JP2580610B2 - Treatment method for water containing iron cyanide complex - Google Patents

Treatment method for water containing iron cyanide complex

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Publication number
JP2580610B2
JP2580610B2 JP62187252A JP18725287A JP2580610B2 JP 2580610 B2 JP2580610 B2 JP 2580610B2 JP 62187252 A JP62187252 A JP 62187252A JP 18725287 A JP18725287 A JP 18725287A JP 2580610 B2 JP2580610 B2 JP 2580610B2
Authority
JP
Japan
Prior art keywords
salt
cyanide complex
ferrous
iron cyanide
copper
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Lifetime
Application number
JP62187252A
Other languages
Japanese (ja)
Other versions
JPS6430693A (en
Inventor
勇 加藤
章 小田島
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.)
KURITA KOGYO KK
NIPPON DENKI KANKYO ENJINIARINGU KK
Original Assignee
KURITA KOGYO KK
NIPPON DENKI KANKYO ENJINIARINGU KK
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 KURITA KOGYO KK, NIPPON DENKI KANKYO ENJINIARINGU KK filed Critical KURITA KOGYO KK
Priority to JP62187252A priority Critical patent/JP2580610B2/en
Publication of JPS6430693A publication Critical patent/JPS6430693A/en
Application granted granted Critical
Publication of JP2580610B2 publication Critical patent/JP2580610B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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Description

【発明の詳細な説明】 〔産業上の利用分野〕 この発明は鉄シアン錯体を含有する水の処理方法、特
に鉄シアン錯体と共存する重金属とを同時に除去できる
鉄シアン錯体含有水の処理方法に関するものである。
Description: TECHNICAL FIELD The present invention relates to a method for treating water containing an iron cyanide complex, and more particularly to a method for treating water containing an iron cyanide complex that can simultaneously remove heavy metals coexisting with the iron cyanide complex. Things.

〔従来の技術〕[Conventional technology]

フェロシアンイオン、フェリシアンイオンなどの鉄シ
アン錯体含有水を処理する方法として、第一鉄塩を添加
して鉄シアン錯体と反応させる紺青法が知られている。
この方法では、弱酸性(pH4〜6)で難溶性の鉄シアン
錯塩を沈殿させ、その後高アルカリ(pH9〜12)で過剰
の第一鉄塩および共存重金属を水酸化物として沈殿させ
る。
As a method for treating water containing an iron cyanide complex such as a ferrocyanide ion or a ferricyan ion, a navy blue method in which a ferrous salt is added to react with water is known.
In this method, a weakly acidic (pH 4 to 6) and hardly soluble iron cyanide complex is precipitated, and then a high alkali (pH 9 to 12) is used to precipitate excess ferrous salt and coexisting heavy metals as hydroxide.

また鉄シアン錯体含有水に第一鉄塩を加えた後アルカ
リを加えてpH7〜8にし、その後第二鉄塩を加えてpH6.5
〜7.3にしてシアン鉄化合物を沈殿分離する方法が知ら
れている(特公昭56−51835号)。この方法は鉄シアン
錯体含有水に第一鉄塩を添加して生成したターンブル青
がアルカリ添加によって一部溶解して生成するフェロシ
アンイオンを第二鉄塩で不活性のベルリン青とするもの
である。
Further, ferrous salt is added to the water containing iron cyanide complex, alkali is added to adjust the pH to 7 to 8, and then ferric salt is added to adjust the pH to 6.5.
A method is known in which the iron cyanide compound is separated by precipitation at a temperature of from 7.3 to 7.3 (JP-B-56-51835). This method turns ferrocyan ion, which is generated by adding a ferrous salt to water containing an iron cyanide complex and partially dissolving by adding an alkali to ferrocyanide ions, to be inactive Berlin blue with a ferric salt. is there.

