JP2000212654A - Recovery of heavy metal from substance containing heavy metal and chlorine - Google Patents

Recovery of heavy metal from substance containing heavy metal and chlorine

Info

Publication number
JP2000212654A
JP2000212654A JP1033099A JP1033099A JP2000212654A JP 2000212654 A JP2000212654 A JP 2000212654A JP 1033099 A JP1033099 A JP 1033099A JP 1033099 A JP1033099 A JP 1033099A JP 2000212654 A JP2000212654 A JP 2000212654A
Authority
JP
Japan
Prior art keywords
heavy metal
chlorine
fly ash
slurry
substance
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
JP1033099A
Other languages
Japanese (ja)
Inventor
Masahisa Miyazaki
正久 宮崎
Takashi Kurokawa
隆史 黒川
Toshiaki Tokumitsu
俊章 徳光
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.)
Dowa Holdings Co Ltd
Original Assignee
Dowa Mining Co Ltd
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 Dowa Mining Co Ltd filed Critical Dowa Mining Co Ltd
Priority to JP1033099A priority Critical patent/JP2000212654A/en
Publication of JP2000212654A publication Critical patent/JP2000212654A/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 provide a method for recovering heavy metal contents from a substance containing copper, lead, zinc and other heavy metal contents, and chlorine in which the heavy metal is directly separated and recovered from chlorine in an initial stage of processing the heavy metal, by reducing chlorine to a degree that the heavy metal can be introduced in a refining process as it is. SOLUTION: After a substance containing the heavy metal such as fly ash and chlorine is changed into a slurry with water, the pH value is regulated to be 12 or over to separate the solid from the liquid, and a sediment containing the heavy metal in which chlorine is remarkably reduced is recovered. The substance containing the heavy metal such as fly ash and chlorine is changed into a slurry, and its pH value is regulated to be 5 or under, and again regulated to be at least 12 with an alkaline agent to separate the solid from the liquid, and the sediment containing the heavy metal with less chlorine is recovered.

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、重金属成分と塩素
とを含む物質の処理すべてに適用でき、特に、都市ゴミ
焼却施設や産業廃棄物焼却場等における焼却炉や溶融炉
あるいは汚泥を処理するセメントキルン等から発生する
重金属含有飛灰からの重金属の回収に好適な処理方法に
関する。
The present invention is applicable to all treatments of substances containing heavy metal components and chlorine, and in particular, treats incinerators, melting furnaces, or sludge in municipal waste incineration facilities, industrial waste incineration plants, and the like. The present invention relates to a treatment method suitable for recovering heavy metals from heavy metal-containing fly ash generated from a cement kiln or the like.

【0002】[0002]

【従来の技術】一般事業所や一般家庭から排出されるゴ
ミ(「都市ゴミ」または「一般廃棄物」と称されてい
る)は都市ゴミ焼却施設や産業廃棄物焼却工場等に集め
られて焼却処分されており、その際に焼却炉から発生す
る焼却灰や飛灰は薬剤処理、または溶融炉、セメントキ
ルン処理等の中間処理が施された後、最終処分場に堆積
されている。
2. Description of the Related Art Garbage (called "municipal waste" or "general waste") discharged from general offices and households is collected and incinerated at municipal waste incineration facilities and industrial waste incineration plants. The incineration ash and fly ash generated from the incinerator at that time are deposited at the final disposal site after being subjected to chemical treatment or intermediate treatment such as melting furnace and cement kiln treatment.

【0003】しかし、上記溶融炉やセメントキルン等で
の中間処理においては、蒸気圧の高い鉛、亜鉛およびカ
ドミウム等の重金属は炉内で揮発して排ガスに入り、こ
の排ガスに入った重金属は排ガス処理設備のなかで凝縮
して再び飛灰となっていた。すなわち、この再度の飛灰
中には、上記のように鉛、銅、亜鉛、カドミウム等の有
用な重金属の他、多量の塩素が含まれており、これらの
飛灰から有用な重金属を回収する方法が求められてい
た。
However, in the above-mentioned intermediate treatment in a melting furnace or a cement kiln, heavy metals such as lead, zinc and cadmium having a high vapor pressure volatilize in the furnace and enter the exhaust gas. It was condensed in the processing equipment and became fly ash again. That is, in the fly ash again, lead, copper, zinc, in addition to useful heavy metals such as cadmium as described above, contains a large amount of chlorine, and recovers useful heavy metals from these fly ash A way was sought.

