランスによつてバブリング撹拌し、投
入された焙焼物の完全均一な溶解を促進する。 斯くして、溶滓中に完全に滓化されたダスト、
スラツジ成分は、溶滓中の構成物質となつて安定
化し、溶出することなく無公害化される。また溶
滓へ焙焼物を投入する時に発生する揮化物は、集
塵フードと、ダンパーの操作によつて、完全
に集塵機に回収され、環境汚染の心配はない。 以下実施例を述べる。 実施例 集塵用バツクフイルターに連通した、直径600
mm、深さ400mmの鉄製の竪型焙焼炉に、あらかじ
め普通鋼電気炉ダスト90%(重量%の事である。
以下全文を通じ同じ)とコークス粉10%とを混練
した混合物100Kgを軽く充填して、上部より吸気
しながら、下部からガスバーナーで着火し、約10
m3/分間の風量で吸引焙焼を行つて、充分に上部
まで焙焼された後に、1t電気炉で溶製してスラグ
鍋に受滓した約550Kgの溶滓(1550℃)に、空気
バブリング撹拌をしながら転倒して、赤熱の状態
で投入し、溶融滓化せしめた。 次に溶滓が冷却凝固後に約25mm以下に破砕して
磁力選鉱を行い、含有メタルを回収すると共に非
磁性スラグの特性を測定し、また集塵機で回収さ
れた揮化物の分析を行つた結果は下記のごとくで
あつた。
Generally, dust and sludge generated from steel mills have iron oxide as the main component, but they also contain Zn, Pb,
Because it is a fine powder that contains harmful metal compounds such as Cd, Ni, Cr, and Cu, and also contains P, S, and Cl, it cannot be used as an iron resource, and on the other hand, it is difficult to dispose of it as industrial waste. The reality is that it costs a lot of money to dispose of it. On the other hand, the current situation is that the molten slag generated from steel factories is left to cool unnecessarily, with a huge amount of sensible heat energy. The present invention focuses on these points and utilizes the sensible heat of the slag as reaction energy, completely converts steelmaking dust and sludge into the slag, prevents the elution of harmful components, and completely eliminates pollution. It is intended for the purpose of tightening. Examples of this type of research include Japanese Patent Application No. 111306/1983 (Japanese Patent Application No. 61304/1983), which the applicant has already filed;
Japanese Patent Application No. 50-53680 (Japanese Unexamined Patent Publication No. 51-129802)
No. 50-69268 (Japanese Unexamined Patent Publication No. 51-145528), etc.
All of these methods use dust containing a reducing agent,
This process involves making sludge briquettes or pellets and reacting them directly with the slag.
It was confirmed that the temperature of the slag rapidly decreases, resulting in an incomplete reaction, and that undissolved dust and sludge remain in the slag after treatment, which is a drawback that is sometimes seen. The method of the present invention eliminates the above-mentioned drawbacks, and also provides a method for increasing the throughput of dust and sludge and making the pollution-free treatment of harmful components more complete. , dust, and sludge are put into the hot molten slag and pre-roasted to remove most of the volatile components and collected using a dust collector. A method of putting it into slag,
Volatile components such as Zn, Pb, Cd, and Cl are completely removed in a two-step process of pre-roasting and slag reaction, and dust and sludge are further removed by slag reaction at high temperatures. Its distinctive feature is that it completes the chemical reaction. The fuel used in the first step is usually coke powder, coal powder, etc., and no auxiliary agent is used, but when the content of Zn, Pb, etc. is particularly high, CaCl 2 etc. is used, and Ni, Cr, etc. When the metal contains Mo, W, V, etc. and is recovered as a metal after the slag reaction, aluminum powder, ferrosilicon powder, etc. are used as the fuel having reducing power, and iron powder etc. are used as the auxiliary agent. The amount used varies depending on the type of dust and sludge, but at least the theoretical amount required for reactions such as volatilization of moisture and volatile substances is required. In the second step, the dust and sludge mixture filled in a roasting furnace using a normal sintering machine is ignited by the side radiation heat of the slag or by an auxiliary burner, and the inside of the packed bed is forcedly ventilated. The entire body is roasted to remove volatile substances and the temperature of the roasted product is raised, but there are no restrictions on the roasting method as long as the roasting effect is good, even if it is roasted using a rotary kiln or the like. It's not something to add. In the third step, when the high-temperature roasted product is introduced into the slag, it is preferable to add the slag while stirring it by bubbling with gas or the like, as this method can uniformly transform it into slag. Next, the method of the present invention will be described in detail with reference to explanatory diagrams shown in the drawings. In the figure, steel dust, sludge, fuel and auxiliary agents, mixer, mixture hopper, mixture, mixture feeder, mobile roasting furnace, roasting furnace packed bed, intake hood, Intake control valve, ignition burner, dust collection damper, intake duct, dust collection duct, dust collector, dust collector blower, dust collection hood, roasted products, slag, slag pot,
indicates a gas lance, and indicates a slag generation furnace. A slag pot that receives the slag from the slag generation furnace is set directly below the mobile roasting furnace, while the steelmaking dust and sludge are mixed with fuel such as coke powder by a mixer, and the mixture is The mixture enters the hopper, is then filled into a mobile roasting furnace by a feeder, is sucked in by a dust collector blower through an intake hood, is ignited at the bottom of the packed bed by an ignition burner, and is controlled by an intake control valve. The intake air volume is adjusted to roast at a high temperature. During this time, the substances volatilized by roasting are efficiently collected by the dust collector, and the packed bed that has been roasted in the mobile roasting furnace is turned over and the roasted material falls into the slag at a high temperature. throw into. In addition, the slag is bubbled and stirred by a gas lance to promote completely uniform dissolution of the roasted material. In this way, the dust completely slaged in the slag,
The sludge component becomes a constituent substance in the slag, stabilizes it, and becomes non-polluting without being eluted. In addition, the volatile substances generated when the roasted material is put into the slag are completely collected in the dust collector by operating the dust collection hood and damper, so there is no concern about environmental pollution. Examples will be described below. Example: Diameter 600mm connected to dust collection back filter
90% (by weight) of ordinary steel electric furnace dust was placed in a vertical iron roasting furnace with a diameter of 400 mm and a depth of 400 mm.
Lightly fill the mixture with 100kg of kneaded coke powder (same throughout the text) and 10% coke powder, and ignite it with a gas burner from the bottom while drawing air from the top.
Suction roasting is performed at an air flow rate of m 3 /min, and after the upper part has been thoroughly roasted, air is poured into approximately 550 kg of slag (1550°C), which was melted in a 1 ton electric furnace and received in a slag pot. While stirring by bubbling, the mixture was turned over and poured in a red-hot state to form a molten slag. Next, after the slag cooled and solidified, it was crushed into pieces of approximately 25 mm or less, subjected to magnetic beneficiation, the metals contained were recovered, the characteristics of the non-magnetic slag were measured, and the volatile matter recovered by the dust collector was analyzed. It was as follows.