〔発明が解決しようとする問題点〕[Problems to be solved by the invention]

しかし紺青法においては、難溶性鉄シアン錯体が生成
する領域は弱酸性であるため、鉄シアン錯体をpH4〜6
で沈殿させる第一工程と、過剰の第一鉄塩および共存重
金属をpH9〜12で沈殿させる第二工程の二段階処理が必
要である。
However, in the navy blue method, since the region where the hardly soluble iron cyanide complex is generated is weakly acidic, the iron cyanide complex is used at pH 4-6.
And a second step of precipitating excess ferrous salt and coexisting heavy metals at pH 9-12.

また特公昭56−51835号の方法においても、共存する
ニッケル、亜鉛などの重金属はpHが中性では水酸化物沈
殿とならないため、二段階処理が必要であった。
Also in the method of JP-B-56-51835, two-stage treatment was necessary because the coexisting heavy metals such as nickel and zinc do not form hydroxide precipitates when the pH is neutral.

この発明は上記問題点を解決するためのもので、鉄シ
アン錯体を高pH下で難溶性化し、これにより一段階の処
理で過剰の鉄、銅および共存重金属も同時に除去できる
鉄シアン錯体含有水の処理方法を提案することを目的と
する。
The present invention has been made to solve the above-mentioned problems. The iron-cyan complex-containing water, which makes the iron-cyan complex hardly soluble at a high pH, whereby excess iron, copper and coexisting heavy metals can be removed at the same time in a single-stage treatment. The purpose of the present invention is to propose a processing method.

〔問題点を解決するための手段〕[Means for solving the problem]

本発明は、鉄シアン錯体含有水に第一鉄塩と銅塩と
を、第一鉄塩および銅塩以外の還元剤の存在下に反応さ
せて、アルカリ性下に難溶性塩を生成させ、固液分離す
ることを特徴とする鉄シアン錯体含有水の処理方法であ
る。
In the present invention, a ferrous salt and a copper salt are reacted with water containing an iron cyanide complex in the presence of a reducing agent other than the ferrous salt and the copper salt to form a hardly soluble salt under alkaline conditions, This is a method for treating water containing iron cyanide complex, which is characterized by liquid separation.

本発明において処理の対象となる鉄シアン錯体含有水
は、フェロシアンイオン(Fe(CN)6 4-)、フェリシア
ンイオン(Fe(CN)6 3-)などの鉄シアン錯体を含む水
で、ニッケル、亜鉛などの他の重金属を含んでいてもよ
い。
Iron cyanide complex-containing water to be processed in the present invention, ferrocyanide ion (Fe (CN) 6 4-) , with water containing an iron cyanide complexes such as ferricyanide ion (Fe (CN) 6 3-) , Other heavy metals such as nickel and zinc may be included.

上記鉄シアン錯体に反応させる第一鉄塩としては塩化
第一鉄、硫酸第一鉄などが使用できる。また銅塩として
は水溶性の塩であればよく、1価の銅塩でも2価の銅塩
でもよいが、一般に1価の銅塩は難溶性で空気により容
易に酸化されるため工業的に入手することが困難であ
り、硫酸銅、塩化銅、硝酸銅などの2価の銅塩が利用可
能である。
As the ferrous salt to be reacted with the iron cyanide complex, ferrous chloride, ferrous sulfate and the like can be used. The copper salt may be any water-soluble salt, and may be a monovalent copper salt or a divalent copper salt. In general, monovalent copper salts are poorly soluble and are easily oxidized by air, so that they are industrially used. It is difficult to obtain, and divalent copper salts such as copper sulfate, copper chloride, and copper nitrate can be used.