【0004】このような飛灰について、特開平7−10
9533号公報には、飛灰を槽内の水に懸濁し、この懸
濁液を酸またはアルカリの添加によりアルカリ域の適当
値にpH調整することによって飛灰中の重金属を水酸化
物として沈殿させ、その澱物を回収する方法について開
示している。また本出願人も、先に、湿式処理方式によ
って対処する方法を出願しており(特開平8−1177
24号公報および特開平8−141539号公報)、こ
のような湿式処理方法により、飛灰に含まれている銅等
有用重金属を安定な形で分離し、重金属資源として有効
に回収できるようになった。
[0004] Such fly ash is disclosed in
No. 9533 discloses that fly ash is suspended in water in a tank, and the suspension is subjected to pH adjustment to an appropriate value in an alkaline region by adding an acid or alkali to precipitate heavy metals in the fly ash as hydroxide. And a method for recovering the precipitate is disclosed. The present applicant has also previously filed a method for coping with the wet processing method (Japanese Unexamined Patent Application Publication No. H8-1177).
No. 24 and Japanese Unexamined Patent Publication No. Hei 8-141539), such a wet treatment method allows useful heavy metals such as copper contained in fly ash to be separated in a stable form and to be effectively recovered as heavy metal resources. Was.

【0005】すなわち、特開平8−117724号公報
には、飛灰を水でスラリー化し、pH調整して浸出し、
固液分離する第1工程と、該第1工程からの殿物をリパ
ルプし、鉱酸により浸出溶解した後、固液分離して鉛産
物を得る第2工程と、前記第1工程と前記第2工程から
の酸性濾液に中和剤またさらに水硫化ソーダを加えて亜
鉛、銅を含む産物を濾別し、濾過水を排水液とする第3
工程からなる方法が開示されており、また、特開平8−
141539号公報には、飛灰を水と中和剤で中和して
固液分離する第1工程と、該第1工程からの澱物をリパ
ルプし、硫酸により浸出溶解して後、固液分離して鉛産
物を得る第2工程と、該第2工程からの濾液に中和剤を
加えて亜鉛、銅を含む産物を濾別する第3工程と、該第
3工程の濾過水を該第1工程の中和液として繰り返し、
該第1工程からの濾液について硫化剤を添加して排液処
理する方法が開示されている。
[0005] That is, JP-A-8-117724 discloses that fly ash is slurried with water, adjusted for pH, and leached.
A first step of solid-liquid separation, a second step of repulping the residue from the first step, leaching and dissolving with a mineral acid, and then performing a solid-liquid separation to obtain a lead product; the first step and the second step; A neutralizing agent or further sodium bisulfide is added to the acidic filtrate from the two steps, and a product containing zinc and copper is separated by filtration.
A method comprising steps is disclosed.
Japanese Patent No. 141539 discloses a first step in which fly ash is neutralized with water and a neutralizing agent to perform solid-liquid separation, and the precipitate from the first step is repulped, leached and dissolved with sulfuric acid, and then solid-liquid separated. A second step of separating to obtain a lead product, a third step of adding a neutralizing agent to the filtrate from the second step to filter out a product containing zinc and copper, and filtering the filtered water of the third step. Repeated as a neutralization solution in the first step,
A method is disclosed in which a sulphating agent is added to the filtrate from the first step for drainage treatment.

【0006】[0006]

【発明が解決しようとする課題】しかしながら、重金属
の製錬工程では原料中の塩素が障害となるので、上記の
各方法においては、スラリー化させた飛灰について、酸
浸出、アルカリ中和、固液分離からなる溶解・分離処理
の操作を繰り返して、塩素の少ない鉛残渣、亜鉛澱物等
個別の金属残渣を得てはいるものの、飛灰の処理方法と
しては必ずしも効率的な手段とは言えない面もあった。
すなわち、スラリー化させた飛灰から単一の溶解・分離
処理のみで直接的に得られる複合的な重金属澱物につい
ては、塩素を多量に含んでおり、そのままでは製錬工程
への導入が困難であるという問題が残されていた。
However, in the smelting process of heavy metals, chlorine in the raw material becomes an obstacle. Therefore, in each of the above methods, fly ash slurried is subjected to acid leaching, alkali neutralization and solidification. Although the operation of dissolution / separation treatment consisting of liquid separation is repeated to obtain individual metal residues such as lead residues and zinc deposits with low chlorine, it can be said that this is not necessarily an efficient means of treating fly ash. There were no aspects.
That is, complex heavy metal deposits obtained directly from slurry fly ash by only a single dissolution / separation treatment contain a large amount of chlorine and are difficult to introduce into the smelting process as it is. The problem that was left.

