JPH08240310A - Treating apparatus for exhaust gas from melting furnace - Google Patents

Treating apparatus for exhaust gas from melting furnace

Info

Publication number
JPH08240310A
JPH08240310A JP4596795A JP4596795A JPH08240310A JP H08240310 A JPH08240310 A JP H08240310A JP 4596795 A JP4596795 A JP 4596795A JP 4596795 A JP4596795 A JP 4596795A JP H08240310 A JPH08240310 A JP H08240310A
Authority
JP
Japan
Prior art keywords
exhaust gas
liquid
solid
melting furnace
cooling
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.)
Granted
Application number
JP4596795A
Other languages
Japanese (ja)
Other versions
JP3787854B2 (en
Inventor
Tetsuya Watanabe
哲也 渡辺
Junya Nishino
順也 西野
Jujiro Umeda
十次郎 梅田
Hiroshi Aramaki
博 荒巻
Kenichi Tawara
賢一 田原
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.)
IHI Corp
Original Assignee
IHI Corp
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 IHI Corp filed Critical IHI Corp
Priority to JP4596795A priority Critical patent/JP3787854B2/en
Publication of JPH08240310A publication Critical patent/JPH08240310A/en
Application granted granted Critical
Publication of JP3787854B2 publication Critical patent/JP3787854B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Abstract

PURPOSE: To take-out useful heavy metal and salt component by providing a cooling and washing tower wherein exhaust gas is cooled and solid and mist component is washed by bringing washing-liquid into contact with the exhaust gas produced when fly ash or incineration ash is treated by melting, a solid-liquid separation means wherein liquid containing solid component is filtrated, and a heavy metal-separating and collecting means wherein metallic component is collected by electrolysis. CONSTITUTION: Fly ash or incineration ash is sent into a melting furnace 1, and molten matter and exhaust gas, which are produced therein, are sent into a cooling and washing tower 3. At this point, by washing-liquid sprayed from a spraying means 3a, the exhaust gas is cooled and solid and mist component being contained in the exhaust gas is washed away and is sent into a circulation liquid storage part 4 and a solid- liquid separation means 5 together with the washing liquid. The solid-liquid separation means 5 filtrates liquid containing sludge by a filter. Filtrate is sent into a heavy metal-separating and collecting means 6, and sludge component is sent into a sludge- conveying means 8. In the heavy metal-separating and collecting means 6, metallic component being contained in the filtrate is collected by electrolysis, and in the sludge- conveying means 8, the sludge component is again thrown into the melting furnace 1.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、溶融炉排ガスの処理装
置に係り、特に、都市ごみ、産業廃棄物等を焼却する廃
棄物焼却炉から排出される飛灰または焼却灰を、溶融炉
で溶融処理した際に生成される排ガス中の含有金属及び
塩分を処理するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a melting furnace exhaust gas treatment apparatus, and more particularly, to a process for melting fly ash or incineration ash discharged from a waste incinerator for incinerating municipal waste, industrial waste, etc. It treats the contained metal and salt in the exhaust gas produced during the melting treatment.

【0002】[0002]

【従来の技術】都市ごみ等の被焼却物を焼却するための
焼却炉の例として、実開平3−56027号「流動床式
焼却炉」が提案されている。また、飛灰または焼却灰
(ダスト)を溶融炉で溶融処理する関連技術例として、
以下の提案がなされている。 特開昭58−030382号「ダストの処理方法」 特開昭58−040791号「出滓方法」 特開昭60−053780号「直接通電式溶融処理炉
の電極挿入制御装置」 特開昭60−054780号「ダストの溶融処理炉」 特公昭63−051755号「ダストの処理方法」 特開昭63−315187号「焼却炉排ガスの処理
法」 特開平02−099184号「重金属含有ダストの無
害化処理方法」 これらの技術では、都市ごみ等の焼却炉から排出される
飛灰または焼却灰(ダスト)を溶融炉で溶融処理してダ
ストの溶融固化を行なう際に、溶融時に生じる諸問題を
解決するようにしている。
2. Description of the Related Art As an example of an incinerator for incinerating incinerators such as municipal waste, there is proposed a fluidized bed type incinerator of No. Kaikaihei 3-56027. In addition, as a related technology example of melting and processing fly ash or incineration ash (dust) in a melting furnace,
The following suggestions have been made. JP-A-58-030382 "Dust processing method" JP-A-58-040791 "Slag method" JP-A-60-053780 "Electrode insertion control device for direct current type melt processing furnace" JP-A-60- No. 054780 "Melting treatment furnace for dust" JP-B-63-051755 "Dust treatment method" JP-A-63-315187 "Incinerator exhaust gas treatment method" JP-A-02-099184 "Detoxification treatment of heavy metal-containing dust" Method ”These technologies solve various problems that occur during melting when fly ash or incinerator ash (dust) discharged from incinerators such as municipal solid waste is melted and solidified in a melting furnace. I am trying.