処理方法は、鉄シアン錯体含有水に第一鉄塩および銅
塩を添加して、第一鉄塩および銅塩以外の還元剤の存在
下に反応させ、フェロシアンの難溶性塩を生成させる。
この場合鉄塩は第一鉄塩の状態で反応させる必要があ
り、反応の時点あるいはその後に第二鉄に酸化されると
難溶性塩が生成しにくくなる。従って反応時における空
気酸化は避けるのが望ましい。また鉄シアン錯体として
フェリシアンイオンが含まれていると、添加した第一鉄
塩がフェリシアンイオンをフェロシアンイオンに還元す
る際酸化されるので、還元剤を添加して還元を行う。還
元剤として第1鉄塩および銅塩を用いると汚泥量が増大
するので、亜硫酸塩、チオ硫酸塩など他の還元剤を同時
に添加して反応させることができる。
In the treatment method, a ferrous salt and a copper salt are added to water containing an iron cyanide complex, and the reaction is carried out in the presence of a reducing agent other than the ferrous salt and the copper salt, thereby producing a sparingly soluble ferrocyanide salt.
In this case, it is necessary to react the iron salt in the state of a ferrous salt, and if it is oxidized to ferric at the time of the reaction or thereafter, it becomes difficult to generate a sparingly soluble salt. Therefore, it is desirable to avoid air oxidation during the reaction. Further, when ferricyan ion is contained as the iron cyanide complex, the added ferrous salt is oxidized when reducing the ferricyan ion to ferrocyanide ion. Therefore, the reduction is performed by adding a reducing agent. If ferrous salts and copper salts are used as reducing agents, the amount of sludge increases, so that other reducing agents such as sulfites and thiosulfates can be simultaneously added and reacted.

鉄シアン錯体と反応させる第一鉄塩および銅塩の量
は、(Fe+Cu)/Fe(CN)=2以上(モル比)、Cu/Fe
=0.2〜2(モル比)であり、過剰に添加されても、後
に水酸化物として除去される。原水がフェリシアン化物
や塩素を含んでいたり、あるいは酸化性雰囲気の場合に
は第一鉄塩が酸化されるので、作業に第一鉄塩を添加し
たり、別の還元剤を添加するのが好ましい。第一鉄塩、
銅塩、還元剤等は原水中に含まれる場合には添加量を少
なくすることができる。
The amounts of the ferrous salt and the copper salt to be reacted with the iron cyanide complex are (Fe + Cu) / Fe (CN) 6 = 2 or more (molar ratio), Cu / Fe
= 0.2 to 2 (molar ratio), and even if added in excess, it is later removed as hydroxide. If the raw water contains ferricyanide or chlorine, or if it is in an oxidizing atmosphere, the ferrous salt will be oxidized, so adding ferrous salt to the work or adding another reducing agent is not an option. preferable. Ferrous salt,
When the copper salt, the reducing agent and the like are contained in the raw water, the amount of addition can be reduced.

鉄シアン錯体含有水は第一鉄塩、銅塩および還元剤を
添加し、撹拌して反応させると、次式により難溶性塩が
生成するものと推測される。
It is presumed that when the ferrous cyanide complex-containing water is added with a ferrous salt, a copper salt, and a reducing agent and reacted with stirring, a sparingly soluble salt is formed by the following formula.

ここで生成物がFexCuy〔Fe(CN)なる複塩の形
であるか、−Fe−O−Cu−または で表わされる複合核錯体と、Fe(CN)6 4-との反応物で
あるかは不明である。
Here, the product is in the form of a double salt of Fe x Cu y [Fe (CN) 6 ] z , or —Fe—O—Cu— or And compound nucleus complex represented in either a Fe (CN) 6 4- and reactants is not known.

上記の反応は酸性領域からpH11までの広いpH範囲で進
行する。従ってアルカリ性下、特にpH9〜11で反応を行
うと、鉄シアン錯体が不溶性の化合物となって析出する
とともに、過剰の第一鉄塩および銅塩、ならびに共存す
るニッケル、亜鉛などの重金属イオンも水酸化物となっ
て析出し、同時に固液分離が可能となる。この場合、初
めからアルカリ側にpH調整して反応させてもよいが、第
一銅塩が溶存酵素で酸化される割合を減少させるために
酸性ないし中性下に第一鉄塩および銅塩を鉄シアン錯体
と反応させた後、アルカリ側にpH調整して他の金属を析
出させるのが望ましい。
The above reaction proceeds in a wide pH range from the acidic region to pH 11. Therefore, when the reaction is carried out under alkaline conditions, particularly at pH 9 to 11, the iron cyanide complex is precipitated as an insoluble compound, and at the same time, excess ferrous salts and copper salts and heavy metal ions such as nickel and zinc coexist with water. It precipitates as an oxide, and at the same time enables solid-liquid separation. In this case, the reaction may be carried out by adjusting the pH to the alkaline side from the beginning, but in order to reduce the rate at which the cuprous salt is oxidized by the dissolved enzyme, the ferrous salt and the copper salt are acidified or neutralized. After the reaction with the iron cyanide complex, it is desirable to adjust the pH to the alkali side to precipitate another metal.

