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JPS6011092B2 - How to treat electric furnace dust - Google Patents
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JPS6011092B2 - How to treat electric furnace dust - Google Patents

How to treat electric furnace dust

Info

Publication number
JPS6011092B2
JPS6011092B2 JP56004793A JP479381A JPS6011092B2 JP S6011092 B2 JPS6011092 B2 JP S6011092B2 JP 56004793 A JP56004793 A JP 56004793A JP 479381 A JP479381 A JP 479381A JP S6011092 B2 JPS6011092 B2 JP S6011092B2
Authority
JP
Japan
Prior art keywords
dust
electric furnace
slag
furnace
rooms
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
JP56004793A
Other languages
Japanese (ja)
Other versions
JPS57120634A (en
Inventor
勝司 山本
昭夫 勝
亘 田代
健 中西
源三郎 原田
琢磨 圓
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 JP56004793A priority Critical patent/JPS6011092B2/en
Publication of JPS57120634A publication Critical patent/JPS57120634A/en
Publication of JPS6011092B2 publication Critical patent/JPS6011092B2/en
Expired 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

  • Manufacture And Refinement Of Metals (AREA)
  • Waste-Gas Treatment And Other Accessory Devices For Furnaces (AREA)

Description

【発明の詳細な説明】 本発明は有害重金属を含む電気炉ダストから有価金属を
回収すると共に、凝塊後の溶融スラグが崩壊しない様な
処理方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a processing method for recovering valuable metals from electric furnace dust containing harmful heavy metals and preventing the molten slag after agglomeration from collapsing.

電気炉ダストは電気炉操業中に発生するダストをバック
フィルターにて浦集し、ホッパーからコンベア−によっ
てべレタィザー室に運び適量の水を散水し、約5〜15
肋ぐに造粒して排出される。電気炉ダストの成分は第1
表に示す様に、亜鉛の様な有価金属と共に、クロム、カ
ドミウム等の有害金属酸化物を多量に含有し、雨水に接
すると溶出するので、埋立廃棄処分を行なうことはでき
ない。環境庁告示方法に基づく電気炉ダストの総出試験
結果を第2表に示す。
Electric furnace dust is generated during electric furnace operation, collected in a back filter, transported from a hopper to the beretizer room by a conveyor, and sprinkled with an appropriate amount of water.
It is granulated and discharged. The components of electric furnace dust are
As shown in the table, it contains valuable metals such as zinc, as well as large amounts of toxic metal oxides such as chromium and cadmium, and because they elute when they come in contact with rainwater, they cannot be disposed of in landfills. Table 2 shows the results of the electric furnace dust total output test based on the method notified by the Environment Agency.

又、高炉原料として使用するために、焼縞用副原料とし
て使用した場合は暁結工程で亜鉛を除去することが出来
ないので、電気炉ダスト中の酸化亜鉛が高炉操業中のコ
ークスによって還元され金属となって高炉壁を浸食する
ので使用できない。
In addition, when used as a raw material for blast furnaces or as an auxiliary raw material for baking stripes, zinc cannot be removed during the freezing process, so zinc oxide in electric furnace dust is reduced by coke during blast furnace operation. It cannot be used because it becomes metal and corrodes the blast furnace wall.

第1表 電気炉ダストの化学分析値第2表 電気炉
ダストの溶出試験結果 これらの理由により、各電気炉メーカーは電気炉ダスト
を二次濃縮業者に依頼し電気炉ダスト処理を行なってい
る。
Table 1 Chemical analysis values of electric furnace dust Table 2 Results of elution test of electric furnace dust For these reasons, each electric furnace manufacturer commissions a secondary concentrator to process the electric furnace dust.