【0003】[0003]

【発明が解決しようとする課題】これらのダストの溶融
処理技術であると、従来技術例に記載されているよう
に、ダスト溶融時の温度が1200〜1350℃に達す
るので、ダストに含まれる水銀等の低融点金属、HCl
等がガス状となって排出されてしまう。このため、従来
技術例に加えて、溶融炉の排ガスから、
低融点金属、有害物質または有用物質を回収する必要が
ある。
According to the melting treatment technology for these dusts, the temperature at the time of melting the dust reaches 1200 to 1350 ° C., as described in the prior art example, and therefore the mercury contained in the dust. Low melting point metal such as HCl, HCl
Etc. will be discharged as a gas. Therefore, in addition to the conventional technology example, from the exhaust gas of the melting furnace,
It is necessary to recover low melting point metals, harmful substances or useful substances.

【0004】一般的な排ガスに含まれる水銀等の重金属
を除去する技術としては、例えば、排ガスを湿式吸収器
に導いてNaOH等のアルカリで吸収させ、重金属固定
用のキレート剤を用いて固定する方法がある。また、排
ガスに含まれる煤塵を捕集する技術としては、例えば、
バグフィルタを使用する方法がある。
As a technique for removing heavy metals such as mercury contained in a general exhaust gas, for example, the exhaust gas is guided to a wet absorber and absorbed by an alkali such as NaOH and fixed by using a chelating agent for fixing heavy metals. There is a way. Further, as a technique for collecting soot and dust contained in exhaust gas, for example,
There is a way to use a bug filter.

【0005】しかし、前者のキレート剤を使用する方法
であると、 1)水銀を完全に固定することが困難であり、排水処理
基準を満足できない場合が生じる。 2)長期間の埋立処分間にキレート剤が劣化して、水銀
の滲み出しや溶け出し現象が生じ易い。 3)キレート剤が高価であるため、水銀除去処理コスト
が上昇する。等の解決すべき課題が残される。 また、後者のバグフィルタを使用する方法であると、温
度が高すぎる場合には金属ガスが通り抜けて捕集するこ
とができず、温度が低すぎる場合には、固形分にHCl
等のミスト分が混入して、捕集物の処理が困難になると
ともに、目づまりが発生し易くなり、加えて捕集物が廃
棄物となって減量化が困難になる等の解決すべき課題が
残される。
However, with the former method of using a chelating agent, 1) it is difficult to completely fix mercury, and there are cases where wastewater treatment standards cannot be satisfied. 2) During long-term landfill disposal, the chelating agent deteriorates, and the exudation or dissolution phenomenon of mercury easily occurs. 3) Since the chelating agent is expensive, the cost for removing mercury increases. Problems to be solved are left. Further, in the latter method using the bag filter, when the temperature is too high, the metal gas cannot pass through and be collected, and when the temperature is too low, the solid content contains HCl.
Mist content such as, etc. mixes in, making it difficult to process the collected matter and easily causing clogging. In addition, the collected matter becomes waste and it is difficult to reduce the volume. Is left.

【0006】本発明は、上記事情に鑑みてなされたもの
で、ダストの溶融処理にともなって生成される排ガスの
無害化を図るとともに、有用な重金属や塩分を再利用可
能な状態で系外に取り出すことを目的とするものであ
る。
The present invention has been made in view of the above circumstances, and aims to render the exhaust gas produced by the melting treatment of dust harmless and to remove useful heavy metals and salt from the system in a reusable state. It is intended to be taken out.

【0007】[0007]

【課題を解決するための手段】飛灰または焼却灰を溶融
炉で溶融処理して生成された排ガスを処理する装置とし
て、排ガスを移送する管路に接続され排ガスに洗浄液を
接触させて冷却洗浄する冷却洗浄塔と、該冷却洗浄塔の
下部に接続され固形分含有液を濾過する固液分離手段
と、該固液分離手段に接続され電解により金属分を回収
する重金属分離回収手段とを具備する構成を採用してい
る。冷却洗浄塔の気相部分には、排ガス洗浄後の排ガス
中に含まれるミスト分を捕集するミストエリミネータが
接続状態に配され、重金属分離回収手段には、電解液中
の塩分を分離回収する塩分離手段が配される。重金属分
離回収手段が電解槽である場合、電解槽の負電極に+イ
オン化した金属原子を吸着させる技術が採用されるとと
もに、塩分離手段として、電解槽の正電極に、−イオン
化した塩分を吸着させる技術が採用される。電解槽にあ
っては、各電極に特定の金属のみを析出させる条件また
は複数種類の金属を混合した状態でまとめて析出させる
条件の電解電位が付与される。溶融炉と固液分離手段と
の間には、固形分含有液の濾過時に捕集したスラッジ分
を溶融炉まで移送して再投入するスラッジ移送手段が配
される技術が採用され、冷却洗浄塔と固液分離手段との
間には、洗浄液または固形分含有液を貯留するととも
に、これらの液の少なくともいずれかを洗浄液として冷
却洗浄塔に送り出す循環液貯留部が配される技術が付加
される。
[Means for Solving the Problems] As a device for treating exhaust gas produced by melting fly ash or incineration ash in a melting furnace, the cleaning liquid is connected to a pipeline for transferring the exhaust gas and a cleaning liquid is brought into contact with the cleaning liquid for cooling and cleaning. A cooling and washing tower, a solid-liquid separating means connected to the lower part of the cooling and washing tower for filtering a solid-content liquid, and a heavy metal separating and collecting means connected to the solid-liquid separating means for collecting metal by electrolysis. The configuration is adopted. A mist eliminator that collects the mist contained in the exhaust gas after cleaning the exhaust gas is arranged in a connected state in the gas phase portion of the cooling and cleaning tower, and the heavy metal separation and recovery means separates and recovers the salt content in the electrolytic solution. A salt separation means is provided. When the heavy metal separation / collection means is an electrolytic cell, a technique of adsorbing + ionized metal atoms to the negative electrode of the electrolytic cell is adopted, and as the salt separation means, −ionized salt content is adsorbed to the positive electrode of the electrolytic cell. The technology to make it adopted. In the electrolytic cell, an electrolytic potential is applied to each electrode under the condition of depositing only a specific metal or the condition of depositing a plurality of kinds of metals collectively. Between the melting furnace and the solid-liquid separation means, there is adopted a technology in which a sludge transfer means for transferring the sludge component collected at the time of filtering the solid content-containing liquid to the melting furnace and re-injecting is arranged, and a cooling and washing tower. Between the solid-liquid separation means and the solid-liquid separation means, there is added a technique of storing a cleaning liquid or a liquid containing a solid content and providing a circulating liquid storage part for sending at least one of these liquids as a cleaning liquid to a cooling and cleaning tower. .

