JPS6023870B2 - How to treat electric furnace dust - Google Patents
How to treat electric furnace dustInfo
- Publication number
- JPS6023870B2 JPS6023870B2 JP54167265A JP16726579A JPS6023870B2 JP S6023870 B2 JPS6023870 B2 JP S6023870B2 JP 54167265 A JP54167265 A JP 54167265A JP 16726579 A JP16726579 A JP 16726579A JP S6023870 B2 JPS6023870 B2 JP S6023870B2
- Authority
- JP
- Japan
- Prior art keywords
- electric furnace
- furnace dust
- slag
- steelmaking slag
- dust
- 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
-
- C—CHEMISTRY; METALLURGY
- C21—METALLURGY OF IRON
- C21B—MANUFACTURE OF IRON OR STEEL
- C21B3/00—General features in the manufacture of pig-iron
- C21B3/04—Recovery of by-products, e.g. slag
- C21B3/06—Treatment of liquid slag
-
- C—CHEMISTRY; METALLURGY
- C21—METALLURGY OF IRON
- C21B—MANUFACTURE OF IRON OR STEEL
- C21B2400/00—Treatment of slags originating from iron or steel processes
- C21B2400/02—Physical or chemical treatment of slags
- C21B2400/022—Methods of cooling or quenching molten slag
- C21B2400/026—Methods of cooling or quenching molten slag using air, inert gases or removable conductive bodies
-
- C—CHEMISTRY; METALLURGY
- C21—METALLURGY OF IRON
- C21B—MANUFACTURE OF IRON OR STEEL
- C21B2400/00—Treatment of slags originating from iron or steel processes
- C21B2400/08—Treatment of slags originating from iron or steel processes with energy recovery
-
- 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
- Y02P10/25—Process efficiency
-
- 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Manufacturing & Machinery (AREA)
- Materials Engineering (AREA)
- Metallurgy (AREA)
- Organic Chemistry (AREA)
- Processing Of Solid Wastes (AREA)
Description
【発明の詳細な説明】
本発明は、電気炉ダストの処理方法に関するものである
。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for treating electric furnace dust.
一般に電気炉ダストは主に鉄、亜鉛、鉛等の有用な酸化
物を含有する産業廃棄物である。Generally, electric furnace dust is industrial waste mainly containing useful oxides such as iron, zinc, and lead.
しかし、その中に多量の亜鉛と有害金属を含み、このス
ラグを露天に埋立てた場合、雨水等により有害金属が溶
出する。又高炉原料とする場合はダスト中の亜鉛、鉛が
金属状態で高炉炉壁を侵蝕する。これ等の弊害のために
高炉原料への再利用、及び埋立処分を行う事が出来ない
現状である。更に電気炉ダストには鉛を多く含有するも
のもあり、この様な電気炉ダスト溶融状態にある製鋼ス
ラグ中に添加して処理する場合、処理後の製鋼スラグか
ら鈴イオンを0.1〜0.2風程度溶出する事がある。However, it contains large amounts of zinc and toxic metals, and if this slag is buried in open ground, the toxic metals will be leached out by rainwater. In addition, when used as a raw material for blast furnaces, the zinc and lead in the dust corrode the walls of the blast furnace in a metallic state. Due to these adverse effects, it is currently impossible to reuse it as a blast furnace raw material or dispose of it in a landfill. Furthermore, some electric furnace dust contains a large amount of lead, and when such electric furnace dust is added to molten steelmaking slag for treatment, 0.1 to 0.0% lead is added to the steelmaking slag after treatment. .2 degrees of elution may occur.
この様な電気炉ダストの処理方法として電気炉ダストを
落籍の上から投入して溶解する方法があるが、溶律表面
の硬化被膜に遮られ、溶淫内部に入らず充分な溶解反応
が行われない欠点がある。There is a method for disposing of such electric furnace dust by charging the electric furnace dust from above and dissolving it, but it is blocked by the hardened film on the surface of the melt, preventing it from entering the inside of the melt and allowing a sufficient melting reaction to take place. There is a drawback that it is not done.
又電気炉ダストを前記溶接の上から投入し、押込み蜂に
より物理的に溶蓬内部に圧入して溶解反応を行わせる方
法もあるが、この方法によると溶律内部へ庄入するのに
時間を要する欠点がある。本発明は上記の問題点を解消
し、電気炉ダストを無害化し有効利用することを目的と
するものである。以下、本発明に係る電気炉ダストの処
理方法の概略につき説明する。There is also a method of injecting electric furnace dust from above the welding and physically pressuring it into the inside of the weld using a push bee to cause a melting reaction, but with this method, it takes a long time to inject it into the weld. There are drawbacks that require The present invention aims to solve the above-mentioned problems and to make electric furnace dust harmless and to effectively utilize it. Hereinafter, the outline of the method for treating electric furnace dust according to the present invention will be explained.