すなわち「各電気炉メーカーから搬入されたべレットに
コークス粉等を配合し、還元燈焼炉であるゥェッル炉に
袋入、還元し磁選機で還元鉄べレットを取り、同時に還
元樽化した亜鉛は再び酸化させて、粗酸化亜鉛として回
収し、有害金属酸化物等は湿式処理によって除去して再
利用されている。
In other words, ``The pellets brought in from each electric furnace manufacturer are mixed with coke powder, etc., placed in bags in a well furnace, which is a reduction sintering furnace, and reduced, and the reduced iron pellets are taken out in a magnetic separator, and at the same time the zinc is made into reduced barrels. It is oxidized again and recovered as crude zinc oxide, and harmful metal oxides are removed by wet treatment and reused.

この様に、投棄することも出来ない産業廃棄物から亜鉛
を回収して有価資源として再利用されているのは資源リ
サイクルの面から見ると適切であると考えられるが、処
理工場までの輸送コスト、再加熱に必要なエネルギー、
電気炉メーカーの相当の費用分担等考えると最も良い方
法とは言えない。
In this way, recovering zinc from industrial waste that cannot be dumped and reusing it as a valuable resource is considered appropriate from a resource recycling perspective, but the cost of transporting it to a processing plant is , the energy required for reheating,
This cannot be said to be the best method considering the considerable cost sharing by the electric furnace manufacturer.

又、製鋼溶融スラグの顕熱を有効利用し、溶融スラグの
粘度を低下し、かつ固化温度を低下させて、有害イオン
の溶出防止を行なうために一種又は二種以上を添加する
添加材の赤泥、粘板岩、マサ士、高炉スラグ、カラミの
化学分析値を第3表に示す。第3表 添加材の化学分析
値 本発明は上記諸問題を解決する方法に係り、その要旨は
、電気炉ダストをそれ単独で電気炉に、又はバブリング
ガスを吹込みつ)ある溶融状製鋼スラグに高炉スラグ、
赤泥、カラミ、マサ士、砧板岩の一種又は二種以上と共
に菱入し、主として酸化亜鉛、酸化鉛から成る揮発性酸
化物を摘果する為炉直引集塵装置を二室に別けてダクト
を付け、通常は全室を使って電気炉操業を行ない、樽化
物質が多くなる時点で上記集塵菱道の二室についてそれ
ぞれの入口のダクトのダンパ−をその一方を閉じるべく
切り替えることで通常ダストと揮化性酸化物を個別的に
共に回収することを特徴とする電気炉ダストの処理方法
In addition, one or more additives are added to effectively utilize the sensible heat of molten steelmaking slag, reduce the viscosity of molten slag, lower the solidification temperature, and prevent the elution of harmful ions. Table 3 shows the chemical analysis values for mud, slate, slag, blast furnace slag, and karami. Table 3 Chemical analysis values of additives The present invention relates to a method for solving the above-mentioned problems. blast furnace slag,
In order to collect volatile oxides, mainly zinc oxide and lead oxide, which are mixed with one or more types of red mud, karami, masashi, and slate, the furnace direct dust collector is divided into two rooms and ducted. Normally, the electric furnace is operated using all chambers, and when the amount of barreled material increases, the damper of the duct at the entrance of each of the two chambers of the dust collection pipe is switched to close one of them. A method for treating electric furnace dust, characterized by separately collecting normal dust and volatile oxides.

なお本願方法に於いて副審熱源として電気炉スラグを利
用する場合には、発生するダストの量に比して発生する
溶融電気炉スラグの量が(藤熱を考慮して)不足するの
でダストの一部はリターンさせて再び電気炉へ袋入する
方式を探るのが実操業上は効率的である。
In addition, when electric furnace slag is used as a sub-examiner heat source in the present method, the amount of molten electric furnace slag generated is insufficient compared to the amount of dust generated (taking into account rattan fever), so the amount of dust In actual operation, it would be efficient to explore a method of returning some of the waste and putting it into the electric furnace again.

転炉や高炉にあっては発生する溶融スラグ量が多大であ
るのでこの様な配慮をする必要がないのはいうまでもな
い。以下本願発明方法を開発するに至った実験及びその
結果を示す。
Since the amount of molten slag generated in converters and blast furnaces is large, it goes without saying that such consideration does not need to be taken. The experiments that led to the development of the method of the present invention and their results will be shown below.