【0008】[0008]

【作用】都市ごみ等の焼却炉から排出される飛灰または
焼却灰を溶融炉で溶融処理すると、溶融物とともに排ガ
スが生成される。該排ガスは、管路により冷却洗浄塔に
移送されて、洗浄液に接触させた状態で冷却洗浄され
る。排ガスに含まれる固形分やミスト分は、洗浄液とと
もに冷却洗浄塔の下部から固液分離手段に送り出され、
固形分含有液の濾過による濾過液が重金属分離回収手段
に供給され、電解に基づく金属分の回収がなされる。一
方、冷却洗浄塔の気相部分から、排ガス洗浄後の排ガス
がミストエリミネータに送り込まれることにより、排ガ
ス中のミスト分が捕集される。重金属分離回収手段が電
解槽である場合には、負電極に+イオン化した金属原子
が吸着されることにより、金属分が固形分含有液の濾過
液の電解液から回収され、電解液中の塩分は、塩分離手
段により分離回収される。そして、塩分離手段として、
電解槽の正電極を利用している場合には、−イオン化し
た塩分が正電極に吸着して回収される。電解槽の負電極
を適用して、電解電位を設定することにより、純粋な状
態の特定の金属のみが析出させられ、または複数種類の
金属が混合した状態でまとめて析出させられる。固形分
含有液を濾過することによって捕集されたスラッジ分
は、スラッジ移送手段によって溶融炉まで移送して再投
入することにより、再度溶融状態に導かれる。また、循
環液貯留部により、洗浄液または固形分含有液が貯留さ
れ、洗浄液として冷却洗浄塔に送り出す循環が行なわれ
る。
[Operation] When fly ash or incinerator ash discharged from an incinerator such as municipal solid waste is melted in a melting furnace, exhaust gas is generated together with the molten material. The exhaust gas is transferred to the cooling and washing tower through a pipe and cooled and washed while being in contact with the washing liquid. The solid content and mist content contained in the exhaust gas are sent to the solid-liquid separation means from the lower part of the cooling washing tower together with the washing liquid,
The filtrate obtained by filtering the solid-content liquid is supplied to the heavy metal separating and recovering means, and the metal content is recovered by electrolysis. On the other hand, the mist component in the exhaust gas is captured by sending the exhaust gas after exhaust gas cleaning to the mist eliminator from the gas phase portion of the cooling and cleaning tower. When the heavy metal separation / collection means is an electrolytic cell, the negative electrode adsorbs + ionized metal atoms, whereby the metal content is recovered from the electrolyte solution of the solid content-containing liquid, and the salt content in the electrolyte solution is recovered. Are separated and recovered by the salt separation means. And as a salt separation means,
When the positive electrode of the electrolytic cell is used, the ionized salt is adsorbed on the positive electrode and recovered. By applying the negative electrode of the electrolytic cell and setting the electrolysis potential, only a specific metal in a pure state is deposited or a plurality of kinds of metals are collectively deposited in a mixed state. The sludge component collected by filtering the solid-content liquid is transferred to the melting furnace by the sludge transfer means and is re-introduced, so that the sludge is brought into a molten state again. In addition, the circulation liquid storage unit stores the cleaning liquid or the solid-containing liquid, and circulates the cleaning liquid as a cleaning liquid to the cooling cleaning tower.

【0009】[0009]

【実施例】以下、本発明に係る溶融炉排ガスの処理装置
の一実施例を図1ないし図3に基づいて説明する。図1
において、符号Aは灰供給系(飛灰供給系)、1は溶融
炉、2は管路、3は冷却洗浄塔、4は循環液貯留部、5
は固液分離手段、6は重金属分離回収手段、7は塩分離
手段、8はスラッジ移送手段、9はミストエリミネータ
である。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of a melting furnace exhaust gas treating apparatus according to the present invention will be described below with reference to FIGS. FIG.
In FIG. 1, reference numeral A is an ash supply system (fly ash supply system), 1 is a melting furnace, 2 is a pipe line, 3 is a cooling and washing tower, 4 is a circulating liquid storage section, 5
Is a solid-liquid separating means, 6 is a heavy metal separating and collecting means, 7 is a salt separating means, 8 is a sludge transferring means, and 9 is a mist eliminator.

