JPS6028896B2 - How to treat electric furnace dust - Google Patents
How to treat electric furnace dustInfo
- Publication number
- JPS6028896B2 JPS6028896B2 JP56072532A JP7253281A JPS6028896B2 JP S6028896 B2 JPS6028896 B2 JP S6028896B2 JP 56072532 A JP56072532 A JP 56072532A JP 7253281 A JP7253281 A JP 7253281A JP S6028896 B2 JPS6028896 B2 JP S6028896B2
- Authority
- JP
- Japan
- Prior art keywords
- electric furnace
- furnace dust
- slag
- dust
- molten slag
- 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
- 239000000428 dust Substances 0.000 title claims description 33
- 239000002893 slag Substances 0.000 claims description 34
- 238000000034 method Methods 0.000 claims description 15
- 229910052725 zinc Inorganic materials 0.000 claims description 13
- 239000011701 zinc Substances 0.000 claims description 13
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 claims description 9
- 230000005587 bubbling Effects 0.000 claims description 8
- 239000008188 pellet Substances 0.000 claims description 7
- 239000000126 substance Substances 0.000 claims description 7
- 239000003638 chemical reducing agent Substances 0.000 claims description 6
- 239000011133 lead Substances 0.000 description 11
- 238000012360 testing method Methods 0.000 description 7
- 238000010828 elution Methods 0.000 description 5
- 239000000463 material Substances 0.000 description 5
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 4
- 238000004458 analytical method Methods 0.000 description 4
- 238000005259 measurement Methods 0.000 description 4
- 239000002994 raw material Substances 0.000 description 4
- 238000007664 blowing Methods 0.000 description 3
- 238000001816 cooling Methods 0.000 description 3
- 239000007789 gas Substances 0.000 description 3
- 150000002500 ions Chemical class 0.000 description 3
- 229910052745 lead Inorganic materials 0.000 description 3
- 229910044991 metal oxide Inorganic materials 0.000 description 3
- 150000004706 metal oxides Chemical class 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- CPLXHLVBOLITMK-UHFFFAOYSA-N Magnesium oxide Chemical compound [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 description 2
- 238000002441 X-ray diffraction Methods 0.000 description 2
- 229910001873 dinitrogen Inorganic materials 0.000 description 2
- 229910001385 heavy metal Inorganic materials 0.000 description 2
- 229910052500 inorganic mineral Inorganic materials 0.000 description 2
- 229910052742 iron Inorganic materials 0.000 description 2
- 229910052749 magnesium Inorganic materials 0.000 description 2
- 239000011777 magnesium Substances 0.000 description 2
- 238000002844 melting Methods 0.000 description 2
- 230000008018 melting Effects 0.000 description 2
- 239000011707 mineral Substances 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 235000018185 Betula X alpestris Nutrition 0.000 description 1
- 235000018212 Betula X uliginosa Nutrition 0.000 description 1
- 101100298225 Caenorhabditis elegans pot-2 gene Proteins 0.000 description 1
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000005485 electric heating Methods 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 238000009472 formulation Methods 0.000 description 1
- 239000002440 industrial waste Substances 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 239000000395 magnesium oxide Substances 0.000 description 1
- 238000007885 magnetic separation Methods 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 238000013021 overheating Methods 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 229910052573 porcelain Inorganic materials 0.000 description 1
- 238000003672 processing method Methods 0.000 description 1
- 238000009877 rendering Methods 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 239000010454 slate Substances 0.000 description 1
- 238000009628 steelmaking Methods 0.000 description 1
- 239000002699 waste material 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
-
- 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
- Y02W30/91—Use of waste materials as fillers for mortars or concrete
Landscapes
- Furnace Details (AREA)
- Curing Cements, Concrete, And Artificial Stone (AREA)
- 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、電気炉ダストの処理方法に関し、更に詳細に
は、電気炉製鋼に於て発生する有害重金属を含む電気炉
ダストを溶融状態にあるスラグの顕熱を利用して一部を
漣化回収し有用資源として再利用すると共に残留分をス
ラグ中に固定化処理する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, and more particularly, the present invention relates to a method for treating electric furnace dust, and more specifically, a method for treating electric furnace dust containing harmful heavy metals generated during electric furnace steelmaking by utilizing the sensible heat of molten slag. The present invention relates to a method in which a portion of the slag is recovered as a slag, reused as a useful resource, and the remaining portion is fixed in slag.
電気炉ダストは、鉄、亜鉛、鉛等の有用な金属酸化物を
含有する産業廃棄物であるが、その中に多量の亜鉛を含
有するために高炉原料へ再利用できず、かつ有害金属を
含有するために、これらの綾出抑制処理を行なって、法
令に適合しなければ埋立、投棄処分も行なうことはでき
ない。Electric furnace dust is an industrial waste that contains useful metal oxides such as iron, zinc, and lead, but because it contains a large amount of zinc, it cannot be reused as a raw material for blast furnaces, and it does not contain harmful metals. Because of the presence of such substances, they cannot be disposed of in landfills or dumped unless they are compliant with laws and regulations.