〔実験 1〕 図面に示した断面形状を有する公称能力4仇炉蓋旋回炉
頂装入方式の電気炉1及び炉直引用バッグフィルター4
を二室にわけ、通常の操業時には切替ダンパー3および
16を開いて巣堕し、集塵ダストはコンペアーでべレタ
イザー7の上のホツパーに入れ、ベレタィザー7で散水
しながら造粒する。
[Experiment 1] Electric furnace 1 with nominal capacity 4 and furnace top charging method with rotating furnace lid having the cross-sectional shape shown in the drawing, and bag filter 4 for direct feeding into the furnace
is divided into two chambers, and during normal operation, the switching dampers 3 and 16 are opened to let the dust fall, and the collected dust is put into the hopper above the beletizer 7 using a comper, and is granulated while being sprinkled with water by the beletizer 7.

精練末期に通常ダストの発生が少なくなってダストホツ
パ−9からダストベレツトを1000k9投入し、切替
バルブ16を閉じ、切替ダンパ−3を開きバッグフィル
ター6で有価金属回収を行ない、系外のホッパ一に入れ
反応が終了すると逆の操作を行ない通常ダストを集塵し
た。
At the end of scouring, when the amount of dust usually decreases, 1000 k9 of dust pellets are charged from the dust hopper 9, the switching valve 16 is closed, the switching damper 3 is opened, valuable metals are recovered using the bag filter 6, and the metals are put into the hopper outside the system. After the reaction was completed, the operation was reversed to collect the normal dust.

〔実験 2〕 図面に示した断面形成を有する公称能力4仇炉蓋旋回炉
頂装入方式の電気炉1で、通常操業後の製鋼溶蓬を台車
14に乗せた、のる鍋12に約4000k9緋律し、ダ
スト処理室15に入れ、ランス11を装入して空気を1
〜3k9/めで送り、バフリングを行なわせながらダス
トベレットホツパー8からべレツトを900ko、添加
材ホツパー10から添加材を150k9(融点低下材お
よび有害物溶出防止材として赤泥、粘板君、カラミ、マ
サ士、高炉スラグのうち二種類)を4分間で投入し、更
にあと吹きとして3分3現@空気を吹き込んだ後、ラン
スを溶融スラグから引き上げた。
[Experiment 2] In an electric furnace 1 with a nominal capacity of 4 mm and a rotating furnace top charging system having the cross-sectional shape shown in the drawing, the steelmaking melt after normal operation was placed on a trolley 14 and placed in a ladle 12 with approximately 4000k9 Hijitsu, put it in the dust treatment chamber 15, insert the lance 11, and blow the air 1
While buffing, feed 900 ko of pellets from dust pellet hopper 8 and 150 ko of additives from additive hopper 10 (red mud, sukuita kun, karami as melting point lowering materials and harmful substances elution prevention materials). After adding 2 types of molten slag, molten slag, and blast furnace slag for 4 minutes, and blowing air for 3 minutes as after-blow, the lance was lifted from the molten slag.