【0010】前記溶融炉1は、例えば従来技術例
に記載されている直接通電式溶融炉が適用さ
れ、灰供給系(例えば飛灰供給系)Aに接続されて供給
されるダストを内部に投入するためのダスト投入口1a
と、ダストを溶融処理して生成された排ガスを管路2を
経由して排出するための排気口1bと、スラッジ移送手
段8に接続されて供給されるスラッジを内部に投入する
ためのスラッジ投入口1cとを有している。
As the melting furnace 1, for example, a direct current type melting furnace described in the prior art example is applied, and dust supplied to the ash supply system (for example, fly ash supply system) A is fed into the inside. Dust inlet 1a for
And an exhaust port 1b for discharging the exhaust gas generated by melting the dust through the pipe line 2, and a sludge charging for charging the sludge connected to the sludge transfer means 8 into the inside. It has a mouth 1c.

【0011】前記冷却洗浄塔3は、管路2に接続され、
排ガスに噴霧状の洗浄液を接触させて冷却洗浄するため
のスプレー手段3aを有している。
The cooling and washing tower 3 is connected to the pipe line 2,
It has spray means 3a for bringing the exhaust gas into contact with a spray-like cleaning liquid for cooling and cleaning.

【0012】前記循環液貯留部4は、冷却洗浄塔3の下
部と固液分離手段5との間に接続状態に配され、洗浄液
または固形分含有液の上澄み液のいずれかあるいはその
両方を洗浄液として送り出すポンプ等の機能を有してス
プレー手段3aに接続される。
The circulating liquid storage section 4 is connected between the lower portion of the cooling and washing tower 3 and the solid-liquid separating means 5 to wash either the washing liquid or the supernatant liquid of the solid content-containing liquid, or both of them. It is connected to the spraying means 3a with the function of a pump or the like for discharging as.

【0013】前記固液分離手段5は、循環液貯留部4を
介在させて循環液貯留部4の下部に接続され、固形分含
有液を濾過または分離する機能を有するフィルタ、液体
サイクロン、沈降分離槽等が内蔵される。
The solid-liquid separating means 5 is connected to the lower part of the circulating-liquid storing section 4 with the circulating-liquid storing section 4 interposed, and has a function of filtering or separating the solid-content liquid, a hydrocyclone, and a sedimentation separation. A tank etc. is built in.

【0014】前記重金属分離回収手段6は、固液分離手
段5に接続され、少なくとも金属分を回収する機能を有
するものが適用される。該金属分回収機能を有するもの
としては、例えば図2に示す電解槽6Aが適用される。
該電解槽6Aには、内部に配される負電極6a及び正電
極6bと、負電極6a,正電極6bに接続され直流電圧
を印加するための直流電源6cと、内部を区画隔離する
セラミックス等の多孔質状の半透膜6dと、内部に充填
される電解液6eとが配設される。
The heavy metal separating / collecting means 6 is connected to the solid-liquid separating means 5 and has a function of collecting at least a metal component. For example, the electrolytic cell 6A shown in FIG. 2 is applied as the one having the metal content recovery function.
The electrolytic cell 6A has a negative electrode 6a and a positive electrode 6b arranged therein, a DC power source 6c connected to the negative electrode 6a and the positive electrode 6b for applying a DC voltage, a ceramic for partitioning and separating the inside, and the like. The porous semipermeable membrane 6d and the electrolytic solution 6e filled therein are provided.

【0015】前記塩分離手段7は、重金属分離回収手段
6と循環液貯留部4との間に接続状態に配され、図2に
あっては、電解槽6Aにおける正電極6bによる電解液
6e中の塩分分離回収機能が利用される。
The salt separating means 7 is arranged in a connected state between the heavy metal separating / collecting means 6 and the circulating liquid storage part 4, and in FIG. 2, in the electrolytic solution 6e by the positive electrode 6b in the electrolytic cell 6A. The salt separation and recovery function of is used.

【0016】前記スラッジ移送手段8は、溶融炉1と固
液分離手段5との間に接続状態に配され、固液分離手段
5における濾過時に捕集したスラッジ分を、スラッジ投
入口1cまで移送して溶融炉1の内部に投入する機能を
有するものとされる。
The sludge transfer means 8 is arranged in a connected state between the melting furnace 1 and the solid-liquid separation means 5, and transfers the sludge component collected during the filtration in the solid-liquid separation means 5 to the sludge input port 1c. Then, it has a function of charging the inside of the melting furnace 1.

【0017】前記ミストエリミネータ9は、冷却洗浄塔
3の気相部分に接続状態に配され、排ガス洗浄後の排ガ
ス中に含まれるミスト分を捕集するものとされる。
The mist eliminator 9 is arranged in a connected state in the gas phase portion of the cooling and cleaning tower 3 and collects the mist contained in the exhaust gas after cleaning the exhaust gas.