【0007】本発明は、このような状況に鑑み、有用重
金属と共に塩素を含む飛灰等の物質から初期段階におい
て直接的に塩素を分離し、製錬工程において再利用可能
な形で低塩素の重金属澱物を回収できる重金属と塩素を
含有する物質からの重金属回収方法の提供を目的とす
る。
[0007] In view of such circumstances, the present invention separates chlorine directly from substances such as fly ash containing chlorine together with useful heavy metals in the initial stage, and reduces the chlorine in a form that can be reused in the smelting process. An object of the present invention is to provide a method for recovering heavy metals from a substance containing heavy metals and chlorine, which can recover heavy metal deposits.

【0008】[0008]

【課題を解決するための手段】上記の目的を達成するた
め、本発明は、第1に亜鉛、銅、鉛のうちの少なくとも
一種の重金属成分と塩素とを含む物質から該重金属成分
を回収する方法において、前記物質に水を加えてスラリ
ー化し、アルカリ剤を用いてpHを12以上に調整した
後、固液分離することにより重金属含有澱物を塩素含有
濾液から分離して回収することを特徴とする重金属と塩
素を含有する物質からの重金属の回収方法;第2に、亜
鉛、銅、鉛のうちの少なくとも一種の重金属成分と塩素
とを含む物質から該重金属成分を回収する方法におい
て、前記物質に鉱酸を加えてスラリー化し、pHを5以
下に調整して塩素を溶解させる塩素溶解工程と、該塩素
溶解工程のスラリーにアルカリ剤を添加してpHを12
以上に調整した後、固液分離することにより、重金属含
有澱物を塩素含有濾液から分離して回収する重金属含有
澱物の回収工程とからなることを特徴とする重金属と塩
素を含有する物質からの重金属の回収方法を提供する。
In order to achieve the above object, the present invention firstly recovers a heavy metal component from a substance containing at least one heavy metal component of zinc, copper and lead and chlorine. The method is characterized in that water is added to the substance to form a slurry, the pH is adjusted to 12 or more using an alkaline agent, and then the heavy metal-containing precipitate is separated from the chlorine-containing filtrate by solid-liquid separation and collected. A method for recovering heavy metals from a substance containing chlorine and heavy metal components of at least one of zinc, copper and lead; and A chlorine dissolving step of dissolving chlorine by adjusting the pH to 5 or less by adding a mineral acid to the substance, and adding an alkaline agent to the slurry in the chlorine dissolving step to adjust the pH to 12
After the above adjustment, by performing solid-liquid separation, the heavy metal-containing precipitate is separated from the chlorine-containing filtrate and collected. And a method for recovering heavy metals.

【0009】[0009]

【発明の実施の形態】本発明を、産業廃棄物を対象とす
る焼却炉からの飛灰の処理方法の場合を例に図1の処理
工程図によって説明する。まず、飛灰を水と混合してス
ラリー化させ、このスラリーを攪拌しながら、水酸化ナ
トリウム等のアルカリ剤を添加してpHを12以上に調
整した後、重金属を含有する澱物と塩化物態の塩素を含
有する濾液とに分離する。このように、飛灰等の塩素含
有物質からのスラリーのpHを12以上にすることによ
って重金属含有澱物と塩素との分離が極めてよくなり、
重金属含有澱物中の塩素をpH11の場合の塩素値の半
分以下にまで低減させることができる。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described with reference to the process diagram of FIG. 1 by taking as an example a method of treating fly ash from an incinerator for industrial waste. First, fly ash is mixed with water to form a slurry, and while the slurry is being stirred, an alkaline agent such as sodium hydroxide is added to adjust the pH to 12 or more, and then the heavy metal-containing precipitate and chloride are added. And a filtrate containing chlorine. As described above, by setting the pH of the slurry from a chlorine-containing substance such as fly ash to 12 or more, separation of heavy metal-containing precipitates and chlorine becomes extremely good,
The chlorine in the heavy metal-containing precipitate can be reduced to less than half of the chlorine value at pH 11.

