JP3837862B2 - Electric melting furnace operation method - Google Patents

Electric melting furnace operation method Download PDF

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Publication number
JP3837862B2
JP3837862B2 JP24044997A JP24044997A JP3837862B2 JP 3837862 B2 JP3837862 B2 JP 3837862B2 JP 24044997 A JP24044997 A JP 24044997A JP 24044997 A JP24044997 A JP 24044997A JP 3837862 B2 JP3837862 B2 JP 3837862B2
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Japan
Prior art keywords
bag filter
exhaust gas
melting furnace
electric melting
activated carbon
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Expired - Fee Related
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JP24044997A
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Japanese (ja)
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JPH1157373A (en
Inventor
幸雄 丹羽
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Daido Steel Co Ltd
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Daido Steel Co Ltd
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Application filed by Daido Steel Co Ltd filed Critical Daido Steel Co Ltd
Priority to JP24044997A priority Critical patent/JP3837862B2/en
Priority to TW087112746A priority patent/TW384236B/en
Priority to KR1019980031851A priority patent/KR100567705B1/en
Priority to MYPI98003745A priority patent/MY128795A/en
Publication of JPH1157373A publication Critical patent/JPH1157373A/en
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Description

【0001】
【発明の属する技術分野】
本発明は、製鋼工場,廃棄物溶融施設等におけるアーク炉等の電気溶融炉から排ガスに混ってダイオキシン等の有害物質が排出されるのを防止する電気溶融炉の操業方法に関するものである。
【0002】
【従来の技術】
例えばアーク炉が設置された製鋼工場においては、溶解期に発生した排ガスを炉体内から直接吸引してバグフィルタ集じん機に導きダストを捕集する直接排気系と、スクラップ装入時や出鋼時等に該アーク炉から建家内に放出された排ガスを天井フードより吸引してバグハウス型の集じん機に導く建家排気系が従来から設けられている。そして炉体内から直接吸引された直接排気系の排ガスは高温度であるので、冷却塔に通して冷却した後にバグフィルタに通しダストを捕集している。
【0003】
【発明が解決しようとする課題】
しかし従来の上記集じん装置では、排ガス中に含まれている有毒の塩素化合物であるダイオキシン(ポリ塩化ジベンゾパラジオキシン,ポリ塩化ジベンゾフラン等の異性体の総称)や重金属等の有害物質を充分に捕集できない問題があり、従ってその除去効率を向上させる技術の開発が待たれていた。
【0004】
また、排ガス中の有害物質を活性炭等の吸着材を用いて吸着することも従来からなされていたが、高い吸着効率を保持するためには多量の吸着材を要するので、そのコストが嵩むようになると共に、多量に発生する使用済みの吸着材を如何に処理するかが問題となりその処理方法が悪いと二次汚染により環境をさらに悪化させるおそれがあった。
【0005】
【課題を解決するための手段】
本発明は上記のような従来の電気溶融炉の操業上の問題点を解決するためになされたもので、電気溶融炉から排出される排ガスの排気経路に少なくとも2基のバグフィルタを直列に設け、該排気経路の上流側のバグフィルタと下流側のバグフィルタの間に炭素系の吸着剤を吹き込むと共に、下流側のバグフィルタにより該吸着剤を捕集し、該吸着剤を前記電気溶融炉に先入れ材またはカーボンインジェクション材として装入し処理することを特徴とする。
【0006】
【発明の実施の形態】
次に図1に従い本発明の実施の形態を鉄スクラップを溶解させるアーク式の電気溶融炉について説明する。図中、1は炉体中に電極3を垂下させたアーク式の電気溶融炉、10は該電気溶融炉1内で発生した排ガスが排出される排ガス出口、11は該電気溶融炉1の上方の建家の天井に設けられた天井フードである。排ガス出口10には上流から順に燃焼塔13,冷却塔14,バグフィルタ15,投入装置16,バグフィルタ17,ブースタ送風機18が設けられ、また、天上フード11にはダクト5を介し送風機19、およびその下流にバグフィルタ20が設けられる。
【0007】
燃焼塔13は、排ガスを下向に流す間に排ガス中のCO等の未燃成分を燃焼分解する。また、冷却塔14は、冷却水を通水するラジエータが内蔵され、排ガスの温度をバグフィルタの耐熱温度である250℃以下に冷却する。
【0008】
バグフィルタ15は、複数のバグハウス25からなり、排ガス中のダストを捕集してバグフィルタに付着したダストを払い落としダスト搬送コンベア27に排出させるようにしている。また、バグフイルタ17も同様に複数のバグハウス28からなり、排ガス中のダストを捕集してバグフィルタに付着したダストを払い落とし、ダスト搬送コンベア30にダストが払い出されるように構成している。
【0009】
投入装置16は、粉状の活性炭が貯留されたホッパ31と、送風機32と、バグフィルタ15およびバグフィルタ17の間の排ガスダクト26に先端が臨むように設けられた投入スロート33とからなり、該ホッパ31中の活性炭を該送風機32によって投入スロート33に圧送し、該投入スロート33の先端から該活性炭を該排ガスダクト26中に吹き込み得るように構成されている。なおその活性炭の添加量は、例えば排ガス1Nm3当り100〜500mgとする。
【0010】
バグフィルタ17の下流側にはブースタ送風機18が設けられ、該送風機18の下流側には流路切換用ダンパ34を設け、該ダンパの下流側を一方は建家排気系のダクト5の送風機19の上流側に接続し、排ガスを該建家排気系に合流させると伴に、他方は煙突(図示せず)に連なる排気ダクト35に接続している。
【0011】
バグフィルタ20は、複数のバグハウス36からなり、排ガス中のダストを捕集してバグフィルタに付着したダストを払い落とし、ダスト搬送コンベア37に排出させるように構成している。そして該バグフィルタ20の上部から清浄ガスとして大気へ排出している。
【0012】
このため、送風機18の作動により電気溶融炉1から吸引された800〜1200℃の排ガスは、燃焼塔13を通ってCO燃焼等がなされ、冷却塔14を通過することにより250℃以下に冷却された後、バグフィルタ15にてダイオキシン,重金属等を含む細かなダストが捕集される。そして、バグフィルタ15の下流側の排ガスの温度は150℃以下となる。
【0013】
そして、投入装置16より活性炭を吹込むことにより該活性炭にダイオキシンおよび重金属等の有害物が吸着され、その活性炭をその下流のバグフィルタ17により捕集できる。このようにバグフィルタ15の下流側で活性炭を添加することによりバグフィルタ15の上流側で添加するのに比べて活性炭の添加量は少なくてすむ。またバグフィルタ15の下流側で添加することで排ガスの温度も充分に下がることと、バグフィルタ15で火種がトラップされるために粉じん爆発,火災等のリスクも少なくなる利点がある。
【0014】
なお、ホッパ31に活性炭と消石灰との混合体を容れて活性炭と伴に消石灰を吹込むことにより排ガス中のHCl,SO4 等の酸性ガスを中和させることができ、酸性ガスの排出および塩素化合物等の有害物質の再生成を抑えることも可能である。
【0015】
そして、バグフィルタ17よりブースタ送風機18を通って排出された排ガスは、排気ダクト35を通してそのまま大気中に排出することができるが、ダンパ34の切換により建家排気系の排ガスと合流させることにより、その濃度を大幅に希釈できると同時に、温度が60℃程度まで下がるので、ダイオキシン等の有害物質の固体化がさらに進みこれをバグフィルタ20にて確実に捕集することができる。
【0016】