【0018】このように構成されている溶融炉排ガスの
処理装置にあっては、都市ごみ等の焼却炉から排出され
る飛灰または焼却灰が、灰供給系Aから溶融炉1に送り
込まれて、溶融炉1の運転によって溶解処理すると、溶
融物とともに排ガスが生成され、排気口1bから管路2
を経由して冷却洗浄塔3に送り込まれる。
In the melting furnace exhaust gas treating apparatus having the above-mentioned structure, fly ash or incineration ash discharged from an incinerator such as municipal solid waste is sent from the ash supply system A to the melting furnace 1. When the melting process is performed by the operation of the melting furnace 1, exhaust gas is generated together with the melt, and the exhaust gas is discharged from the exhaust port 1b to the pipeline
Is sent to the cooling and washing tower 3 via.

【0019】冷却洗浄塔3にあって、スプレー手段3a
の作動により洗浄液を噴出させて、洗浄液と排ガスとを
接触させると、排ガスの冷却が行なわれるとともに、排
ガスに含まれる固形分やミスト分が洗い流されて、洗浄
液とともに冷却洗浄塔3の下部から循環液貯留部4及び
固液分離手段5に送り出される。
In the cooling and washing tower 3, spray means 3a
When the cleaning liquid is jetted out by the operation of, and the cleaning liquid and the exhaust gas are brought into contact with each other, the exhaust gas is cooled and the solid content and mist contained in the exhaust gas are washed away, and the cleaning liquid is circulated from the lower part of the cooling cleaning tower 3. It is sent out to the liquid storage section 4 and the solid-liquid separation means 5.

【0020】循環液貯留部4にあっては、固形分やミス
ト分を含む洗浄液、つまり固形分含有液を一時貯留する
ことにより、固形分含有液中の上澄み液等の分離した液
相部分を、冷却洗浄塔3におけるスプレー手段3aに戻
す循環が行なわれるとともに、固形分等が多く含まれて
いるスラッジ含有液を、固液分離手段5に送り込むこと
が行なわれる。
In the circulating liquid storage section 4, the cleaning liquid containing solids and mist, that is, the liquid containing solids is temporarily stored to separate the separated liquid phase portion such as the supernatant liquid in the liquid containing solids. The cooling / washing tower 3 is circulated to return to the spraying means 3a, and the sludge-containing liquid containing a large amount of solids and the like is sent to the solid-liquid separating means 5.

【0021】固液分離手段5にあっては、スラッジ含有
液をフィルタに送り込んで濾過する方法等により、液分
の濾液を重金属分離回収手段6に送り込むとともに、堆
積したスラッジ分をスラッジ移送手段8に適宜時期に送
り込むことが行なわれる。
In the solid-liquid separation means 5, the sludge containing liquid is sent to the heavy metal separation and recovery means 6 by a method of sending the sludge-containing liquid to a filter and filtering the same, and the accumulated sludge is sent to the sludge transfer means 8 It will be sent at an appropriate time.

【0022】重金属分離回収手段6にあっては、濾液を
電解することにより、濾液中に含まれる金属分を回収す
ることが行なわれる。図2に示す電解槽6Aに送り込ま
れた濾液は、電解による析出金属の種類に基づいて、ア
ルカリ液を添加する等により、液の酸性度が例えばpH
6程度となるpH調整を行なった後、直流電源6cから
の給電を行なって、負電極6a及び正電極6bの間に金
属の種類に対応した電位を付与して、負電極6aに+イ
オン化した金属原子を吸着させる。pH6の電解液中に
おいて、Cuを負電極6aの表面に付着させる場合であ
ると、図3の位置に示すピークよりも若干右寄りとな
る負電極6aの電位、つまり、概略−0.15〜−0.
3V程度の電解電位に保持することによってCuの析出
を促進させ、Pbを負電極6aの表面に付着させる場合
であると、図3の位置に示すピークよりも若干右寄り
となるように、負電極6aの電位を−0.45〜−0.
55V程度に保持することによってPbの析出を促進さ
せ、Znを負電極6aの表面に付着させる場合である
と、図3の位置に示すピークよりも若干右寄りとなる
ように、負電極6aの電位を−1.05〜−1.15V
程度に保持することによってZnの析出を促進させる。
したがって、電解槽6Aの内部に複数の負電極6aを設
置しておいて、電解槽6Aの内部の電解液(濾液)のp
H調整と負電極6aの電位設定とを順次行なうことによ
り、所望の金属について、負電極6aの表面に析出させ
た状態で分離回収することができる。この場合、他の金
属As,Hg等の陽イオンについても同様の回収を行な
うことができる。
In the heavy metal separating / collecting means 6, the metal component contained in the filtrate is collected by electrolyzing the filtrate. The filtrate sent to the electrolytic cell 6A shown in FIG. 2 has an acidity of, for example, pH by adding an alkaline solution based on the type of metal deposited by electrolysis.
After adjusting the pH to about 6, power was supplied from the DC power supply 6c to apply a potential corresponding to the type of metal between the negative electrode 6a and the positive electrode 6b, and the negative electrode 6a was + ionized. Adsorb metal atoms. In the case of adhering Cu to the surface of the negative electrode 6a in the electrolytic solution of pH 6, the potential of the negative electrode 6a slightly to the right of the peak shown in the position of FIG. 3, that is, about −0.15 to − 0.
When the precipitation of Cu is promoted by maintaining the electrolytic potential of about 3 V and Pb is attached to the surface of the negative electrode 6a, the negative electrode is slightly shifted to the right of the peak shown in the position of FIG. 6a to -0.45--0.
When the deposition of Pb is promoted by maintaining the voltage at about 55 V and Zn is attached to the surface of the negative electrode 6a, the potential of the negative electrode 6a is adjusted so as to be slightly to the right of the peak shown in FIG. To -1.05 to -1.15V
By keeping the content to some extent, precipitation of Zn is promoted.
Therefore, a plurality of negative electrodes 6a are installed inside the electrolytic cell 6A, and p of the electrolytic solution (filtrate) inside the electrolytic cell 6A is
By sequentially adjusting H and setting the potential of the negative electrode 6a, a desired metal can be separated and recovered in a state of being deposited on the surface of the negative electrode 6a. In this case, similar recovery can be performed for cations such as other metals As and Hg.

