JPH10273793A - Method for removing harmful heavy metal from liquid absorbent containing harmful heavy metal - Google Patents

Method for removing harmful heavy metal from liquid absorbent containing harmful heavy metal

Info

Publication number
JPH10273793A
JPH10273793A JP9092861A JP9286197A JPH10273793A JP H10273793 A JPH10273793 A JP H10273793A JP 9092861 A JP9092861 A JP 9092861A JP 9286197 A JP9286197 A JP 9286197A JP H10273793 A JPH10273793 A JP H10273793A
Authority
JP
Japan
Prior art keywords
heavy metal
negative electrode
electrolytic cell
harmful heavy
surfactant
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.)
Pending
Application number
JP9092861A
Other languages
Japanese (ja)
Inventor
Tetsuya Watanabe
哲也 渡辺
Jujiro Umeda
十次郎 梅田
Junya Nishino
順也 西野
Toshiyuki Suzuki
俊行 鈴木
Takeshi Miura
武之 三浦
Masaru Kiyota
優 清田
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 RIIRONAALE KK
IHI Corp
Original Assignee
NIPPON RIIRONAALE KK
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 NIPPON RIIRONAALE KK, IHI Corp filed Critical NIPPON RIIRONAALE KK
Priority to JP9092861A priority Critical patent/JPH10273793A/en
Publication of JPH10273793A publication Critical patent/JPH10273793A/en
Pending 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

Abstract

PROBLEM TO BE SOLVED: To facilitate the electrodeposition of a heavy metal on an electrode from a liq. absorbent. SOLUTION: A liq. absorbent 4 contg. the harmful heavy metal transferred from a waste gas 1 when the waste gas 1 is cleaned is introduced into an electrolytic cell 9. The electrolytic cell 9 is divided into a cathode compartment 12 and an anode compartment 14. A potential is applied between a negative electrode 13 set in the cathode compartment 12 and a positive electrode 15 set in the anode compartment 14 to deposit the heavy metal in the liq. absorbent on the negative electrode 13. A surfactant 19 is added to the cathode compartment 12 of the electrolytic cell 9 to facilitate the electrodeposition of the heavy metal on the negative electrode 13, and a dense deposit is obtained on the electrode surface.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は都市ごみや廃棄され
た家庭電化製品、自動車等のシュレッダーダスト等を焼
却した際に生ずる飛灰や焼却灰を溶融処理する溶融炉か
らの排ガスから洗浄に供した吸収液に移行した有害重金
属を吸収液から除去するための方法に関するものであ
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention is used for cleaning exhaust gas from a melting furnace that melts fly ash and incinerated ash generated when incinerating municipal waste, discarded household appliances, shredder dust of automobiles and the like. The present invention relates to a method for removing harmful heavy metals transferred to an absorbing solution from the absorbing solution.

【0002】[0002]

【従来の技術】都市ごみや廃棄された家庭電化製品等の
シュレッダーダストを焼却炉で焼却させると、焼却炉か
ら排出される飛灰又は焼却灰には鉛等の如き有害な重金
属が含まれているので、これを溶融炉で溶融処理し、該
溶融炉で溶融処理した際に生成される排ガスを洗浄し、
該洗浄に供した吸収液に排ガスから移行した有害重金属
を除去し回収することが行われている。
2. Description of the Related Art When shredder dust such as municipal waste and discarded household appliances is incinerated in an incinerator, fly ash or incinerated ash discharged from the incinerator contains harmful heavy metals such as lead. Therefore, this is melted in a melting furnace, and the exhaust gas generated when the melting processing is performed in the melting furnace is washed,
It has been practiced to remove and recover harmful heavy metals transferred from exhaust gas into the absorbent used for the washing.