しかして本発明では、バグフィルタ17により補集されそのダスト搬送コンベア30に収集された活性炭を、図1中に破断線6にて示したように空気輸送等により電気溶融炉1に先入れ材またはカーボンインジェクション材として装入する。装入した活性炭は、燃焼熱が溶融金属の加熱のために利用され、または溶解金属の還元剤および成分調整用材として有効利用できる。また活性炭に吸着されていたダイオキシン等の有害物質は、炉内で800℃以上の高温度に加熱されることより熱分解するので、活性炭がそのまま廃棄された場合のような二次汚染により環境悪化を起こすおそれも全くない。
【0017】
なお、バグフイルタ17にて補集した活性炭だけでなく、バグフイルタ20にて捕集した活性炭についても電気溶融炉1に装入してもよい。
また、電気溶融炉1とバグフィルタ15との間には実施形態に示した燃焼塔13,冷却塔14のほか、スクラップバケット予熱室、ツイン型バケツト予熱室等を設けてもよい。
【0018】
また、図1の実施形態ではダクトに吹き込んだ活性炭をバグフイルタで捕集するようにしたが、図2に示したように、活性炭が貯留された吸着塔40を電気溶融炉1の排ガス排気系に設け、排ガスを該吸着塔に通してダイオキシン等の有害物質を吸着させてもよい。即ち、図2に示した吸着塔40は、下部側壁に排ガス入口41、上部側壁に排ガス出口42が設けられ、通気間隙43が生じるように漏斗状低壁44が二重底状に形成され、該低壁44上にホッパ45から流落する活性炭46が貯留され、排ガス入口41から流入した排ガスが図中矢印で示したように通気間隙43から該活性炭貯留部中に入り排ガス出口42に向けて上昇する間に有害物質が該活性炭に吸着されるようにしたものである。
【0019】
なお、有害物質を吸着した活性炭は低部の仕切弁47を解放することにより排出され、該活性炭は同様に電気溶融炉1に先入れ材またはカーボンインジェクション材として装入する。吸着塔40では、バグフイルタによっても捕集しきれない、クロム,すず,マンガン等を含有する微細なダスト、および、ダイオキシン等の有機塩素化合物,硫黄化合物,窒素酸化物等を吸着できる。そして清浄となった排ガスは大気中に放出される。なお、上記吸着塔には活性炭のほか、褐炭等の炭素系の吸着材を用いることができる。
【0020】
【発明の効果】
このように本発明に係る電気溶融炉の操業方法では、電気溶融炉の排ガス中に含まれるダイオキシン等の有害物質を高効率で除去できると共に、有害物質を吸着した炭素系の吸着材を電気溶融炉に装入し処理することにより、二次汚染による環境悪化のおそれがないと共に、吸着材を有効利用できる有益な効果がある。
【図面の簡単な説明】
【図1】本発明に係る電気溶融炉の操業方法の実施形態を示した排ガス系統図。
【図2】本発明に係る電気溶融炉の操業方法の実施に使用する吸着塔の縦断面図。
【符号の説明】
1 電気溶融炉
10 排ガス出口
13 燃焼塔
14 冷却塔
15 バグフィルタ
16 投入装置
17 バグフィルタ
20 バグフイルタ
40 吸着塔
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a method for operating an electric melting furnace that prevents discharge of harmful substances such as dioxin from an electric melting furnace such as an arc furnace in a steel factory, a waste melting facility, and the like.
[0002]
[Prior art]
For example, in a steel mill where an arc furnace is installed, a direct exhaust system that sucks exhaust gas generated during the melting period directly from the furnace body and directs it to the bag filter dust collector to collect dust, and at the time of scrap charging and steel output. Conventionally, there has been provided a building exhaust system that sucks exhaust gas discharged from the arc furnace into the building from a ceiling hood and leads it to a baghouse type dust collector. And since the exhaust gas of the direct exhaust system directly sucked from the furnace body has a high temperature, it is cooled through a cooling tower and then passed through a bag filter to collect dust.
[0003]
[Problems to be solved by the invention]
However, the above conventional dust collectors sufficiently capture harmful substances such as dioxins (a general term for isomers such as polychlorinated dibenzopararadixin and polychlorinated dibenzofuran) and heavy metals contained in exhaust gas. There is a problem that cannot be collected, and therefore development of a technique for improving the removal efficiency has been awaited.
[0004]
In addition, it has been conventionally performed to adsorb harmful substances in exhaust gas using an adsorbent such as activated carbon. However, since a large amount of adsorbent is required to maintain high adsorption efficiency, the cost increases. At the same time, there is a problem of how to treat a large amount of used adsorbent, and if the treatment method is poor, there is a risk that the environment will be further deteriorated due to secondary contamination.
[0005]
[Means for Solving the Problems]
The present invention has been made to solve the above-described problems in operation of the conventional electric melting furnace, and at least two bag filters are provided in series in the exhaust path of the exhaust gas discharged from the electric melting furnace. , together with the blowing carbonaceous adsorbent between the upstream side of the bag filter and the downstream side of the bag filter of the exhaust path, collecting the adsorbent by the downstream side of the bag filter, the electric melting furnace the adsorbent It is characterized by being charged and treated as a pre-fill material or a carbon injection material.
[0006]
DETAILED DESCRIPTION OF THE INVENTION