【表】 第1表は、処理ダストと、処理後の産物との化
学分析値を示したもので、揮化回収物にZn,Pb,
Clが濃縮されることを示している。 以上の結果より、ダスト中Zn,Pb,Clの揮化
率を計算すると、 焙焼工程Zn揮化率 〔1−78Kg×0.1011/100Kg×0.1504〕×100=47.6(
%) 焙焼工程Pb揮化率 〔1−78Kg×0.0052/100Kg×0.0107〕×100=62.1(
%) 焙焼工程Cl揮化率 〔1−78Kg×0.0309/100Kg×0.0889〕×100=72.9(
%) さらに溶滓との反応時の揮化を含めた、 総合Zn揮化率 〔1−608Kg×0.0039+16Kg×0.0045/100Kg×0.1504
〕×100 =83.7(%) 総合Pb揮化率 〔1−608Kg×0.0001/100Kg×0.0107〕×100=94.3
(%) 総合Cl揮化率 〔1−608Kg×0.000/100Kg×0.0889〕×100=100.0
(%) となる。 また第2表は、処理後の非磁性スラグを環境庁
告示による方法で、溶出イオンを測定した結果を
示したもので、
[Table] Table 1 shows the chemical analysis values of treated dust and products after treatment.
This shows that Cl is concentrated. Based on the above results, the volatilization rate of Zn, Pb, and Cl in the dust is calculated as follows.
%) Roasting process Pb volatilization rate [1-78Kg×0.0052/100Kg×0.0107]×100=62.1(
%) Roasting process Cl volatilization rate [1-78Kg×0.0309/100Kg×0.0889]×100=72.9(
%) Total Zn volatilization rate including volatilization during reaction with slag [1-608Kg×0.0039+16Kg×0.0045/100Kg×0.1504
] × 100 = 83.7 (%) Total Pb volatilization rate [1-608Kg × 0.0001/100Kg × 0.0107] × 100 = 94.3
(%) Total Cl volatilization rate [1-608Kg×0.000/100Kg×0.0889]×100=100.0
(%). In addition, Table 2 shows the results of measuring the eluted ions of the non-magnetic slag after treatment using the method notified by the Environment Agency.

【表】 有害成分の溶出は全く無く、処理後スラグを道
路用バラス等の土木資材として使用しても、何ん
ら問題のないことを明らかとした。 以上説明した如く、本願方法によれば製鋼ダス
ト、スラツジ類は、先ず予備焙焼によつて、大部
分の揮化成分を除去した後に、赤熱高温の状態で
溶滓との直接反応が行われるために、反応が確実
であり、処理に失敗がなく、溶滓当りのダスト類
処理能力が大きく、溶滓量の比較的に少ない製鋼
工場に於いても自社発生のダスト類を自社発生の
溶滓で無公害化処理出来る利点を有するものであ
る。
[Table] There was no elution of harmful components at all, and it was revealed that there would be no problem in using the treated slag as civil engineering materials such as road ballasts. As explained above, according to the method of the present invention, steelmaking dust and sludge are first subjected to preliminary roasting to remove most of the volatile components, and then directly reacted with the molten slag at a red-hot high temperature. Therefore, the reaction is reliable, there is no failure in the treatment, and the dust processing capacity per molten slag is large. Even in steelmaking plants with a relatively small amount of slag, the dust generated in-house can be used to process the dust generated in-house. This has the advantage that the slag can be treated to make it non-polluting.