【0010】また、図2の処理工程図のように、飛灰を
水と混合してスラリー化させ、このスラリーを攪拌しな
がら、塩酸または硫酸等の鉱酸を用いてpHを5以下、
好ましくは、pHを4以下に調整して塩素をナトリウ
ム、カルシウムの塩化物態で液中に溶解させる(塩素溶
解工程)。次いで、水酸化ナトリウム等のアルカリ中和
剤を添加してpH12以上に調整することにより重金属
は澱物化するので、固液分離することによって重金属を
含有する澱物と、塩素、ナトリウム、カルシウム等塩類
を含有する濾液とに分離させることができる(重金属含
有殿物回収工程)。なお、上記スラリーのpHは、飛灰
の組成によって異なるため、上記の塩素溶解工程におけ
る鉱酸の添加量は飛灰に応じて調整する。したがって、
上記スラリーのpHがすでに最適pHにある場合には、
鉱酸を加える必要はない。
Further, as shown in the treatment process diagram of FIG. 2, fly ash is mixed with water to form a slurry, and while the slurry is being stirred, the pH is adjusted to 5 or less using a mineral acid such as hydrochloric acid or sulfuric acid.
Preferably, the pH is adjusted to 4 or less to dissolve chlorine in the liquid in the form of chlorides of sodium and calcium (chlorine dissolving step). Then, the heavy metal is converted into a precipitate by adding an alkali neutralizing agent such as sodium hydroxide to adjust the pH to 12 or more. Therefore, the heavy metal-containing precipitate is subjected to solid-liquid separation, and a salt such as chlorine, sodium, calcium or the like is removed. (Heavy metal-containing residue collection step). Since the pH of the slurry varies depending on the composition of the fly ash, the amount of the mineral acid added in the chlorine dissolving step is adjusted according to the fly ash. Therefore,
If the pH of the slurry is already at the optimum pH,
There is no need to add mineral acids.

【0011】以上のように、塩素溶解工程で飛灰等の塩
素含有物質中の塩化物態塩素を酸性域において十分に溶
出させた後、重金属含有澱物回収工程でこの酸性の溶出
液を強アルカリ域に調整することにより、重金属含有澱
物の塩素含有率をさらに著しく減少させることができ
る。この塩素含有率の低い重金属含有澱物は、そのまま
製錬工程の原料とすることが可能である。
As described above, after the chloride chlorine in the chlorine-containing substance such as fly ash is sufficiently eluted in the acidic region in the chlorine dissolving step, the acidic eluate is strongly concentrated in the heavy metal-containing precipitate recovery step. By adjusting to an alkaline range, the chlorine content of the heavy metal-containing precipitate can be further significantly reduced. The heavy metal-containing deposit having a low chlorine content can be directly used as a raw material in a smelting process.

【0012】また、さらに塩素含有率を低減させたい場
合においては、上記重金属含有澱物回収工程で得られた
低塩素の重金属含有澱物にさらに塩酸または硫酸等の鉱
酸を添加して再度pHを5以下に調整した後、水酸化ナ
トリウム等のアルカリ剤を添加してpHを6以上に調整
することによって極度に塩素含有率が低減した重金属含
有澱物を得ることができる。
When it is desired to further reduce the chlorine content, a mineral acid such as hydrochloric acid or sulfuric acid is further added to the low-chlorine heavy metal-containing precipitate obtained in the above-mentioned heavy metal-containing precipitate recovery step, and the pH is reduced again. Is adjusted to 5 or less, and by adding an alkali agent such as sodium hydroxide to adjust the pH to 6 or more, a heavy metal-containing precipitate with extremely reduced chlorine content can be obtained.