Next, an arc type electric melting furnace for melting iron scrap will be described with reference to FIG. In the figure, 1 is an arc type electric melting furnace in which an electrode 3 is suspended in a furnace body, 10 is an exhaust gas outlet through which exhaust gas generated in the electric melting furnace 1 is discharged, and 11 is an upper side of the electric melting furnace 1. It is a ceiling hood provided on the ceiling of the building. The exhaust gas outlet 10 is provided with a combustion tower 13, a cooling tower 14, a bag filter 15, a charging device 16, a bag filter 17, and a booster blower 18 in order from the upstream, and the top hood 11 has a blower 19 via a duct 5, and A bag filter 20 is provided downstream thereof.
[0007]
The combustion tower 13 combusts and decomposes unburned components such as CO in the exhaust gas while flowing the exhaust gas downward. The cooling tower 14 has a built-in radiator for passing cooling water, and cools the temperature of the exhaust gas to 250 ° C. or less, which is the heat resistant temperature of the bag filter.
[0008]
The bag filter 15 includes a plurality of bag houses 25. The bag filter 15 collects dust in the exhaust gas, removes the dust attached to the bag filter, and discharges it to the dust transport conveyor 27. Similarly, the bag filter 17 is composed of a plurality of bag houses 28, and is configured to collect dust in the exhaust gas, remove the dust adhering to the bag filter, and discharge the dust to the dust transfer conveyor 30.
[0009]
The charging device 16 includes a hopper 31 in which powdered activated carbon is stored, a blower 32, and a charging throat 33 provided so that the front end faces the exhaust gas duct 26 between the bag filter 15 and the bag filter 17, The activated carbon in the hopper 31 is pumped to the charging throat 33 by the blower 32, and the activated carbon can be blown into the exhaust gas duct 26 from the tip of the charging throat 33. The amount of the activated carbon added is, for example, 100 to 500 mg per 1 Nm 3 of exhaust gas.
[0010]
A booster blower 18 is provided on the downstream side of the bag filter 17, a flow path switching damper 34 is provided on the downstream side of the blower 18, and the blower 19 of the duct 5 of the building exhaust system is provided on the downstream side of the damper. The exhaust gas is joined to the building exhaust system, and the other is connected to an exhaust duct 35 connected to a chimney (not shown).
[0011]
The bag filter 20 includes a plurality of bag houses 36, and is configured to collect dust in the exhaust gas, remove the dust attached to the bag filter, and discharge the dust to the dust transfer conveyor 37. And it is discharged | emitted from the upper part of this bag filter 20 to air | atmosphere as clean gas.
[0012]
Therefore, the exhaust gas at 800 to 1200 ° C. sucked from the electric melting furnace 1 by the operation of the blower 18 is subjected to CO combustion or the like through the combustion tower 13 and is cooled to 250 ° C. or less by passing through the cooling tower 14. After that, fine dust containing dioxins, heavy metals and the like is collected by the bag filter 15. The temperature of the exhaust gas downstream of the bag filter 15 is 150 ° C. or lower.
[0013]
Then, when activated carbon is blown from the charging device 16, harmful substances such as dioxins and heavy metals are adsorbed to the activated carbon, and the activated carbon can be collected by the bag filter 17 downstream thereof. In this manner, the amount of activated carbon added can be reduced by adding activated carbon downstream of the bag filter 15 as compared to adding activated carbon upstream of the bag filter 15. In addition, the addition at the downstream side of the bag filter 15 has an advantage that the temperature of the exhaust gas is sufficiently lowered and the risk of dust explosion, fire, etc. is reduced because the fire type is trapped by the bag filter 15.
[0014]
In addition, acidic gas such as HCl and SO4 in the exhaust gas can be neutralized by filling the hopper 31 with a mixture of activated carbon and slaked lime and blowing slaked lime with the activated carbon. It is also possible to suppress the regeneration of harmful substances such as.
[0015]
The exhaust gas discharged from the bag filter 17 through the booster blower 18 can be discharged into the atmosphere as it is through the exhaust duct 35. By combining the damper 34 with the exhaust gas of the building exhaust system, Since the concentration can be greatly diluted and the temperature is lowered to about 60 ° C., the solidification of harmful substances such as dioxins further proceeds and can be reliably collected by the bag filter 20.