【図面の簡単な説明】[Brief explanation of drawings]

図面は本願発明方法の概要説明図。 The drawing is a schematic explanatory diagram of the method of the present invention.

Claims (1)

【特許請求の範囲】 1 下記の各工程より成る製鋼ダスト、スラツジ
類の処理方法。 第1工程:製鋼ダスト、スラツジ類と、該ダス
ト、スラツジ類を焙焼するに必要な量の燃料単
味、又は燃料と助剤とを混合する。 第2工程:第1工程で得られた混合物を、焙焼炉
に装入した後燃料に着火し、混合燃料等の燃焼
熱によつて焙焼し、水分を除去すると共に、該
ダスト、スラツジ類に含まれる揮発性物質を揮
化させる。 第3工程:第2工程で得られた焙焼ダスト、スラ
ツジ類を、高温の溶滓中に投入して溶解し、滓
化させると共に、残留揮発性物質を完全に揮化
させる。 第4工程:第3工程で得られた溶滓を冷却凝固
し、次いで破砕した後通常の選鉱手段で、含有
している粒鉄等を回収する。 第5工程:第2工程及び第3工程で揮化した揮発
性物質は、集塵装置により吸引回収する。 2 第1工程で用いる燃料が、炭素質燃料、アル
ミニユーム粉、フエロシリコン粉の少なくとも1
種以上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1工程で用いる助剤が、鉄粉、CaCl2
KClO3の少なくと1種以上であることを特徴とす
る特許請求の範囲第1項若しくは第2項記載の方
法。 4 第3工程で焙焼ダスト、スラツジ類を溶滓中
に投入するに際し、溶滓を気体バブリングさせな
がら均一に投入することを特徴とする特許請求の
範囲第1項〜第3項のいずれかに記載の方法。
[Claims] 1. A method for treating steelmaking dust and sludge, which comprises the following steps. First step: Steelmaking dust and sludge are mixed with fuel alone or fuel and auxiliary agent in an amount necessary for roasting the dust and sludge. 2nd step: After charging the mixture obtained in the 1st step into a roasting furnace, the fuel is ignited, and the mixture is roasted using the combustion heat of the mixed fuel, etc., to remove moisture and remove the dust and sludge. volatilizes volatile substances contained in Third step: The roasting dust and sludge obtained in the second step are poured into high-temperature slag to dissolve and turn into slag, and the remaining volatile substances are completely volatilized. 4th step: The slag obtained in the 3rd step is cooled and solidified, then crushed, and the iron particles contained therein are recovered by ordinary beneficiation means. Fifth step: The volatile substances volatilized in the second and third steps are collected by suction using a dust collector. 2 The fuel used in the first step is at least one of carbonaceous fuel, aluminum powder, and ferrosilicon powder.
The method according to claim 1, characterized in that the number of species is more than one species. 3 The auxiliary agents used in the first step are iron powder, CaCl 2 ,
The method according to claim 1 or 2, characterized in that at least one kind of KClO 3 is used. 4. Any one of claims 1 to 3, characterized in that when the roasting dust and sludge are introduced into the slag in the third step, the slag is uniformly introduced while bubbling the slag with gas. The method described in.
JP59036823A 1984-02-24 1984-02-24 Treatment of dust and sludge or the like in steel manufacture Granted JPS60181247A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP59036823A JPS60181247A (en) 1984-02-24 1984-02-24 Treatment of dust and sludge or the like in steel manufacture

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP59036823A JPS60181247A (en) 1984-02-24 1984-02-24 Treatment of dust and sludge or the like in steel manufacture

Publications (2)

Publication Number Publication Date
JPS60181247A JPS60181247A (en) 1985-09-14
JPH0128821B2 true JPH0128821B2 (en) 1989-06-06

Family

ID=12480472

Family Applications (1)

Application Number Title Priority Date Filing Date
JP59036823A Granted JPS60181247A (en) 1984-02-24 1984-02-24 Treatment of dust and sludge or the like in steel manufacture

Country Status (1)

Country Link
JP (1) JPS60181247A (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5718509B1 (en) * 2014-06-11 2015-05-13 株式会社清田鋳機 Foundry sand recycling equipment
CN109504863B (en) * 2018-12-29 2021-04-20 巢湖云海镁业有限公司 Slag tapping smelting device with buffer structure at bottom of reduced crude magnesium

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5324001B2 (en) * 1973-10-02 1978-07-18
JPS5217321A (en) * 1975-08-01 1977-02-09 Seiichi Funaki Process for recovering zinc contained in dust from steel manufacture
JPS52138402A (en) * 1976-05-17 1977-11-18 Kawasaki Steel Co Process for recovery of lowwboilinggpoint metals from iron manufacture dust originating from slag

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Publication number Publication date
JPS60181247A (en) 1985-09-14

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