こうして生成する難溶性塩はそのまま固液分離される
が、高分子凝集剤等の凝集剤を添加して凝集沈殿分離を
行うのが好ましい。凝集剤は第一鉄塩等と同時に添加し
てもよく、後から添加してもよい。また上記の反応およ
び凝集処理は1つの反応槽で同時に行ってもよく、時間
的にずらせて行ってもよい。固液分離は沈殿、濾過等の
公知の分離手段によることができる。
The hardly soluble salt thus formed is subjected to solid-liquid separation as it is, but it is preferable to perform coagulation precipitation separation by adding a coagulant such as a polymer coagulant. The coagulant may be added simultaneously with the ferrous salt or the like, or may be added later. Further, the above reaction and aggregation treatment may be performed simultaneously in one reaction tank, or may be performed with a time lag. Solid-liquid separation can be performed by known separation means such as precipitation and filtration.

上記の処理方法では、生成する難溶性塩は高pHにおい
てもシアン錯体を再溶解させることがないから、他の共
存金属と一緒に高pHで沈殿分離される。こうして得られ
た処理水はシアン、鉄、銅その他の重金属が除去され、
そのまま放流可能である。
In the above-described treatment method, the resulting hardly soluble salt does not redissolve the cyan complex even at a high pH, and thus is precipitated and separated at a high pH together with other coexisting metals. The treated water thus obtained is free of cyan, iron, copper and other heavy metals,
It can be released as it is.

〔発明の効果〕〔The invention's effect〕

以上の通り、本発明によれば、鉄シアン錯体含有水に
第一鉄塩および銅塩を反応させ、アルカリ性下で難溶性
塩を分離させるようにしたので、一段階の処理により、
鉄シアン錯体、過剰の鉄、銅、および共存重金属などを
同時に高除去率で除去できるとともに、薬剤使用量およ
び汚泥発生量を少なくすることができる。
As described above, according to the present invention, a ferrous salt and a copper salt are reacted with water containing an iron cyanide complex, and a sparingly soluble salt is separated under alkalinity.
The iron cyanide complex, excess iron, copper, coexisting heavy metals, and the like can be simultaneously removed at a high removal rate, and the amount of chemicals used and the amount of sludge generated can be reduced.

〔実施例〕〔Example〕

フェリシアン化ナトリウムNa3〔Fe(CN)〕を35mg/
(CNとして)含む原水に硫酸第一鉄(FeSO4・7H
2O)、硫酸銅(CuSO4・5H2O)および亜硫酸ナトリウム
(Na2SO3)を表1の通り添加した後、所定のpHに調整し
て10分間反応させ、濾紙No.5Aで濾過した濾液の水質を
表1に示す。
Sodium ferricyanide Na 3 [Fe (CN) 6 ] 35mg /
(As CN) raw ferrous sulfate containing (FeSO 4 · 7H
2 O), copper sulfate (CuSO 4 .5H 2 O) and sodium sulfite (Na 2 SO 3 ) were added as shown in Table 1, adjusted to a predetermined pH, reacted for 10 minutes, and filtered through filter paper No. 5A. The water quality of the filtrate obtained is shown in Table 1.

比較例として、第一鉄塩または(および)銅塩を添加
しないで、あるいは塩化亜鉛(ZnCl2)を添加して同様
の試験を行った結果を表2に示す。
As a comparative example, Table 2 shows the results of a similar test conducted without adding a ferrous salt and / or a copper salt or adding zinc chloride (ZnCl 2 ).