【0013】[0013]

【実施例】[実施例1](試験番号1) まず、10リットルビーカーに純水6リットルを入れて
攪拌しながら、原料としてA処理工場の飛灰600gを
入れてスラリーとし、10分間攪拌しながら、アルカリ
剤として200g/リットルの水酸化ナトリウム溶液で
pHを13に調整し、30分間維持した後、濾過操作に
より重金属含有澱物と濾液とを分離した。得られた重金
属含有澱物全量を水2リットルで5分間リパルプ洗浄し
た後、濾過操作により重金属澱物を得た。この重金属含
有澱物中のCl,Cu,Pb,Zn含有率を測定し、そ
の結果を試験番号1として、原料飛灰の組成と共に、表
1に示した。
[Example 1] (Test No. 1) First, 6 g of pure water was placed in a 10-liter beaker and stirred, and 600 g of fly ash from the A treatment plant was added as a raw material to form a slurry and stirred for 10 minutes. Meanwhile, the pH was adjusted to 13 with a 200 g / liter sodium hydroxide solution as an alkaline agent, and the mixture was maintained for 30 minutes. Then, the heavy metal-containing precipitate and the filtrate were separated by a filtration operation. After the whole amount of the obtained heavy metal-containing precipitate was washed with 2 liters of water for 5 minutes by repulping, a heavy metal precipitate was obtained by a filtration operation. The Cl, Cu, Pb, and Zn contents in the heavy metal-containing precipitate were measured, and the results are shown in Table 1 along with the composition of the raw material fly ash as Test No. 1.

【0014】[実施例2](試験番号2) 実施例1と同様に、10リットルビーカーに純水6リッ
トルを入れて攪拌しながら、A処理工場の上記飛灰60
0gを入れてスラリーとし、10分間攪拌しながら、鉱
酸として36%塩酸を添加してpHを4に調整して維持
し、30分間溶解処理を行ない(塩素溶解工程)、次い
で、アルカリ中和剤として200g/リットルの水酸化
ナトリウム溶液を添加してpHを13に調整し30分間
維持した後、濾過操作により重金属含有澱物と塩素を主
として含有する濾液とに分離した(重金属含有澱物回収
工程)。得られた重金属含有澱物全量を水2リットルで
5分間リパルプ洗浄した後、濾過操作により重金属含有
澱物を得た。この重金属含有澱物中のCl,Cu,P
b,Zn含有率を測定し、その結果を試験番号2として
表1に示した。
[Example 2] (Test No. 2) As in Example 1, 6 liters of pure water was placed in a 10 liter beaker and stirred, and the fly ash 60 of the A treatment plant was stirred.
0 g was added to form a slurry, and while stirring for 10 minutes, 36% hydrochloric acid was added as a mineral acid to adjust and maintain the pH at 4, and a dissolution treatment was performed for 30 minutes (chlorine dissolution step), followed by alkali neutralization. After adding 200 g / l of sodium hydroxide solution as an agent to adjust the pH to 13 and maintaining it for 30 minutes, it was separated by filtration into a heavy metal-containing precipitate and a filtrate mainly containing chlorine (recovery of heavy metal-containing precipitate). Process). After the entire amount of the obtained heavy metal-containing precipitate was repulped and washed with 2 liters of water for 5 minutes, a heavy metal-containing precipitate was obtained by a filtration operation. Cl, Cu, P in this heavy metal-containing precipitate
The b and Zn contents were measured, and the results are shown in Table 1 as Test No. 2.

【0015】[実施例3](試験番号3) 上記スラリーの溶解処理において、鉱酸として98wt%
硫酸を同量の水で稀釈した硫酸液を用いた以外は実施例
2と同操作により回収処理を行なった。得られた重金属
含有澱物中のCl,Cu,Pb,Znの含有率の測定結
果を試験番号3として表1に示した。
Example 3 (Test No. 3) In the dissolution treatment of the slurry, 98 wt% as mineral acid
A recovery treatment was performed in the same manner as in Example 2 except that a sulfuric acid solution obtained by diluting sulfuric acid with the same amount of water was used. Table 1 shows the measurement results of the contents of Cl, Cu, Pb, and Zn in the obtained heavy metal-containing precipitate as Test No. 3.