本発明者等は、かかる問題を鱗決すべく鋭意研究せる結
果、多量の亜鉛等の重金属を含む電気炉ダストを溶融状
態にあるスラグの顕熱を有効利用して一部を樺化回収し
再利用すると共に残留分をスラグ中に固定化処理を行な
う電気炉ダストの処理方法の発明を完成したものである
。As a result of intensive research to solve this problem, the inventors of the present invention effectively utilize the sensible heat of molten slag to collect and recycle a portion of electric furnace dust, which contains a large amount of heavy metals such as zinc, into birch. This invention has completed the invention of a method for treating electric furnace dust, in which the residue is fixed in slag.
即ち、本発明の要旨は、溶融スラグに還元剤を内袋した
電気炉ダストベレツトをバブリングガスと共に吹き込み
薄化する亜鉛、鉛を主体とする金属酸化物を回収すると
共に、電気炉ダスト中に含まれる有害物を無害化するこ
とを特徴とする電気炉ダストの処理方法に存するもので
あり、以下に本発明の方法について詳述する。That is, the gist of the present invention is to recover metal oxides mainly containing zinc and lead which are thinned by blowing an electric furnace dust pellet containing a reducing agent into molten slag together with bubbling gas, and to collect metal oxides mainly containing zinc and lead contained in the electric furnace dust. The invention resides in a method for treating electric furnace dust, which is characterized by rendering harmful substances harmless, and the method of the present invention will be described in detail below.
本発明は、電気炉ダストを処理する方法として溶融スラ
グの有する顕熱を有効利用し、新たに加えることなく、
添加ダストを溶融反応させる方法として、のる鍋に受け
た溶融スラグに還元剤を内装した電気炉ダストベレット
をバブリングガスと共に吹き込み、溶融スラグの対流又
はバブリングを行なわせ漣化亜鉛、鉛等を集塵機で回収
し、粗亜鉛とする。The present invention effectively utilizes the sensible heat of molten slag as a method for treating electric furnace dust, without adding any additional heat.
As a method of melting and reacting the added dust, an electric furnace dust pellet containing a reducing agent is blown into the molten slag received in the ladle along with bubbling gas, and convection or bubbling of the molten slag is performed to remove zinc, lead, etc. The zinc is recovered as crude zinc.
反応が終了した熔融スラグは放流又はのる鍋内で硬化さ
せ、破砕、磁選後路盤材等に有効利用する。ただ、添加
する電気炉ダストに鉛の多い場合があり、該電気炉ダス
トのみを添加して処理するとスラグより鉛イオンを約0
.1脚〜0.2風程度溶出することもある。After the reaction, the molten slag is discharged or hardened in a ladle, and after being crushed and magnetically sorted, it is effectively used for roadbed materials, etc. However, there are cases where the electric furnace dust to be added contains a lot of lead, and if only the electric furnace dust is added to the treatment, lead ions are reduced to about 0% compared to slag.
.. In some cases, about 1 leg to 0.2 leg is eluted.
そこで赤泥、カラミ、マサ士、粘板岩、高炉スラグの一
種以上を添加し鉛イオンの溶出を防止することもある。
一方スラグ中にはF・Ca○(遊離石灰)、ッ−Xa○
・Si02,F・Mg○(遊離マグネシウム)等を含有
しているので崩壊性を有する。この崩壊性を防止するた
めには電気炉ダストのみ添加する場合は多量に使用しな
ければならず、その結果スラグより鉛イオンの溶出の危
険性があるため、赤泥、カラミ、マサ士、粘板岩、高炉
スラグ等を配合、組み合せて処理するものである。なお
本願方法に於いて頭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(顕熱を考慮して)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装入する方式を
採るのが実操業上は効率的である。Therefore, one or more of red mud, karami, masashi, slate, and blast furnace slag may be added to prevent the elution of lead ions.
On the other hand, the slag contains F・Ca○ (free lime), -Xa○
- It has disintegrability because it contains Si02, F, Mg○ (free magnesium), etc. In order to prevent this disintegration, if only electric furnace dust is added, it must be used in large quantities, and as a result, there is a risk of lead ions being leached from the slag. , blast furnace slag, etc. are blended and combined for treatment. In addition, when electric furnace slag is used as the head heat source in the present method, the amount of molten electric furnace slag generated is insufficient compared to the amount of dust generated (taking sensible heat into consideration), so the amount of dust is reduced. In actual operation, it is efficient to return some of the waste and charge 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。以下に本発明の実施例について説明する。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. Examples of the present invention will be described below.