即ち亜鉛、鉛その他有害金属を含む電気炉ダストを、高
炉スラグ、赤泥、カラミ、マサ士、粘板岩の中の一種又
は二種以上と共に、のる鍋に受けた溶融状態にある製鋼
スラグに窒素、酸素又は空気を吹き込みバブリングを行
いつつ添加混合することにより、製鋼スラグの表面硬化
被膜を巻き込んでスラグ全体に対流を起しながら新たに
熱を加えることなく製鋼スラグの顕熱を利用し電気炉ダ
スト及び前記一種又は二種以上の添加物を短時間に効果
的に溶融反応させるものである。又此の反応の際、燈化
した亜鉛、鉛は通常の粟塵装置で回収し、有価資源とし
て活用する。In other words, electric furnace dust containing zinc, lead, and other harmful metals is mixed with nitrogen into molten steelmaking slag that is placed in a ladle together with one or more of blast furnace slag, red mud, karami, masashi, and slate. By adding and mixing oxygen or air while performing bubbling, the steelmaking slag's surface hardened coating is involved and convection is generated throughout the slag, making use of the sensible heat of the steelmaking slag without adding new heat. The dust and the one or more additives mentioned above are melted and reacted effectively in a short time. In addition, during this reaction, the ignited zinc and lead are recovered with a normal millet equipment and used as valuable resources.
此の結果、反応後の放冷した製鋼スラグは鉛イオンのみ
ならず、他の重金属イオンの溶出も完全に防止され同時
に崩壊をも防止し、路盤村への有効利用が期待される。
以下本発明の実験結果の数例を示す。As a result, the steelmaking slag left to cool after the reaction completely prevents the elution of not only lead ions but also other heavy metal ions, and at the same time prevents collapse, and is expected to be effectively used for roadbed villages.
Some examples of experimental results of the present invention are shown below.
実験例
製鋼スラグ、電気炉ダスト、赤泥、マサ土、カラミ、高
炉スラグ、粘板岩の各試料を105〜110qCの陣溢
乾燥器で2独特間以上乾燥、次に製鋼スラグ、赤泥、マ
サ士、カラミ、高炉スラグ、粘板岩は4柳以下に粗砕し
、製鋼スラグのみ更に磁選を行い、有磁物を除去した後
供試料とした。Experimental Examples Steelmaking slag, electric furnace dust, red mud, masa soil, karami, blast furnace slag, and slate samples were dried for at least 2 hours in an overflow dryer at 105 to 110qC, then steelmaking slag, red mud, and slate were dried. , karami, blast furnace slag, and slate were coarsely crushed to 4 pieces or less, and only the steelmaking slag was further subjected to magnetic separation to remove magnetic substances, and then used as a sample.
供試料の化学分析値は下記第1表に示す通りである。第
1表尚、工場発生の電気炉ダストの環境庁告示に基づく
溶出試験の結果を第2表に示す。The chemical analysis values of the sample are shown in Table 1 below. Table 1 Table 2 shows the results of an elution test based on the Environmental Agency notification for electric furnace dust generated at factories.
第2表 工場発生電気炉ダストの溶出試験結果供した。Table 2 provides the results of elution tests for factory-generated electric furnace dust.
その試験結果を第3表に示す。第3表
第1表、第2表の例に示す様に、電気炉ダストは電気炉
製鋼での使用原料、操業条件によるものと思われるが、
成分的にもばらつき、溶出試験に於て鉛等の重金属イオ
ンの溶出に可成りの変動が見られる。The test results are shown in Table 3. As shown in the examples in Tables 1 and 2 of Table 3, electric furnace dust seems to be caused by the raw materials used in electric furnace steelmaking and the operating conditions.
There are also variations in composition, and considerable variation is seen in the elution of heavy metal ions such as lead in elution tests.
次に第1表に示す供試料を0.3肌以下に粉砕し適度に
配合してゼーゲル錐を作り熔劉温度測定に一方、製鋼ス
ラグを露融マグネシャ柑禍に入れ1550ooに保持し
たシリコニット電気炉で再溶融させ、これに窒素ガス又
は空気を約3〆/minの流量で2分間吹き込み溶連を
対流させながらその中に赤泥、マサ士、カラミ、高炉ス
ラグ、粘板岩及び電気炉ダスト(約5柵◇べレット)を
添加した。Next, the test samples shown in Table 1 were crushed to 0.3 mm or less and mixed appropriately to make a Zegel cone and used to measure the temperature of the melt.Meanwhile, steelmaking slag was placed in a dew-molten magnesia and held at 1550 oo. It is remelted in a furnace, and nitrogen gas or air is blown into it at a flow rate of about 3/min for 2 minutes to cause convection of the melt, and red mud, masashi, karami, blast furnace slag, slate, and electric furnace dust ( Approximately 5 fences ◇ pellets) were added.