【0023】また、重金属分離回収手段6が、電解槽6
Aにおける負電極6aに対して金属析出を行なうもので
あると、金属の析出と並行して正電極6bを利用した塩
分の回収を行なうことが可能となる。この場合、正電極
6bが+電位であると、電解により−イオン化した塩分
が正電極6bに吸引されて表面に析出するため、電解槽
6Aの一部を塩分離手段7として利用することにより、
所望の塩分のCl,Na等の陰イオンについても同様の
回収を行なうことができる。
Further, the heavy metal separating / collecting means 6 is composed of the electrolytic cell 6
When the metal is deposited on the negative electrode 6a in A, it is possible to recover the salt content using the positive electrode 6b in parallel with the deposition of the metal. In this case, when the positive electrode 6b is at + potential, the salt ionized by electrolysis is attracted to the positive electrode 6b and is deposited on the surface. Therefore, by using a part of the electrolytic cell 6A as the salt separating means 7,
Similar recovery can be performed for anions such as Cl and Na having a desired salt content.

【0024】電解槽6Aにおいて金属及び塩分が除去さ
れた電解液6eは、図1に矢印で示すように、循環液貯
留部4に戻されて、洗浄液として再利用される。
The electrolytic solution 6e from which the metal and salt are removed in the electrolytic bath 6A is returned to the circulating solution storage section 4 and reused as a cleaning solution, as shown by the arrow in FIG.

【0025】一方、スラッジ移送手段8にあっては、固
液分離手段5において捕集したスラッジ分を、溶融炉1
まで移送してスラッジ投入口1cを経由して再投入する
ことが行なわれ、固形分を溶解して溶融物として再処理
することが繰り返される。
On the other hand, in the sludge transfer means 8, the sludge component collected by the solid-liquid separation means 5 is transferred to the melting furnace 1.
Is carried out and re-input is carried out via the sludge charging port 1c, and the solid content is repeatedly dissolved and re-processed as a molten material.

【0026】次いで、ミストエリミネータ9にあって
は、冷却洗浄塔3の気相部分から、排ガス洗浄後の排ガ
スが送り込まれ、排ガス中に含まれるミスト分を捕集し
て、空気成分や炭酸ガス等のみを大気中に放出する等の
処理がなされる。
Next, in the mist eliminator 9, the exhaust gas after exhaust gas cleaning is sent from the gas phase part of the cooling and cleaning tower 3, and the mist component contained in the exhaust gas is collected to collect air components and carbon dioxide gas. Processing such as releasing only the above into the atmosphere is performed.

【0027】〔他の実施態様〕本発明にあっては、実施
例に加えて以下の技術を包含するものである。 a)図3を参照して説明した前述のCu,Pb等を順番
に析出する技術に代えて、例えばZnの析出に適した電
位により、Cu,Pb,Cd等をまとめて分離回収する
こと。 b)特定の金属、例えばCuだけを純Cuの状態で析出
させて分離回収した後、残りの複数種類の金属をまとめ
て分離回収すること。 c)特定金属に対して、電解液の温度,pH等を変え
て、最適条件により分離回収すること。
[Other Embodiments] The present invention includes the following techniques in addition to the embodiments. a) Instead of the technique of sequentially depositing Cu, Pb, etc. described with reference to FIG. 3, Cu, Pb, Cd, etc. are collectively separated and recovered by a potential suitable for Zn deposition, for example. b) Precipitating a specific metal, for example, only Cu, in the state of pure Cu, separating and recovering, and then collecting and recovering the remaining plural kinds of metals collectively. c) The temperature, pH, etc. of the electrolyte solution should be changed for the specific metal and separated and collected under the optimum conditions.