まず第1表は、本発明に使用した使用原料の化学分析値
を示し、第2表は第1表の使用原料について環境庁告示
方法による溶出試験を行った結果を示すものである。First, Table 1 shows the chemical analysis values of the raw materials used in the present invention, and Table 2 shows the results of an elution test performed on the raw materials in Table 1 according to the method notified by the Environment Agency.
第1表
第2表
上記した原料を10500〜11000の垣温乾燥機で
24時間以上乾燥後、スラグはサンプルグラインダーで
4肌以下に粗砕し、0.3肋以下に粉砕してゼーゲル錐
を作り、溶倒温度を測定した。Table 1 Table 2 After drying the above-mentioned raw materials in a 10,500~11,000 scale dryer for more than 24 hours, the slag is crushed into 4 or less pieces using a sample grinder, and then crushed into 0.3 or less pieces using a Seegel cone. The melting temperature was measured.
又、4側以下のスラグの磁選尾鉱を電熱マグネシアルッ
ボに入れ、155000に保持したシリコニット電気炉
で再熔融させ、コークスを1の重量%〜15重量%内装
した電気炉ダストベレット(約2側J〜3側め)とし、
このべレットとしたものを窒素ガス又は空気と一緒にラ
ンスバィプ状物(磁製管)を通して1分間で吹き込み(
合計200夕)、更に窒素ガス又は空気をあと吹きとし
て1分間(約4.3そ/分)吹き込んでバブリングを行
ない152000〜1510こ0で1分間保持後、電源
スイッチを切って約120000で炉外に出し空冷した
。In addition, the magnetic tailings of the slag of 4 sides or less are placed in an electric heating magnesia arubbo and remelted in a siliconite electric furnace maintained at 155,000 ℃, and an electric furnace dust pellet (approximately 2 side J~3 side),
Blow this pellet together with nitrogen gas or air through a lance pipe (porcelain tube) for 1 minute (
After blowing nitrogen gas or air for 1 minute (approximately 4.3 so/min) and keeping the temperature at 152,000 to 1,510 °C for 1 minute, turn off the power switch and heat the furnace at approximately 120,000 °C. I took it outside and let it cool in the air.
このスラグにつき港出試験(環境庁告示方法)、X線回
折による主含有鉱物、崩壊率の測定、(ASTM規格の
オートクレープ処理法で5肌〜IQ肋の粒度につき行な
い5柳以下を崩壊物とした。This slag was subjected to a port export test (method announced by the Environment Agency), measurement of the main mineral content and disintegration rate by X-ray diffraction, and measurements of the particle size of 5 to IQ ribs using the autoclave treatment method of ASTM standards. And so.
)等を行なった。第3表は、以上の実験の内の総倒温合
についての測定結果を示すものである。), etc. Table 3 shows the measurement results for total overheating in the above experiments.
次に代表的な配合組成のものについて下記の如き各測定
を行なった。Next, the following measurements were performed on typical formulations.
ここで該代表的配合組成物についての配合割合を下記第
4表に示す。Here, the blending ratios of the representative blended compositions are shown in Table 4 below.
以下溶出試験結果を第5表に、X線回折による主含有鉱
物の生成状況結果を第6表に、試製スラグの化学分析値
を第7表に、更に試製スラグ中の残存Zn,P雌率を第
8表にそれぞれ示す。The results of the elution test are shown in Table 5, the results of the formation status of the main minerals by X-ray diffraction are shown in Table 6, the chemical analysis values of the trial slag are shown in Table 7, and the percentage of remaining Zn and P in the trial slag is shown below. are shown in Table 8.
第3表第4表
第5表
第6表
※ 冷却時Kダスティンクを して崩壊しているので、
オートクレープ処理を行なわず。Table 3, Table 4, Table 5, Table 6 *K dustink occurs during cooling and disintegrates.
No autoclape treatment.
第7表第8表 次に本願処理方法の一実施例を示す。Table 7 Table 8 Next, an example of the present application processing method will be described.
第1図に示すごとく、熔融スラグ1を入れたのる鍋2(
受律後、約25分、約600k9)をダスト処理室3(
陣化ダストが飛散しない様に三方を鉄板溶接し、他の一
方はのる鍋が入ると下部に若干、冷却空気導入の為に空
間を有したトビラを閉じ)に入れ、コンブレスドェアー
をバルブ4を開いて、ランス5に通しながら、ランス5
を溶融スラグに装入し、バブリングを始め、バルブ6を
開いてホッパー7からコークス粉10%を内装した電気
炉ダストベレット(約5側め)11、約800k9を約
5分間で装入し、バルブ12を閉じて、エアーのみを通
しあと吹きとしてバブリングを行ない、薄化物がほとん
どなくなった(ダストベレット投入中止後、約6分)時
点で、ランスを溶融スラグから引き上げ、バルブ4を閉
じた。As shown in Figure 1, a pot 2 containing molten slag 1 (
After passing the test, the dust treatment room 3 (approximately 600k9) was removed for approximately 25 minutes.