その時には切替バルブ16は開いて通常ダストを集摩し
、切替バルブ3,17を閉じて、切替バルブ5,18を
開き、バッグフィルター6で集塵し、有価金属酸化物の
回収を行ない、系外のホッパーに入れた。以上の実験結
果としての回収された有価金属酸化物の化学分析値を第
4表に示す。第 4 表 試 料 1 酸化期操業末期に電気炉に投入して回収
物2還元期3 ダスト処理室で溶達で処理した場合の
回収物電気炉に投入した場合、輝化せずに残った成分は
製鋼スラグに固落され、同様にダスト処理室で溶律に投
入した場合、揮化せずに残った成分も製鋼スラグに固落
されているので同スラグの化学分析値および環境庁告示
の溶出試験結果を第5、6表に示す。
At that time, the switching valve 16 is opened to collect normal dust, the switching valves 3 and 17 are closed, the switching valves 5 and 18 are opened, the dust is collected by the bag filter 6, valuable metal oxides are recovered, and the system I put it in the hopper outside. Table 4 shows the chemical analysis values of the valuable metal oxides recovered as the results of the above experiments. Table 4 Samples 1 Recovered materials put into the electric furnace at the end of the oxidation period operation 2 Recovered materials treated by melting in the dust treatment room When put into the electric furnace, the recovered materials remained without brightening The components are solidified into the steelmaking slag, and when they are similarly put into the melting process in the dust treatment room, the components that remain without being volatilized are also solidified into the steelmaking slag, so the chemical analysis value of the slag and the Environmental Agency notification. The dissolution test results are shown in Tables 5 and 6.

第 5 表 電気炉スラグの化学分析値第 6 表
電気炉スラグの溶出試験結果又、同上スラグを路盤村
試験(JIS法)、崩壊率(ASTM規格で10〜25
側の粒度につき行ない、10肌以下を崩壊物とした)、
F・Ca○(JISセメント・協会法)の測定を行ない
、主含有鉱物はX線回析で調べた結果を第7表に示す。
Table 5 Chemical analysis values of electric furnace slag Table 6
Elution test results for electric furnace slag. Also, the above slag was subjected to roadbed village test (JIS method), disintegration rate (10 to 25 according to ASTM standard)
(The grain size was measured on the side, and those below 10 grains were considered to be disintegrated).
F.Ca○ (JIS Cement Association method) was measured, and the main minerals contained were examined by X-ray diffraction. The results are shown in Table 7.

第7表 路盤材試験結果等 ※1 大部分はダスティングを起し崩壊しているので測
定せず。
Table 7: Roadbed material test results, etc. *1 Most of the material had dusted and collapsed, so it was not measured.

〆−。2S・・・グ−20a。〆-. 2S...Goo-20a.

‐Si。2 ※3 JIS B粒度による測定結果を示す。-Si. 2 *3 Indicates the measurement results based on JIS B particle size.

又、酸化期操業の途中および酸化期操業開始前の製鋼原
料と共にダストベレット1000k9を炉項より投入し
、前記と同じ操作で有価金属回収用集塵機6で回収した
ダストを分析しても通常ダストとダストベレツトからの
輝化物が混合し、第8表の如くT・Feは高く、Znの
低い淡褐色のダストであった。第8表 回収ダストの
化学分析値 以上説明した如く、本願発明方法によれば現状では産業
廃棄物としてその処理に窮している電気炉ダストを操業
中の電気炉に投入したり、あるいは溶融状製鋼スラグに
空気をはじめとするバブリングガスを吹込み乍ら高炉ス
ラグ、赤泥、カラミ、マサ士、粘板岩等の添加材と共に
投入し、ダンパーを適宜切替えることにより、有価金属
酸化物を回収し、併せてスラグに残留成分を固溶させ無
害化処理が行なえると共に、凝塊後のスラグは崩壊する
ことがないので路盤材等として有効利用ができるもので
ある。
Furthermore, even if a dust pellet of 1000k9 is introduced from the furnace section together with the steelmaking raw material during the oxidation period operation and before the start of the oxidation period operation, and the dust collected by the valuable metal recovery dust collector 6 is analyzed in the same manner as above, it is not found to be normal dust. Bright substances from the dust pellet were mixed in, and as shown in Table 8, the dust was light brown with high T and Fe content and low Zn content. Table 8: Chemical analysis values of recovered dust As explained above, according to the method of the present invention, electric furnace dust, which is currently difficult to dispose of as industrial waste, can be put into an operating electric furnace or molten While bubbling gas such as air is blown into steelmaking slag, it is added together with additives such as blast furnace slag, red mud, karami, masashi, slate, etc., and valuable metal oxides are recovered by appropriately switching the damper. In addition, residual components can be solid-dissolved in the slag to render it harmless, and since the slag after agglomeration does not disintegrate, it can be effectively used as a roadbed material, etc.