【0028】[0028]

【発明の効果】本発明に係る溶融炉排ガスの処理装置に
よれば、以下のような効果を奏する。 (1) 溶融炉から排出される排ガスに洗浄液を接触さ
せて、冷却と洗浄とを行なうことにより、排ガス中に混
入した金属ミストや有害物質を除去して、排ガスの無害
化を図ることができる。 (2) 排ガスの洗浄時に排ガス中に混入したミスト分
をミストエリミネータで除去することにより、系外の放
出ガス中へのミスト分の混入を低減し、安全性を向上さ
せることができる。 (3) 排ガスの洗浄によって生じた固形分含有液の濾
過液を電解して金属分を分離回収することにより、有用
な重金属等を個別に分離した状態で回収し、単独金属と
して再利用可能な状態で系外に取り出すことができる。 (4) 固形分含有液の濾過時に捕集したスラッジ分を
溶融炉に再投入することにより、スラッジを再溶解して
金属の回収率を向上させることができる。 (5) スラッジ分を除去した濾液を分離回収するとと
もに、塩分離手段として電解槽の正電極を利用すること
により、金属分の回収と同時に塩分の回収を行なうこと
ができる。 (6) 電解槽の負電極を適用することにより、特定の
金属を純粋な状態で析出させて分離回収することや、複
数種類の金属を混合した状態でまとめて分離回収する等
の融通性を高めることができる。
EFFECTS OF THE INVENTION The melting furnace exhaust gas treatment apparatus according to the present invention has the following effects. (1) The cleaning liquid is brought into contact with the exhaust gas discharged from the melting furnace, and cooling and cleaning are performed to remove metal mist and harmful substances mixed in the exhaust gas, thereby making the exhaust gas harmless. . (2) By removing the mist component mixed in the exhaust gas at the time of cleaning the exhaust gas with the mist eliminator, it is possible to reduce the mixing of the mist component in the released gas outside the system and improve the safety. (3) Useful heavy metals, etc. can be individually separated and recovered by electrolyzing the filtrate of the solid-containing liquid generated by the cleaning of the exhaust gas, and can be reused as a single metal. It can be taken out of the system in the state. (4) By re-charging the sludge component collected at the time of filtering the solid-containing liquid into the melting furnace, the sludge can be redissolved and the metal recovery rate can be improved. (5) By separating and recovering the filtrate from which sludge has been removed, and by using the positive electrode of the electrolytic cell as the salt separating means, it is possible to recover metal and salt at the same time. (6) By applying the negative electrode of the electrolytic cell, the flexibility of depositing a specific metal in a pure state and separating and collecting it, or collectively separating and collecting a plurality of kinds of metals in a mixed state is provided. Can be increased.

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

【図1】本発明に係る溶融炉排ガスの処理装置の一実施
例を示すブロック結線図である。
FIG. 1 is a block connection diagram showing an embodiment of a melting furnace exhaust gas treatment apparatus according to the present invention.

【図2】図1における重金属分離回収手段及び塩分離手
段の例を示す正断面図である。
FIG. 2 is a front cross-sectional view showing an example of a heavy metal separating and collecting means and a salt separating means in FIG.

【図3】析出金属の電解電位と電解電流との関係曲線図
である。
FIG. 3 is a relationship curve diagram between an electrolytic potential of a deposited metal and an electrolytic current.

【符号の説明】[Explanation of symbols]

A 灰供給系(飛灰供給系) 1 溶融炉 1a ダスト投入口 1b 排気口 1c スラッジ投入口 2 管路 3 冷却洗浄塔 3a スプレー手段 4 循環液貯留部 5 固液分離手段 6 重金属分離回収手段 6A 電解槽 6a 負電極 6b 正電極 6c 直流電源 6d 半透膜 6e 電解液 7 塩分離手段 8 スラッジ移送手段 9 ミストエリミネータ A Ash supply system (fly ash supply system) 1 Melting furnace 1a Dust input port 1b Exhaust port 1c Sludge input port 2 Pipe line 3 Cooling and washing tower 3a Spray means 4 Circulating liquid storage section 5 Solid-liquid separation means 6 Heavy metal separation and recovery means 6A Electrolyzer 6a Negative electrode 6b Positive electrode 6c DC power source 6d Semipermeable membrane 6e Electrolyte 7 Salt separation means 8 Sludge transfer means 9 Mist eliminator

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 B03C 3/16 B09B 3/00 303L B09B 3/00 (72)発明者 荒巻 博 神奈川県横浜市磯子区新中原町1番地 石 川島播磨重工業株式会社技術研究所内 (72)発明者 田原 賢一 神奈川県横浜市磯子区新中原町1番地 石 川島播磨重工業株式会社技術研究所内─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification number Reference number within the agency FI Technical display location B03C 3/16 B09B 3/00 303L B09B 3/00 (72) Inventor Hiroshi Aramaki Isogo Yokohama, Kanagawa Prefecture Shin-Nakahara-cho, Ichi-Ku, Ishikawajima-Harima Heavy Industry Co., Ltd. Technical Research Institute (72) Inventor Kenichi Tahara, Shin-Nakahara-cho, Isogo-ku, Yokohama, Kanagawa Prefecture