【0016】[実施例4](試験番号4) 実施例3と同操作を行ない、得られた低塩素の重金属含
有澱物について、さらに水2リットルでリパルプし、再
度98wt%硫酸を同量の水で稀釈した硫酸液でpHを4
に調整して維持し、10分間溶解処理を行ない、次い
で、アルカリ中和剤として200g/リットルの水酸化
ナトリウム溶液を添加してpHを9に調整して30分間
維持した後、濾過操作により重金属を主とする重金属含
有澱物と塩素を主として含有する濾液とに分離した。得
られた重金属含有澱物全量を水2リットルで5分間リパ
ルプ洗浄した後、濾過操作により重金属含有澱物を得
た。この重金属含有澱物中のCl,Cu,Pb,Znの
含有率を測定し、その結果を試験番号4として表1に示
した。
Example 4 (Test No. 4) The same operation as in Example 3 was carried out, and the obtained low-chlorine heavy metal-containing precipitate was further repulped with 2 liters of water, and 98 wt% sulfuric acid was again used in the same amount with 98 wt% sulfuric acid. PH 4 with sulfuric acid diluted with water
After adjusting the pH to 9 and performing a dissolution treatment for 10 minutes, adding a 200 g / L sodium hydroxide solution as an alkali neutralizer to adjust the pH to 9 and maintaining the mixture for 30 minutes, the heavy metals are filtered out. And a filtrate mainly containing heavy metal and a filtrate mainly containing chlorine. After the entire amount of the obtained heavy metal-containing precipitate was repulped and washed with 2 liters of water for 5 minutes, a heavy metal-containing precipitate was obtained by a filtration operation. The contents of Cl, Cu, Pb, and Zn in the heavy metal-containing precipitate were measured, and the results are shown in Table 1 as Test No. 4.

【0017】[0017]

【表1】 [Table 1]

【0018】表1からわかるように、本発明によれば、
飛灰スラリーをpH13に調整・維持することにより、
銅、鉛等の重金属が澱物中に濃縮的に回収されると共
に、澱物中の塩素は著しく低減することがわかる。特
に、スラリーを酸溶解した後、pH13のアルカリ域に
維持することにより、大幅に低減することがわかる。ま
た、鉱酸としては、塩酸より硫酸の方が塩素の低減には
より効果的である。さらに、処理済の重金属含有澱物に
ついて、再び酸溶解とアルカリ域維持を繰り返すことに
より、塩素は激減した。
As can be seen from Table 1, according to the present invention,
By adjusting and maintaining the fly ash slurry to pH 13,
It is understood that heavy metals such as copper and lead are concentrated and recovered in the precipitate, and chlorine in the precipitate is significantly reduced. In particular, it can be seen that, by dissolving the slurry in acid and maintaining it in an alkaline region of pH 13, it is significantly reduced. As a mineral acid, sulfuric acid is more effective in reducing chlorine than hydrochloric acid. Furthermore, chlorine was drastically reduced by repeating the dissolution of acid and the maintenance of the alkaline region again for the treated heavy metal-containing precipitate.

【0019】[比較例1](試験番号5) 10リットルビーカーに純水6リットリを入れて攪拌し
ながら、原料として実施例の場合と同じA処理工場の飛
灰600gを入れてスラリーとし、10分間攪拌しなが
ら、アルカリ剤として200g/リットルの水酸化ナト
リウム溶液でpHを7に調整し、30分間維持した後、
濾過操作により重金属含有澱物と濾液とを分離した。
(この比較例1における処理は、アルカリ剤による調整
pHを7とした以外は、実施例1と同様である)得られ
た重金属含有澱物中のCl含有率を測定し、その結果を
試験番号5として表2に示した。
[Comparative Example 1] (Test No. 5) 6 g of pure water was placed in a 10 liter beaker and stirred, and 600 g of fly ash from the A treatment plant as in the embodiment was added as a raw material to form a slurry. The pH was adjusted to 7 with a 200 g / liter sodium hydroxide solution as an alkaline agent while stirring for 30 minutes, and after maintaining for 30 minutes,
The heavy metal-containing precipitate and the filtrate were separated by a filtration operation.
(The treatment in Comparative Example 1 was the same as in Example 1 except that the pH adjusted with an alkaline agent was adjusted to 7.) The Cl content in the obtained heavy metal-containing precipitate was measured, and the results were used as test numbers. 5 is shown in Table 2.