【0003】一例を示すと、図2に示す如く、焼却炉か
ら排出された飛灰や焼却灰aを溶融炉bに導入して溶融
処理し、溶融炉bからの排ガスcを吸収塔dに入れて吸
収液で洗浄し、排ガスc中の重金属を吸収液とともに循
環槽eに移し、更に、重金属を含む吸収液を固液分離器
fに入れて固液分離を行い、循環槽e内の吸収液の一部
は吸収塔dのスプレー装置gへ循環させるようにし、上
記固液分離器fで濾過又は分離された重金属を含む吸収
液を重金属分離回収装置hとしての電解槽へ供給し、+
イオン化された重金属を負電極に電着させて回収するよ
うにしたものが提案されている(特願平7−45967
号)。なお、iは固液分離器fで濾過するときに捕集し
たスラッジ分を溶融炉b内へ移送するスラッジ移送手段
である。
As an example, as shown in FIG. 2, fly ash and incinerated ash a discharged from an incinerator are introduced into a melting furnace b for melting, and exhaust gas c from the melting furnace b is sent to an absorption tower d. Into the circulation tank e together with the absorption liquid, the absorption liquid containing the heavy metal is further introduced into the solid-liquid separator f to perform solid-liquid separation. A part of the absorbing solution is circulated to the spray device g of the absorption tower d, and the absorbing solution containing the heavy metal filtered or separated by the solid-liquid separator f is supplied to an electrolytic cell as a heavy metal separation and recovery device h, +
A method has been proposed in which an ionized heavy metal is recovered by electrodeposition on a negative electrode (Japanese Patent Application No. 7-45967).
issue). Incidentally, i is a sludge transfer means for transferring the sludge collected during filtration by the solid-liquid separator f into the melting furnace b.

【0004】[0004]

【発明が解決しようとする課題】ところが、上記既に提
案されている重金属回収方式では、重金属分離回収装置
としての電解槽で重金属を電極に付着させることができ
るので、電極ごと取り出して重金属を精製することがで
きるものである。
However, in the heavy metal recovery system proposed above, the heavy metal can be attached to the electrode in an electrolytic cell as a heavy metal separation and recovery apparatus. Is what you can do.

【0005】本発明は、上記提案されているものを更に
一歩進め、目的とする重金属を含む吸収液から重金属を
電極表面に緻密に電着させるようにしようとするもので
ある。
The present invention is intended to take the above-mentioned proposal one step further, and to attempt to finely deposit the heavy metal on the electrode surface from the absorption liquid containing the target heavy metal.

【0006】[0006]

【課題を解決するための手段】本発明は、上記課題を解
決するために、ごみ処理施設から排出された排ガスを吸
収液と接触させて洗浄することにより排ガスから移行し
た有害重金属を含む吸収液を、電解槽に入れ、該電解槽
に設置された負電極と正電極との間に電位を付与させて
上記重金属を含む吸収液中から負電極に重金属を析出さ
せるときに、電解槽内に界面活性剤を添加する方法とす
る。
SUMMARY OF THE INVENTION In order to solve the above-mentioned problems, the present invention provides an absorbing solution containing harmful heavy metals transferred from an exhaust gas by washing exhaust gas discharged from a refuse treatment facility by contacting the exhaust gas with the absorbing solution. Is placed in an electrolytic cell, and when a heavy metal is deposited on the negative electrode from the absorbing solution containing the heavy metal by applying a potential between the negative electrode and the positive electrode provided in the electrolytic cell, The method is to add a surfactant.

【0007】界面活性剤を添加すると、負電極への吸収
液中の重金属の電着性がよくなり、電極表面に緻密な析
出が得られる。
[0007] When a surfactant is added, the electrodeposition of heavy metals in the absorbing solution to the negative electrode is improved, and dense deposition is obtained on the electrode surface.

【0008】[0008]

【発明の実施の形態】以下、本発明の実施の形態を図面
を参照して説明する。
Embodiments of the present invention will be described below with reference to the drawings.