(試料合計200夕)。その後1520〜1510oo
で1分間保持した後、電源スイッチを切り約1200o
oで炉外に出し放冷した。この放冷後のスラグについて
環境庁告示に基づく熔出試験Xray回析による主含有
鉱物の同定、セメント協会法によるフリーライムの測定
、崩壊率の測定(ASTM規格のオートクレープ処理法
で5〜1仇吻粒度につき行い、5肋以下を崩壊物とした
)等の試験を行った。(200 samples in total). After that 1520~1510oo
After holding it for 1 minute, turn off the power switch and heat it to about 1200o.
The mixture was taken out of the furnace at o and allowed to cool. After this slag has been allowed to cool, identification of the main minerals contained in the slag is carried out by Xray diffraction, a melting test based on the notification of the Environment Agency, measurement of free lime by the Cement Association method, and measurement of the disintegration rate (5 to 1 The following tests were conducted for each grain size, and those with 5 or less ribs were considered to be disintegrated.
これらの結果を第4表01〜第6表に示す。第4表 (
1)
第 4 表(2)
・第5表
第6表
第4表で明かな様に、鉛の含有量の少し、電気炉ダスト
単味のべレツトを、窒素又は空気を吹き込みながら溶融
状態の製鋼スラグに添加溶融させた場合、重金属イオン
の溶出はなく問題はない。These results are shown in Tables 4-01 to 6. Table 4 (
1) Table 4 (2) - As is clear from Table 5, Table 6, and Table 4, pellets with a small lead content and only electric furnace dust were brought to a molten state while blowing nitrogen or air. When added to steelmaking slag and melted, no heavy metal ions are eluted and there is no problem.
しかし、鉛含有量の少し、電気炉ダスト単味のべレツト
を、窒素又は空気を吹き込みながら溶融状態の製鋼スラ
グに添加溶融させた場合、鉛イオンが若干港出すること
もある。そこで溶融状態の製鋼スラグに窒素又は空気を
吹き込みながら電気炉ダスト及び高炉スラグ、赤泥、マ
サ土、カラミ、粘板岩を添加すると製鋼スラグの溶接江
温度が低下することで明かな様に融点が下り必然的に粘
度が下る。However, when a pellet containing only a small amount of lead, consisting of electric furnace dust, is added to and melted into molten steelmaking slag while blowing nitrogen or air, some lead ions may be released. Therefore, when electric furnace dust, blast furnace slag, red mud, masa soil, karami, and slate are added to the molten steelmaking slag while blowing nitrogen or air into it, the welding temperature of the steelmaking slag decreases, which clearly lowers the melting point. The viscosity inevitably decreases.
この結果、窒素又は空気の吹き込みによる溶融スラグの
対流が十分に行われて添加物との反応が完全に行われ、
重金属の溶出がなくなる。又、製鋼スラグの崩壊原因で
あるF・Ca○,y−Xa01Si02等が非常に少〈
なり、安定な鉱物にa○,A〆203・Si02・本a
○・Fe203,4Ca○・Aと203・Fe203等
が生成して崩壊しなくなる。尚、製鋼スラグの顕熱不足
の場合には、本実験例から明らかな様に、外部から熱を
補給するか、或は反応熱の高い物質を添加すれば同等の
結果が得られることは自明である。As a result, sufficient convection of the molten slag due to nitrogen or air blowing is carried out, and the reaction with the additives is completely carried out.
Elimination of heavy metal elution. In addition, F・Ca○, y-Xa01Si02, etc., which cause the collapse of steelmaking slag, are extremely small.
and stable mineral a○, A〆203・Si02・hona
○・Fe203,4Ca○・A and 203・Fe203 etc. are generated and no longer collapse. In addition, if the steelmaking slag lacks sensible heat, it is obvious from this experimental example that equivalent results can be obtained by supplying heat from the outside or adding a substance with a high reaction heat. It is.
次に本発明の実施例を示す。Next, examples of the present invention will be shown.
実施例 1
電気炉ダスト単味の添加例
のる鍋に受けた溶融状態の製鋼スラグ約6000k9に
ランスを挿入し、窒素を2分間吹き込み綾藻を対流させ
た。Example 1 Example of addition of electric furnace dust alone A lance was inserted into approximately 6,000 k9 of molten steelmaking slag received in a pot, and nitrogen was blown in for 2 minutes to cause convection of the algae.