【0020】[比較例2](試験番号6) 上記スラリーに対するアルカリ剤の添加量を調整してp
Hを9とした以外は、比較例1と同操作による処理を行
なった。得られた重金属含有澱物中のCl含有率を測定
し、その結果を試験番号6として表2に示した。
[Comparative Example 2] (Test No. 6)
The same operation as in Comparative Example 1 was performed except that H was set to 9. The Cl content in the obtained heavy metal-containing precipitate was measured, and the results are shown in Table 2 as Test No. 6.

【0021】[比較例3](試験番号7) 上記スラリーに対するアルカリ剤の添加量を調整してp
Hを11とした以外は、比較例1と同操作による処理を
行なった。得られた重金属含有澱物中のCl含有率を測
定し、その結果を試験番号7として表2に示した。
[Comparative Example 3] (Test No. 7)
The same operation as in Comparative Example 1 was performed except that H was set to 11. The Cl content in the obtained heavy metal-containing precipitate was measured, and the results are shown in Table 2 as Test No. 7.

【0022】[0022]

【表2】 [Table 2]

【0023】飛灰のスラリーのpHを本発明の範囲外に
調整した以外は、実施例1の場合と同様の操作により飛
灰を処理した比較例の場合、前記表1の試験番号1の数
値に比較して明らかなように、重金属含有澱物中には、
なお多くの量の塩素が残留しているのがわかる。
In the case of the comparative example in which the fly ash was treated by the same operation as in Example 1 except that the pH of the fly ash slurry was adjusted to be outside the range of the present invention, the numerical value of Test No. 1 in Table 1 was used. As is apparent from comparison with the above, in the heavy metal-containing precipitate,
It can be seen that a large amount of chlorine remains.

【0024】[0024]

【発明の効果】飛灰等の重金属と塩素を含有する物質の
スラリーをpH12以上に調整して重金属澱物を分離す
る本発明によれば、飛灰等の重金属と塩素を含有する物
質に含まれている銅、鉛、亜鉛等重金属を、処理の初期
段階で直接的に、安定した形で濃縮的に、かつ、そのま
ま製錬工程に導入可能な程度までに塩素含有量を低減し
た状態で回収できる飛灰等の重金属と塩素を含有する物
質からの重金属回収方法を提供できるという効果を奏す
る。上記スラリーを鉱酸溶解工程を経てpH12以上に
調整する本発明によれば、さらに重金属澱物の塩素をさ
らに顕著に低減できる飛灰等の重金属と塩素を含有する
物質からの重金属回収方法を提供できるという効果を奏
する。
According to the present invention, a slurry of a substance containing a heavy metal and chlorine such as fly ash is adjusted to pH 12 or more to separate heavy metal deposits. According to the present invention, the slurry is included in a substance containing a heavy metal such as fly ash and chlorine. Heavy metals such as copper, lead, zinc, etc. directly in the initial stage of treatment, in a stable and concentrated manner, and with a reduced chlorine content to such an extent that it can be directly introduced into the smelting process. An effect is provided that a method for recovering heavy metals from substances containing chlorine and heavy metals such as fly ash that can be recovered can be provided. According to the present invention, in which the slurry is adjusted to a pH of 12 or more through a mineral acid dissolving step, a method for recovering heavy metals from substances containing chlorine and heavy metals such as fly ash, which can further remarkably reduce chlorine in heavy metal deposits, is provided. It has the effect of being able to.

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

【図1】本発明の重金属回収方法の実施例を示す工程図
である。
FIG. 1 is a process chart showing an embodiment of a heavy metal recovery method of the present invention.

【図2】本発明の重金属回収方法の別の実施例を示す工
程図である。
FIG. 2 is a process chart showing another embodiment of the heavy metal recovery method of the present invention.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C22B 13/00 C22B 3/00 Q 15/00 13/04 19/20 15/12 (72)発明者 徳光 俊章 東京都千代田区丸の内一丁目8番2号 同 和鉱業株式会社内 Fターム(参考) 4D004 AA37 AB06 AC04 BA05 CA13 CA34 CA35 CC12 DA03 DA20 4K001 AA09 AA20 AA30 BA08 BA14 CA02 DB02 DB07 DB23 ──────────────────────────────────────────────────の Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) C22B 13/00 C22B 3/00 Q 15/00 13/04 19/20 15/12 (72) Inventor Tokumitsu Shunsho 1-8-2 Marunouchi, Chiyoda-ku, Tokyo F-term in Dowa Mining Co., Ltd. (reference) 4D004 AA37 AB06 AC04 BA05 CA13 CA34 CA35 CC12 DA03 DA20 4K001 AA09 AA20 AA30 BA08 BA14 CA02 DB02 DB07 DB23