【0009】図1は本発明の実施の一形態を示すもの
で、図2に示した場合と同様に、溶融炉からの排ガス1
を吸収塔2内に入れてスプレー装置3から噴出される吸
収液と接触させて洗浄し、排ガス1からの有害重金属を
含む吸収液4を循環槽5に移して、該循環槽5内の上澄
液の如き一部の液を循環ポンプ6、循環ライン7でスプ
レー装置3へ循環するようにし、又、循環槽5から吸収
液4を固液分離器8に移し、ここで濾過又は分離された
重金属を含む吸収液4を、重金属分離回収装置としての
電解槽9へ供給管10より供給するようにしてある構成
において、上記電解槽9には、多孔質状の半透膜11を
設置して、片側を陰極室12として負電極13を設置す
ると共に、反対側を陽極室14として正電極15を設置
し、且つ両電極13と15を直流電源16に接続して、
給電により負電極13と正電極15の間に電位を付与さ
せるようにし、更に、負電極13を設置した陰極室12
に界面活性剤供給管17を接続し、又、上記固液分離器
8からの重金属を含む吸収液4を電解槽9の陰極室12
側へ供給して、重金属の蓄積がない吸収液を陰極室12
より戻し管18にて循環槽5へ戻すようにし、吸収液を
系内で再使用できるようにする。
FIG. 1 shows an embodiment of the present invention. As in the case shown in FIG.
Is put into the absorption tower 2, washed by contacting with the absorbing liquid ejected from the spray device 3, and the absorbing liquid 4 containing harmful heavy metals from the exhaust gas 1 is transferred to the circulation tank 5, A part of the liquid such as a clear liquid is circulated to the spray device 3 by a circulation pump 6 and a circulation line 7, and the absorption liquid 4 is transferred from a circulation tank 5 to a solid-liquid separator 8, where it is filtered or separated. In the configuration in which the absorbent 4 containing the heavy metal is supplied from a supply pipe 10 to an electrolytic cell 9 as a heavy metal separation and recovery device, a porous semipermeable membrane 11 is provided in the electrolytic cell 9. By installing the negative electrode 13 on one side as the cathode chamber 12, installing the positive electrode 15 on the other side as the anode chamber 14, and connecting both electrodes 13 and 15 to a DC power supply 16,
An electric potential is applied between the negative electrode 13 and the positive electrode 15 by power supply, and the cathode chamber 12 in which the negative electrode 13 is installed is further provided.
Is connected to a surfactant supply pipe 17, and the absorbent 4 containing heavy metals from the solid-liquid separator 8 is supplied to the cathode chamber 12 of the electrolytic cell 9.
To the cathode chamber 12 and supply the absorbing solution having no accumulation of heavy metal to the cathode chamber 12.
Then, the liquid is returned to the circulation tank 5 through the return pipe 18 so that the absorbent can be reused in the system.

【0010】本発明においては、上記界面活性剤供給管
17を通して電解槽9に供給する界面活性剤19として
は、ノニオン系界面活性剤を用いるようにするが、特に
ポリオキシアルキレン縮合物が好ましく、ポリエチレン
グリコール、ポリエチレングリコール・ポリプロピレン
グリコールブロックポリマー、脂肪酸アルコール・アル
キレンオキサイド・エーテル、芳香族アルコール・アル
キレンオキサイド・エーテル、脂肪族アミン・アルキレ
ンオキサイド付加物等が例示できる。又、正電極15に
カーボン電極、負電極13にステンレス板を用いて、
0.5〜5A/dm2 で電気分解させるようにする。
In the present invention, a nonionic surfactant is used as the surfactant 19 supplied to the electrolytic cell 9 through the surfactant supply pipe 17, and a polyoxyalkylene condensate is particularly preferable. Examples thereof include polyethylene glycol, polyethylene glycol / polypropylene glycol block polymer, fatty acid alcohol / alkylene oxide ether, aromatic alcohol / alkylene oxide ether, and aliphatic amine / alkylene oxide adduct. Also, using a carbon electrode for the positive electrode 15 and a stainless steel plate for the negative electrode 13,
Electrolysis is performed at 0.5 to 5 A / dm 2 .