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

図面は本願方法の概要説明図。 図中、1……電気炉、2……操業用集塵ダクト、3……
切替ダンパ−、4……操業用集塵機(バッグフィルター
)、5・・・・・・切替ダンパー、6・・・…有価金属
回収及び操業用集塵機、7・・・・・・ベレタイザ−、
8,9……ダストベレツトホツパ−、10……添加材ホ
ッパー、11……ランス、12…のる鍋、13・・・・
・・溶融スラグ、14・・・・・・台車、15・・・・
・・ダスト処理室、16,17,18・・・・・・切替
ダンパー。
The drawing is a schematic explanatory diagram of the method of the present application. In the figure, 1... electric furnace, 2... dust collection duct for operation, 3...
Switching damper, 4...Dust collector for operation (bag filter), 5...Switching damper, 6...Dust collector for valuable metal recovery and operation, 7...Beletizer,
8, 9... Dust barrel hopper, 10... Additive hopper, 11... Lance, 12... Nori pot, 13...
... Molten slag, 14 ... Trolley, 15 ...
...Dust processing chamber, 16, 17, 18...Switching damper.

Claims (1)

【特許請求の範囲】[Claims] 1 電気炉ダストをそれ単独で電気炉に、又はバブリン
グガスを吹込みつつある溶融状製鋼スラグに高炉スラグ
、赤泥、カラミ、マサ土、粘板岩の一種又は二種以上と
共に装入し、主として酸化亜鉛、酸化鉛から成る揮発性
酸化物を捕集する為炉直引集塵装置を二室に別けてダク
トを付け、通常は全室を使って電気炉操業を行い、揮化
物質が多くなる時点で上記集塵装置の二室についてそれ
ぞれの入口のダクトのダンパーをその一方を閉じるべく
切り替えることで通常ダストと揮化性酸化物を個別的に
共に回収することを特徴とする電気炉ダストの処理方法
1. Electric furnace dust is charged alone into an electric furnace or into molten steelmaking slag into which bubbling gas is being blown together with one or more of blast furnace slag, red mud, karami, masa soil, and slate, and the dust is mainly oxidized. In order to collect volatile oxides consisting of zinc and lead oxide, the furnace direct dust collector is divided into two rooms with ducts attached, and normally all rooms are used for electric furnace operation, which results in a large amount of volatile substances. The electric furnace dust is characterized in that normal dust and volatile oxides are individually collected together by switching the damper of the duct at the entrance of each of the two chambers of the dust collector to close one of them at the time. Processing method.
JP56004793A 1981-01-14 1981-01-14 How to treat electric furnace dust Expired JPS6011092B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP56004793A JPS6011092B2 (en) 1981-01-14 1981-01-14 How to treat electric furnace dust

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP56004793A JPS6011092B2 (en) 1981-01-14 1981-01-14 How to treat electric furnace dust

Publications (2)

Publication Number Publication Date
JPS57120634A JPS57120634A (en) 1982-07-27
JPS6011092B2 true JPS6011092B2 (en) 1985-03-23

Family

ID=11593651

Family Applications (1)

Application Number Title Priority Date Filing Date
JP56004793A Expired JPS6011092B2 (en) 1981-01-14 1981-01-14 How to treat electric furnace dust

Country Status (1)

Country Link
JP (1) JPS6011092B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
NO164253C (en) * 1988-03-28 1990-09-12 Elkem Technology TREATMENT OF DUST.
DE4023686C1 (en) * 1989-09-15 1991-11-14 Klimanek, Margareta, 6680 Neunkirchen, De
DE4303751C1 (en) * 1993-02-09 1994-09-08 Intracon Sarl Process for recycling filter dusts

Also Published As

Publication number Publication date
JPS57120634A (en) 1982-07-27

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