次に電気炉ダストのべレットを200k9添加し、引き
続き窒素を2.鏡う間吹き込み添加物を激しく反応させ
、陣化した亜鉛等は集じん機で回収した。反応が終了し
た製鋼スラグは冷却後破砕、磁選処理をした後、環境庁
告示に基づく溶出試験、路盤試験等を行った。その結果
を第7表、第8表に示す。尚、使用電気炉ダストの分析
値は実施例ロの第9表に示す。第7表
第8表
第7表に示す如く鉛含有量の多い電気炉ダスト単味(P
b≠4.67%)を処理した場合、鈴イオンの溶出が若
干見られる。Next, 200k9 of electric furnace dust pellets were added, followed by 2.0kg of nitrogen. The additives were blown into the tank and reacted violently, and the formed zinc and other substances were collected using a dust collector. After the reaction was completed, the steelmaking slag was cooled, crushed, and subjected to magnetic separation treatment, and then subjected to elution tests, roadbed tests, etc. based on the Environmental Agency notification. The results are shown in Tables 7 and 8. The analytical values of the electric furnace dust used are shown in Table 9 of Example B. Table 7 Table 8 As shown in Table 7, electric furnace dust with high lead content (P
b≠4.67%), some elution of bell ions was observed.
実施例 ロ
電気炉ダスト+高炉スラグ+カラミの添加例のる鍋に受
けた溶融状態の製鋼スラグ約600k9中にランスを挿
入し、窒素を2分間吹き込み溶連を対流させた。Example (b) Addition Example of Electric Furnace Dust + Blast Furnace Slag + Karami A lance was inserted into approximately 600 k9 of molten steelmaking slag received in a pot, and nitrogen was blown in for 2 minutes to cause convection of the weld metal.
次にその中に電気炉ダストのべしツトを200kg、高
炉スラグ200k9、カラミ200kgを添加し、引き
続き窒素を2.5分間吹き込み添加物を激しく反応させ
、溝化した亜鉛等は集じん機で回収した。反応が終了し
た製鋼スラグは冷却後破砕、滋選処理した後、環境庁告
示に基づく溶出試験、路盤材試験行った。Next, 200 kg of electric furnace dust, 200 kg of blast furnace slag, and 200 kg of karami were added to the mixture, and nitrogen was then blown in for 2.5 minutes to cause the additives to react vigorously. The grooved zinc etc. was collected by a dust collector. did. After the reaction, the steelmaking slag was cooled, crushed, and sorted, and then subjected to elution tests and roadbed material tests based on the Environmental Agency notification.
その結果を第9表〜第12表に示す。第9表
第10表
第11表
第12表
以上説明した如く、本発明は有害金属酸化物及びその塩
類等を含む産業廃棄物として、その処理に困難性を有し
ている蟹臭気炉ダストを溶融状態にある製鋼スラグの顕
蚕熱と反応機構を巧みに利用して無公害化処理を簡単且
つ容易に行う事が出釆ると共に有価金属の回収を行い、
併せて製鋼スラグの賜嬢防止をも行い得て、聡盤材等へ
の有効利用を計ることが可能となる合理的且つ有益な発
明である。The results are shown in Tables 9 to 12. Table 9 Table 10 Table 11 Table 12 As explained above, the present invention uses crab odor furnace dust, which is difficult to dispose of, as industrial waste containing toxic metal oxides and their salts. By skillfully utilizing the sensible heat and reaction mechanism of steelmaking slag in a molten state, it is possible to perform pollution-free treatment simply and easily, as well as to recover valuable metals.
It is also a rational and useful invention that can prevent steelmaking slag from being lost and make it possible to effectively use it for slag board materials and the like.
Claims (1)
土、粘板岩の中の一種又は二種以上と共に、溶融状態に
ある製鋼スラグに窒素、酸素又は空気を吹き込みバブリ
ングを行いつつ添加混合することを特徴とする電気炉ダ
ストの処理方法。1 Adding and mixing electric furnace dust with one or more of blast furnace slag, red mud, karami, masa soil, and slate while blowing nitrogen, oxygen, or air into molten steelmaking slag while bubbling it. A method for treating electric furnace dust, characterized by:
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP54167265A JPS6023870B2 (en) | 1979-12-22 | 1979-12-22 | How to treat electric furnace dust |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP54167265A JPS6023870B2 (en) | 1979-12-22 | 1979-12-22 | How to treat electric furnace dust |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5689888A JPS5689888A (en) | 1981-07-21 |
| JPS6023870B2 true JPS6023870B2 (en) | 1985-06-10 |
Family
ID=15846523
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP54167265A Expired JPS6023870B2 (en) | 1979-12-22 | 1979-12-22 | How to treat electric furnace dust |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6023870B2 (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS62154462U (en) * | 1986-03-20 | 1987-09-30 |
-
1979
- 1979-12-22 JP JP54167265A patent/JPS6023870B2/en not_active Expired
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS62154462U (en) * | 1986-03-20 | 1987-09-30 |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5689888A (en) | 1981-07-21 |
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