【0011】今、固液分離器8からの重金属を含む吸収
液4を電解槽9内の陰極室12へ供給して、負電極13
と正電極15の間に電位を付与させると、+イオン化し
た重金属が負電極13の表面に電着させられる。この
際、電解槽9の陰極室12の吸収液中に、有機添加物と
してノニオン系界面活性剤19を供給管17より添加す
ると、負電極13表面に緻密に電着させることができ、
負電極13表面に金属皮膜として回収することができ
る。
Now, the absorbing solution 4 containing the heavy metal from the solid-liquid separator 8 is supplied to the cathode chamber 12 in the electrolytic cell 9 and the negative electrode 13 is supplied.
When a potential is applied between the negative electrode 13 and the positive electrode 15, the + ionized heavy metal is electrodeposited on the surface of the negative electrode 13. At this time, when a nonionic surfactant 19 is added as an organic additive from the supply pipe 17 to the absorbing solution in the cathode chamber 12 of the electrolytic cell 9, the nonelectrolytic surfactant 19 can be densely electrodeposited on the surface of the negative electrode 13.
It can be collected as a metal film on the surface of the negative electrode 13.

【0012】又、負電極13と正電極15の間に付与さ
れる電位を変えると、その電位に対応する重金属を選択
的に負電極13に析出させて付着させることができ、こ
こに界面活性剤19を添加することにより負電極13へ
の重金属の付着性をよくすることができる。
When the potential applied between the negative electrode 13 and the positive electrode 15 is changed, a heavy metal corresponding to the potential can be selectively deposited on the negative electrode 13 and adhered thereto. By adding the agent 19, the adhesion of the heavy metal to the negative electrode 13 can be improved.

【0013】なお、希薄な濃度の金属イオンを含む水溶
液を電解し負電極上に金属を析出させる場合、負電極に
析出する金属の種類により電解に必要な電圧は異なる
が、負電極13上に水素が発生する電位を基準点0.0
0Vとした場合の各種金属の析出電位を示すと、次のと
おりである。
When an aqueous solution containing a dilute concentration of metal ions is electrolyzed to deposit a metal on the negative electrode, the voltage required for the electrolysis depends on the type of the metal deposited on the negative electrode. The reference potential is 0.0
The deposition potentials of various metals at 0 V are as follows.

【0014】 Cr:−0.74V Fe:−0.44V Ni:−0.25V Pb:−0.13V H2 : 0.00V Cu: 0.34V 金属の析出は負電極13上での反応であるため、上記の
電位が小さいほど(マイナス側であるほど)電解に高い
電位を必要とすることを意味する。したがって、目的の
重金属のみを選択的に負電極に析出させようとするとき
は、電位を変えて行くことによりその電位の重金属のみ
を順に析出することができる。
Cr: −0.74 V Fe: −0.44 V Ni: −0.25 V Pb: −0.13 V H 2 : 0.00 V Cu: 0.34 V Metal deposition is a reaction on the negative electrode 13. Therefore, the smaller the potential is (the more negative the potential is), the higher the potential is required for electrolysis. Therefore, when only the intended heavy metal is to be selectively deposited on the negative electrode, by changing the potential, only the heavy metal having the potential can be sequentially deposited.

【0015】[0015]

【実施例】本発明者等が界面活性剤添加の効果について
行った実験結果を次に説明する。ハロゲン系成分を含む
電解浴に界面活性剤を添加しなかったときは、負電極に
析出する金属は粗雑であった。これに対し、界面活性剤
を約1〜2%添加した結果、負電極13表面に緻密な析
出が得られた。
EXAMPLES The results of experiments conducted by the present inventors on the effect of adding a surfactant will be described below. When the surfactant was not added to the electrolytic bath containing the halogen component, the metal deposited on the negative electrode was coarse. On the other hand, as a result of adding about 1 to 2% of the surfactant, dense precipitation was obtained on the surface of the negative electrode 13.