[0016]
In the present invention, the activated carbon collected by the bag filter 17 and collected on the dust conveyor 30 is pre-filled into the electric melting furnace 1 by pneumatic transportation or the like as indicated by the broken line 6 in FIG. Or, it is charged as a carbon injection material. The charged activated carbon is used for heating the molten metal, or can be effectively used as a reducing agent for the molten metal and a component adjusting material. In addition, harmful substances such as dioxin adsorbed on the activated carbon are thermally decomposed by being heated to a high temperature of 800 ° C or higher in the furnace, so that the environment deteriorates due to secondary pollution as when the activated carbon is discarded as it is. There is no risk of causing any problems.
[0017]
The activated carbon collected by the bag filter 20 as well as the activated carbon collected by the bag filter 17 may be charged into the electric melting furnace 1.
In addition to the combustion tower 13 and the cooling tower 14 shown in the embodiment, a scrap bucket preheating chamber, a twin bucket preheating chamber, and the like may be provided between the electric melting furnace 1 and the bag filter 15.
[0018]
In the embodiment of FIG. 1, the activated carbon blown into the duct is collected by the bag filter. However, as shown in FIG. 2, the adsorption tower 40 storing the activated carbon is used as the exhaust gas exhaust system of the electric melting furnace 1. The exhaust gas may be passed through the adsorption tower to adsorb harmful substances such as dioxins. That is, the adsorption tower 40 shown in FIG. 2 is provided with an exhaust gas inlet 41 on the lower side wall and an exhaust gas outlet 42 on the upper side wall, and a funnel-shaped low wall 44 is formed in a double bottom so that a ventilation gap 43 is formed, Activated carbon 46 flowing down from the hopper 45 is stored on the low wall 44, and the exhaust gas flowing in from the exhaust gas inlet 41 enters the activated carbon storage part through the ventilation gap 43 as shown by the arrow in the figure, and toward the exhaust gas outlet 42. While rising, harmful substances are adsorbed on the activated carbon.
[0019]
The activated carbon that has adsorbed the harmful substances is discharged by releasing the lower gate valve 47, and the activated carbon is similarly charged into the electric melting furnace 1 as a pre-fill material or a carbon injection material. The adsorption tower 40 can adsorb fine dust containing chromium, tin, manganese, and the like, and organic chlorine compounds such as dioxin, sulfur compounds, nitrogen oxides, and the like that cannot be collected even by bag filters. The cleaned exhaust gas is released into the atmosphere. In addition to activated carbon, carbon-based adsorbents such as lignite can be used for the adsorption tower.
[0020]
【The invention's effect】
As described above, in the operation method of the electric melting furnace according to the present invention, harmful substances such as dioxin contained in the exhaust gas of the electric melting furnace can be removed with high efficiency, and the carbon-based adsorbent adsorbing the harmful substances can be electrically melted. By charging and treating the furnace, there is no risk of environmental deterioration due to secondary contamination, and there is a beneficial effect that the adsorbent can be used effectively.
[Brief description of the drawings]
FIG. 1 is an exhaust gas system diagram showing an embodiment of an electric melting furnace operating method according to the present invention.
FIG. 2 is a longitudinal sectional view of an adsorption tower used for carrying out the method for operating an electric melting furnace according to the present invention.
[Explanation of symbols]
1 Electric melting furnace 10 Exhaust gas outlet 13 Combustion tower 14 Cooling tower 15 Bag filter 16 Loading device 17 Bag filter 20 Bag filter 40 Adsorption tower