表1において、比較例1では第一鉄塩を還元剤として
利用するとシアン等の除去率が高くなるが、第一鉄塩を
大過剰に添加する必要があり、汚泥量も増大することが
わかる。比較例2のように少過剰の第一鉄塩を還元剤の
不存在下に反応させると、溶存酵素による第二鉄への酸
化およびフェリシアンの還元に消費されて第一鉄が不足
し、効果が悪くなると推定される。そこで実施例1のよ
うに還元剤を併用すると、シアン等の除去率が高くなる
ことがわかる。
In Table 1, in Comparative Example 1, when ferrous salt is used as a reducing agent, the removal rate of cyan and the like is increased, but it is necessary to add a large excess of ferrous salt, and the amount of sludge also increases. . When a small excess of ferrous salt is reacted in the absence of a reducing agent as in Comparative Example 2, ferrous deficiency is consumed due to oxidation to ferric iron by the dissolved enzyme and reduction of ferricyan, It is estimated that the effect will be worse. Thus, it can be seen that when a reducing agent is used in combination as in Example 1, the removal rate of cyan and the like increases.

これに対して表2の比較例3〜7では、第一鉄塩また
は銅塩の単独添加、あるいはこれらと還元剤もしくは亜
鉛との併用の場合、いずれもpH9以上でシアン除去率が
低下することがわかる。比較例8では曝気併用により第
一鉄塩を酸化した場合であり、これによりシアン除去効
果が悪化することがわかる。
On the other hand, in Comparative Examples 3 to 7 in Table 2, when only the ferrous salt or the copper salt is added alone, or when these are used in combination with the reducing agent or zinc, the cyan removal rate decreases at pH 9 or more. I understand. Comparative Example 8 shows the case where the ferrous salt was oxidized by the combined use of aeration, which indicates that the cyanide removing effect was deteriorated.

Claims (2)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】鉄シアン錯体含有水に第一鉄塩と銅塩と
を、第一鉄塩および銅塩以外の還元剤の存在下に反応さ
せて、アルカリ性下に難溶性塩を生成させ、固液分離す
ることを特徴とする鉄シアン錯体含有水の処理方法。
1. A ferrous salt and a copper salt are reacted with water containing an iron cyanide complex in the presence of a reducing agent other than the ferrous salt and the copper salt to form a poorly soluble salt under alkaline conditions. A method for treating iron-cyan complex-containing water, comprising performing solid-liquid separation.
【請求項2】難溶性塩を生成させるpHが9〜11である特
許請求の範囲第1項記載の方法。
2. The method according to claim 1, wherein the pH for forming the hardly soluble salt is 9 to 11.
JP62187252A 1987-07-27 1987-07-27 Treatment method for water containing iron cyanide complex Expired - Lifetime JP2580610B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP62187252A JP2580610B2 (en) 1987-07-27 1987-07-27 Treatment method for water containing iron cyanide complex

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP62187252A JP2580610B2 (en) 1987-07-27 1987-07-27 Treatment method for water containing iron cyanide complex

Publications (2)

Publication Number Publication Date
JPS6430693A JPS6430693A (en) 1989-02-01
JP2580610B2 true JP2580610B2 (en) 1997-02-12

Family

ID=16202713

Family Applications (1)

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JP62187252A Expired - Lifetime JP2580610B2 (en) 1987-07-27 1987-07-27 Treatment method for water containing iron cyanide complex

Country Status (1)

Country Link
JP (1) JP2580610B2 (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4639309B2 (en) * 2004-04-30 2011-02-23 株式会社片山化学工業研究所 Treatment method of wastewater containing cyanide
JP2012157798A (en) * 2011-01-31 2012-08-23 Jfe Steel Corp Method for treating cyanide-containing wastewater
JP2013163144A (en) * 2012-02-10 2013-08-22 Nippon Steel & Sumikin Eco-Tech Corp Treatment method for cyanide-containing wastewater
JP5962177B2 (en) * 2012-04-25 2016-08-03 栗田工業株式会社 Cyanogen-containing wastewater treatment method and treatment agent
JP7074167B2 (en) 2020-08-19 2022-05-24 栗田工業株式会社 Cyan-containing water treatment method and treatment equipment

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS49134163A (en) * 1973-04-27 1974-12-24

Also Published As

Publication number Publication date
JPS6430693A (en) 1989-02-01

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