【0016】又、上記実験において、電解液に、無機酸
たとえば硫酸、有機酸の代表として、アルカンスルホン
酸、たとえば、メタンスルホン酸、アルカノールスルホ
ン酸、たとえば、フェノールスルホン酸を用いることに
より負電極の析出金属表面は緻密になった。
In the above experiment, the negative electrode was formed by using an alkanesulfonic acid such as methanesulfonic acid or alkanolsulfonic acid such as phenolsulfonic acid as a representative of an inorganic acid such as sulfuric acid or an organic acid. The surface of the deposited metal became dense.

【0017】[0017]

【発明の効果】以上述べた如く、本発明の有害重金属含
有吸収液からの有害重金属除去方法によれば、重金属を
含む吸収液を電解槽に入れ、該電解槽内に界面活性剤を
添加し、負電極と正電極の間に電位を付与させることに
より、電解槽内で吸収液中の重金属を負電極に析出させ
て回収することができ、この際、界面活性剤の添加によ
り析出される重金属を電極表面に緻密に電着させること
ができて、商品価値を高めることができ、電位を順次変
えて運転することにより複数種類の金属が含まれている
吸収液から目的の金属のみを順に選択的に析出させるこ
とができる、という優れた効果を奏し得る。
As described above, according to the method for removing harmful heavy metals from the harmful heavy metal-containing absorbing solution of the present invention, the absorbing solution containing heavy metals is put into the electrolytic cell, and the surfactant is added to the electrolytic cell. By applying a potential between the negative electrode and the positive electrode, heavy metals in the absorbing solution can be precipitated and collected on the negative electrode in the electrolytic cell, and at this time, are precipitated by the addition of a surfactant. Heavy metals can be densely electrodeposited on the electrode surface, and the commercial value can be increased.By changing the potential sequentially, only the target metal can be removed in order from the absorbing solution containing multiple types of metals. An excellent effect that it can be selectively deposited can be obtained.

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

【図1】本発明の実施の一形態を示す概要図である。FIG. 1 is a schematic diagram showing an embodiment of the present invention.

【図2】従来の排ガスの処理と吸収液からの重金属除去
について示す概要図である。
FIG. 2 is a schematic diagram showing conventional treatment of exhaust gas and removal of heavy metals from an absorbent.

【符号の説明】[Explanation of symbols]

1 排ガス 2 吸収塔 4 吸収液 9 電解槽 11 多孔質状の半透膜 13 負電極 15 正電極 19 界面活性剤 DESCRIPTION OF SYMBOLS 1 Exhaust gas 2 Absorption tower 4 Absorbing liquid 9 Electrolysis tank 11 Porous semipermeable membrane 13 Negative electrode 15 Positive electrode 19 Surfactant

───────────────────────────────────────────────────── フロントページの続き (72)発明者 西野 順也 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 鈴木 俊行 東京都江東区豊洲二丁目1番1号 石川島 播磨重工業株式会社東京第一工場内 (72)発明者 三浦 武之 埼玉県大宮市島町1178−3 (72)発明者 清田 優 埼玉県北足立郡伊奈町栄1−146−5 ──────────────────────────────────────────────────続 き Continuing on the front page (72) Inventor Junya Nishino 1st place, Shin-Nakahara-cho, Isogo-ku, Yokohama-shi, Kanagawa Ishikawashima Harima Heavy Industries, Ltd. (72) Inventor Toshiyuki Suzuki 2-1-1 Toyosu, Koto-ku, Tokyo No. 1 Ishikawajima Harima Heavy Industries, Ltd., Tokyo No. 1 Factory (72) Inventor Takeyuki Miura 1178-3, Shimacho, Omiya City, Saitama Prefecture (72) Inventor Yu Seita 1-146-5 Inamachi Sakae Kita Adachi-gun, Saitama Prefecture