Claims (1)

電気溶融炉から排出される排ガスの排気経路に少なくとも2基のバグフィルタを直列に設け、該排気経路の上流側のバグフィルタと下流側のバグフィルタの間に炭素系の吸着剤を吹き込むと共に、下流側のバグフィルタにより該吸着剤を捕集し、該吸着剤を前記電気溶融炉に先入れ材またはカーボンインジェクション材として装入し処理することを特徴とした電気溶融炉の操業方法。At least two bag filters are provided in series in the exhaust path of the exhaust gas discharged from the electric melting furnace , and a carbon-based adsorbent is blown between the upstream bag filter and the downstream bag filter in the exhaust path, collecting the adsorbent with the downstream side of the bag filter, charged to the process operation method for an electro-melting furnace, characterized in that the adsorbent as first-material or carbon injection material into the electric melting furnace.
JP24044997A 1997-08-20 1997-08-20 Electric melting furnace operation method Expired - Fee Related JP3837862B2 (en)

Priority Applications (4)

Application Number Priority Date Filing Date Title
JP24044997A JP3837862B2 (en) 1997-08-20 1997-08-20 Electric melting furnace operation method
TW087112746A TW384236B (en) 1997-08-20 1998-08-03 Operation of electric melting furnace
KR1019980031851A KR100567705B1 (en) 1997-08-20 1998-08-03 Operation Method of Electric Melting Furnace
MYPI98003745A MY128795A (en) 1997-08-20 1998-08-18 Method of operating an electric melting furnace

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP24044997A JP3837862B2 (en) 1997-08-20 1997-08-20 Electric melting furnace operation method

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JPH1157373A JPH1157373A (en) 1999-03-02
JP3837862B2 true JP3837862B2 (en) 2006-10-25

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