Welded iron plates on three sides to prevent dust from scattering, and closed the door on the other side (which had a small space at the bottom to introduce cooling air when the pot was put in), and connected the combreath door with a valve. Open 4 and pass it through lance 5, then insert lance 5.
was charged into the molten slag, bubbling was started, the valve 6 was opened, and an electric furnace dust pellet (approximately 5th side) 11, approximately 800 k9, containing 10% coke powder was charged from the hopper 7 for approximately 5 minutes. Valve 12 was closed, and only air was passed through to perform bubbling as an after-blow. When the thinned material was almost gone (about 6 minutes after stopping the addition of the dust pellet), the lance was pulled up from the molten slag and valve 4 was closed.
バブリング中に発生するZn,Pb酸化物主体の薄化ダ
ストは集塵機6で回収した。The thinned dust mainly composed of Zn and Pb oxides generated during bubbling was collected by a dust collector 6.
このスラグを冷却後、破砕、磁選処理して、溶出、路盤
村試験等を行なった。この実施例に於ける溶融スラグ、
ダスト及びダスト処理後のスラグの化学分析値を第9表
に、溶出試験結果を第1損表‘こ、揮化回収物の化学分
析値を第11表に、更に路盤材試験結果を第IZ表もこ
それぞれ示す。After cooling this slag, it was crushed, subjected to magnetic separation treatment, and subjected to elution, roadbed village tests, etc. Molten slag in this example,
The chemical analysis values of dust and slag after dust treatment are shown in Table 9, the elution test results are shown in Table 1, the chemical analysis values of the volatilized recovered material are shown in Table 11, and the results of the roadbed material test are shown in Table IZ. The tables are also shown.
第9表
第10表
第11表
第12表
以上述べて来た如く、本願発明方法によれば、溶融スラ
グに還元剤と共に電気炉ダストを装入することによって
Zn,Pbの揮化率が著しく高まる、例えば略同条件で
還元剤を入れずに処理した場合に比べるとZn,Pbと
も約1.2倍近い硬化率を示している。Table 9 Table 10 Table 11 Table 12 As mentioned above, according to the method of the present invention, the volatilization rate of Zn and Pb is significantly increased by charging the electric furnace dust into the molten slag together with the reducing agent. For example, both Zn and Pb show a curing rate that is approximately 1.2 times higher than when treated under substantially the same conditions without adding a reducing agent.
又、バプリングガスの吹き込みによって溶融スラグ、電
気炉ダスト及び還元剤の反応を迅速かつ十分に進行せし
め処理後のスラグは無害化されると共にスラグは非崩壊
性のものとなるので、路盤材等に有効利用ができるとい
う効果がある。In addition, by blowing bubbling gas, the reaction between molten slag, electric furnace dust, and reducing agent proceeds quickly and sufficiently, and the slag after treatment becomes harmless and non-degradable, making it effective for roadbed materials, etc. It has the effect of being usable.
図面は本発明の電気炉ダストの処理に使用する装置の一
実施例を示す系統図。The drawing is a system diagram showing one embodiment of the apparatus used for treating electric furnace dust according to the present invention.
Claims (1)
トをバブリングガスと共に吹き込み、揮化する亜鉛、鉛
を主体とする酸化物を回収すると共に、電気炉ダスト中
に含まれる有害物を無害化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 pellets containing a reducing agent are blown into molten slag along with bubbling gas to recover volatilized oxides mainly consisting of zinc and lead, and to detoxify harmful substances contained in the electric furnace dust. Characteristic electric furnace dust treatment method.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP56072532A JPS6028896B2 (en) | 1981-05-12 | 1981-05-12 | How to treat electric furnace dust |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP56072532A JPS6028896B2 (en) | 1981-05-12 | 1981-05-12 | How to treat electric furnace dust |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS57185936A JPS57185936A (en) | 1982-11-16 |
| JPS6028896B2 true JPS6028896B2 (en) | 1985-07-08 |
Family
ID=13492043
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP56072532A Expired JPS6028896B2 (en) | 1981-05-12 | 1981-05-12 | How to treat electric furnace dust |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6028896B2 (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS60184643A (en) * | 1984-02-29 | 1985-09-20 | Nippon Jiryoku Senko Kk | Treating device for dust and sludge |
-
1981
- 1981-05-12 JP JP56072532A patent/JPS6028896B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS57185936A (en) | 1982-11-16 |
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