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 ごみ処理施設から排出された排ガスを吸
収液と接触させて洗浄することにより排ガスから移行し
た有害重金属を含む吸収液を、電解槽に入れ、該電解槽
に設置された負電極と正電極との間に電位を付与させて
上記重金属を含む吸収液中から負電極に重金属を析出さ
せるときに、電解槽内に界面活性剤を添加することを特
徴とする有害重金属含有吸収液からの有害重金属除去方
法。
1. An exhaust solution discharged from a refuse treatment facility, which is brought into contact with an absorbent and washed by bringing the exhaust gas into contact with the absorbent and containing a harmful heavy metal transferred from the exhaust gas into an electrolytic cell, and a negative electrode installed in the electrolytic cell. A harmful heavy metal-containing absorbing solution, wherein a surfactant is added to the electrolytic cell when a heavy metal is deposited on the negative electrode from the absorbing solution containing the heavy metal by applying a potential between the negative electrode and the positive electrode. Of hazardous heavy metals from wastewater.
【請求項2】 電解槽を多孔質状の半透膜で仕切って、
負電極設置側の吸収液に界面活性剤を添加するようにす
る請求項1記載の有害重金属含有吸収液からの有害重金
属除去方法。
2. An electrolytic cell partitioned by a porous semipermeable membrane,
The method for removing harmful heavy metals from a harmful heavy metal-containing absorption solution according to claim 1, wherein a surfactant is added to the absorption solution on the negative electrode installation side.
JP9092861A 1997-03-28 1997-03-28 Method for removing harmful heavy metal from liquid absorbent containing harmful heavy metal Pending JPH10273793A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9092861A JPH10273793A (en) 1997-03-28 1997-03-28 Method for removing harmful heavy metal from liquid absorbent containing harmful heavy metal

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9092861A JPH10273793A (en) 1997-03-28 1997-03-28 Method for removing harmful heavy metal from liquid absorbent containing harmful heavy metal

Publications (1)

Publication Number Publication Date
JPH10273793A true JPH10273793A (en) 1998-10-13

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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001087411A (en) * 1999-09-24 2001-04-03 Nishimatsu Constr Co Ltd Dioxins decontaminating method and dioxins treatment device
KR100433801B1 (en) * 2002-01-18 2004-06-04 학교법인 고운학원 Electrolytic decontamination of toxic materials and the apparatus
JP2006097128A (en) * 2004-09-06 2006-04-13 Nippon Mining & Metals Co Ltd Method for producing sheet-form electrolytic copper
JP2008530367A (en) * 2005-02-15 2008-08-07 ビーエーエスエフ ソシエタス・ヨーロピア Use of nonionic surfactants in obtaining metals by electrolysis
US8877148B2 (en) 2009-07-24 2014-11-04 Graham Dickson Apparatus and method for removing mercury from a gas

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001087411A (en) * 1999-09-24 2001-04-03 Nishimatsu Constr Co Ltd Dioxins decontaminating method and dioxins treatment device
JP4550188B2 (en) * 1999-09-24 2010-09-22 西松建設株式会社 Dioxin decontamination method and dioxin treatment apparatus
KR100433801B1 (en) * 2002-01-18 2004-06-04 학교법인 고운학원 Electrolytic decontamination of toxic materials and the apparatus
JP2006097128A (en) * 2004-09-06 2006-04-13 Nippon Mining & Metals Co Ltd Method for producing sheet-form electrolytic copper
JP2008530367A (en) * 2005-02-15 2008-08-07 ビーエーエスエフ ソシエタス・ヨーロピア Use of nonionic surfactants in obtaining metals by electrolysis
US8877148B2 (en) 2009-07-24 2014-11-04 Graham Dickson Apparatus and method for removing mercury from a gas

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