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 飛灰または焼却灰を溶融炉(1)で溶融
処理して生成された排ガスを処理する装置であって、排
ガスを移送する管路(2)に接続され排ガスに洗浄液を
接触させて冷却洗浄する冷却洗浄塔(3)と、該冷却洗
浄塔の下部に接続され固形分含有液を濾過する固液分離
手段(5)と、該固液分離手段に接続され電解により金
属分を回収する重金属分離回収手段(6)とを具備する
ことを特徴とする溶融炉排ガスの処理装置。
1. A device for treating exhaust gas produced by melting and processing fly ash or incineration ash in a melting furnace (1), which is connected to a pipe line (2) for transferring the exhaust gas to contact the cleaning liquid with the exhaust gas. A cooling and washing tower (3) for cooling and washing, a solid-liquid separating means (5) connected to a lower part of the cooling and washing tower for filtering a solid-content liquid, and a metal component by electrolysis connected to the solid-liquid separating means. And a heavy metal separation and recovery means (6) for recovering the gas.
【請求項2】 冷却洗浄塔(3)の気相部分に、排ガス
洗浄後の排ガス中に含まれるミスト分を捕集するミスト
エリミネータ(9)が接続されることを特徴とする請求
項1記載の溶融炉排ガスの処理装置。
2. The mist eliminator (9) for collecting the mist contained in the exhaust gas after cleaning the exhaust gas is connected to the gas phase portion of the cooling cleaning tower (3). Equipment for melting furnace exhaust gas.
【請求項3】 重金属分離回収手段(6)に、電解液中
の塩分を分離回収する塩分離手段(7)が配されること
を特徴とする請求項1または2記載の溶融炉排ガスの処
理装置。
3. Treatment of exhaust gas from a melting furnace according to claim 1 or 2, wherein the heavy metal separating / collecting means (6) is provided with a salt separating means (7) for separating and collecting salt in the electrolytic solution. apparatus.
【請求項4】 溶融炉(1)と固液分離手段(5)との
間に、固形分含有液の濾過時に捕集したスラッジ分を溶
融炉まで移送して再投入するスラッジ移送手段(8)が
配されることを特徴とする請求項1または2記載の溶融
炉排ガスの処理装置。
4. A sludge transfer means (8) for transferring, to the melting furnace (1) and the solid-liquid separation means (5), sludge components collected at the time of filtration of the solid-content liquid to the melting furnace. ) Is provided, The apparatus for treating melting furnace exhaust gas according to claim 1 or 2, characterized in that.
【請求項5】 冷却洗浄塔(3)と固液分離手段(5)
との間に、洗浄液または固形分含有液を貯留するととも
に、これらの液の少なくともいずれかを洗浄液として冷
却洗浄塔に送り出す循環液貯留部(4)が配されること
を特徴とする請求項1、2、3または4記載の溶融炉排
ガスの処理装置。
5. A cooling and washing tower (3) and a solid-liquid separation means (5)
A circulating liquid storage section (4) for storing a cleaning liquid or a liquid containing a solid content and sending at least one of these liquids as a cleaning liquid to a cooling and cleaning tower is provided between The processing apparatus for melting furnace exhaust gas according to 2, 3, or 4.
【請求項6】 重金属分離回収手段(6)として電解槽
(6A)が適用され、電解槽の負電極(6a)に、+イ
オン化した特定の金属のみを析出させる条件または複数
種類の金属を混合した状態でまとめて析出させる条件の
電解電位が付与されることを特徴とする請求項1記載の
溶融炉排ガスの処理装置。
6. An electrolytic cell (6A) is applied as the heavy metal separating and recovering means (6), and the negative electrode (6a) of the electrolytic cell is mixed with a condition for precipitating only a specific ionized metal or a mixture of plural kinds of metals. 2. The apparatus for treating a melting furnace exhaust gas according to claim 1, wherein an electrolytic potential under a condition of collectively precipitating in this state is applied.
JP4596795A 1995-03-06 1995-03-06 Melting furnace exhaust gas treatment equipment Expired - Fee Related JP3787854B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4596795A JP3787854B2 (en) 1995-03-06 1995-03-06 Melting furnace exhaust gas treatment equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4596795A JP3787854B2 (en) 1995-03-06 1995-03-06 Melting furnace exhaust gas treatment equipment

Publications (2)

Publication Number Publication Date
JPH08240310A true JPH08240310A (en) 1996-09-17
JP3787854B2 JP3787854B2 (en) 2006-06-21

Family

ID=12734013

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4596795A Expired - Fee Related JP3787854B2 (en) 1995-03-06 1995-03-06 Melting furnace exhaust gas treatment equipment

Country Status (1)

Country Link
JP (1) JP3787854B2 (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2012176634A1 (en) * 2011-06-23 2012-12-27 三菱重工業株式会社 Exhaust gas treatment apparatus and orp control method therefor
WO2012176635A1 (en) * 2011-06-23 2012-12-27 三菱重工業株式会社 Exhaust gas treatment apparatus and orp control method therefor
US8877148B2 (en) 2009-07-24 2014-11-04 Graham Dickson Apparatus and method for removing mercury from a gas
CN110064643A (en) * 2019-05-20 2019-07-30 北京建筑材料科学研究总院有限公司 The processing system and processing method of flying ash

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US8877148B2 (en) 2009-07-24 2014-11-04 Graham Dickson Apparatus and method for removing mercury from a gas
WO2012176634A1 (en) * 2011-06-23 2012-12-27 三菱重工業株式会社 Exhaust gas treatment apparatus and orp control method therefor
WO2012176635A1 (en) * 2011-06-23 2012-12-27 三菱重工業株式会社 Exhaust gas treatment apparatus and orp control method therefor
CN110064643A (en) * 2019-05-20 2019-07-30 北京建筑材料科学研究总院有限公司 The processing system and processing method of flying ash

Also Published As

Publication number Publication date
JP3787854B2 (en) 2006-06-21

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