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 亜鉛、銅、鉛のうちの少なくとも一種の
重金属成分と塩素とを含む物質から上記重金属成分を回
収する方法において、前記物質に水を加えてスラリー化
し、アルカリ剤を用いてpHを12以上に調整した後、
固液分離することにより重金属含有澱物を塩素含有濾液
から分離して回収することを特徴とする重金属と塩素を
含有する物質からの重金属の回収方法。
1. A method for recovering a heavy metal component from a substance containing at least one heavy metal component of zinc, copper and lead and chlorine, wherein said substance is slurried by adding water, and the pH is adjusted using an alkaline agent. After adjusting to 12 or more,
A method for recovering heavy metals from substances containing heavy metals and chlorine, wherein the heavy metal-containing precipitates are separated from the chlorine-containing filtrate by solid-liquid separation and recovered.
【請求項2】 亜鉛、銅、鉛のうちの少なくとも一種の
重金属成分と塩素とを含む物質から上記重金属成分を回
収する方法において、前記物質に鉱酸を加えてスラリー
化し、pHを5以下に調整して塩素を溶解させる塩素溶
解工程と、該塩素溶解工程のスラリーにアルカリ剤を添
加してpHを12以上に調整した後、固液分離すること
により重金属含有澱物を塩素含有濾液から分離して回収
する重金属含有澱物回収工程とからなることを特徴とす
る重金属と塩素を含有する物質からの重金属の回収方
法。
2. A method for recovering a heavy metal component from a substance containing at least one heavy metal component of zinc, copper and lead and chlorine, wherein said substance is slurried by adding a mineral acid to adjust the pH to 5 or less. A chlorine dissolving step of adjusting and dissolving chlorine, and after adding an alkali agent to the slurry in the chlorine dissolving step to adjust the pH to 12 or more, separating heavy metal-containing precipitates from the chlorine-containing filtrate by solid-liquid separation. And recovering the heavy metal from the substance containing heavy metal and chlorine.
JP1033099A 1999-01-19 1999-01-19 Recovery of heavy metal from substance containing heavy metal and chlorine Pending JP2000212654A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
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Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP1033099A JP2000212654A (en) 1999-01-19 1999-01-19 Recovery of heavy metal from substance containing heavy metal and chlorine

Publications (1)

Publication Number Publication Date
JP2000212654A true JP2000212654A (en) 2000-08-02

Family

ID=11747205

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP2000212654A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005246226A (en) * 2004-03-03 2005-09-15 Dowa Mining Co Ltd Treating method for fly ash
JP2007253029A (en) * 2006-03-22 2007-10-04 Kyoei Bussan Kk Incineration residue treatment method and incineration residue treated matter
JP2013014789A (en) * 2011-06-30 2013-01-24 Mitsubishi Materials Corp Method for treating flue cinder
KR20150105982A (en) 2013-03-22 2015-09-18 닛폰 스틸 앤드 스미킨 스테인레스 스틸 코포레이션 Dust cleaning device and dust cleaning method
WO2018148870A1 (en) * 2017-02-14 2018-08-23 深圳市能源环保有限公司 In-line heavy metal detection and solid waste dehazardization method

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005246226A (en) * 2004-03-03 2005-09-15 Dowa Mining Co Ltd Treating method for fly ash
JP2007253029A (en) * 2006-03-22 2007-10-04 Kyoei Bussan Kk Incineration residue treatment method and incineration residue treated matter
JP2013014789A (en) * 2011-06-30 2013-01-24 Mitsubishi Materials Corp Method for treating flue cinder
KR20150105982A (en) 2013-03-22 2015-09-18 닛폰 스틸 앤드 스미킨 스테인레스 스틸 코포레이션 Dust cleaning device and dust cleaning method
WO2018148870A1 (en) * 2017-02-14 2018-08-23 深圳市能源环保有限公司 In-line heavy metal detection and solid waste dehazardization method

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