JPH0483590A - Method and apparatus for treating cyan compound-containing solution - Google Patents
Method and apparatus for treating cyan compound-containing solutionInfo
- Publication number
- JPH0483590A JPH0483590A JP19666490A JP19666490A JPH0483590A JP H0483590 A JPH0483590 A JP H0483590A JP 19666490 A JP19666490 A JP 19666490A JP 19666490 A JP19666490 A JP 19666490A JP H0483590 A JPH0483590 A JP H0483590A
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- Japan
- Prior art keywords
- ferrous salt
- cyanide
- salt
- dissolved oxygen
- ferrous
- Prior art date
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Abstract
(57)【要約】本公報は電子出願前の出願データであるた
め要約のデータは記録されません。(57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.
Description
【発明の詳細な説明】
〔産業上の利用分野〕
この発明は、シアン化合物含有液に第一鉄塩を添加して
反応させ、シアン化合物を水不溶性塩として分離除去す
るシアン化合物含有液の処理方法および処理装置に関す
るものである。[Detailed Description of the Invention] [Industrial Application Field] This invention relates to the treatment of a cyanide compound-containing liquid, in which a ferrous salt is added to a cyanide-containing liquid and reacted, and the cyanide compound is separated and removed as a water-insoluble salt. The present invention relates to a method and a processing apparatus.
従来、シアン化合物1例えば金属シアン錯イオン含有液
を第一鉄塩と反応させ、水不溶性塩を生成させて分離除
去する方法として、特公昭51−28939号では、鉄
シアン錯体を対象とし、アルカリ塩素法による二段分解
のあと、酸化還元電位(以下、ORPという)が200
〜300mVになるように第一鉄塩を添加している。こ
の方法は次式の反応によるものである・
3Fe2” + 2Fe (CN)ニー→Fe、(Fe
(CN)slz↓ ・(1)2Fe” + OCQ’
−+ 2H” →2Fe” + Cj)−+ LO・・
・(2)ここでは(2)式よりも(1)式が優先して、
鉄シアン錯体の難溶化反応が起き、次いで、残留塩素が
還元されるため、残留塩素が消失した時点のORP値、
すなわち200〜300mVになるまで第一鉄塩を添加
すれば難溶化反応は完了しており、理論上処理は完全と
考えられていた。Conventionally, as a method for separating and removing cyanide compounds 1, for example, metal cyanide complex ion-containing liquids, by reacting them with ferrous salts to generate water-insoluble salts, Japanese Patent Publication No. 51-28939 deals with iron cyanide complexes, After two-stage decomposition using the chlorine method, the oxidation-reduction potential (hereinafter referred to as ORP) was 200.
Ferrous salt is added so that the voltage is ~300 mV. This method is based on the reaction of the following formula: 3Fe2" + 2Fe (CN) knee → Fe, (Fe
(CN)slz↓ ・(1)2Fe" + OCQ'
−+ 2H” →2Fe” + Cj)−+ LO・・
・(2) Here, equation (1) takes precedence over equation (2),
The reaction to make the iron cyanide complex less soluble occurs, and then the residual chlorine is reduced, so the ORP value at the time the residual chlorine disappears,
That is, if the ferrous salt was added until the voltage reached 200 to 300 mV, the reaction to make it difficult to solubilize would be completed, and it was thought that the treatment was theoretically complete.
また、特開平1−30693号および特公平1−355
3号では、鉄シアン錯体あるいは銀シアン錯体の含有景
に対して当量以上の第一鉄塩と銅塩を添加している。こ
の方法は次式により水不溶性の錯塩が生成する。Also, JP-A-1-30693 and JP-A-1-355
In No. 3, ferrous salt and copper salt are added in an amount equal to or more than the amount of iron cyanide complex or silver cyanide complex contained. In this method, a water-insoluble complex salt is generated according to the following formula.
xFa”+yCu”+zFe(CN)4−*FexCu
y(Fe(CN)、)、↓ ・(3)xFe”+yCu
”+zAg(CN)i−+FexCuy(Ag(CN)
、)、↓ ・(4)しかしながら、適正なORP制御
、 あるいは当量以上の第一鉄塩と銅塩を添加しても、
処理水シアン濃度が1 mg/Ωを越える場合があり、
このようなときには処理液を原水槽へ返送して再処理を
行わなければならず、安定した水処理ができないという
問題点があった。xFa"+yCu"+zFe(CN)4-*FexCu
y(Fe(CN), ), ↓ ・(3)xFe”+yCu
”+zAg(CN)i-+FexCuy(Ag(CN)
, ), ↓ ・(4) However, even if proper ORP control or more than equivalent amounts of ferrous salt and copper salt are added,
The cyanide concentration in treated water may exceed 1 mg/Ω,
In such a case, the treatment liquid must be returned to the raw water tank for reprocessing, which poses a problem in that stable water treatment cannot be performed.
この発明の目的は、上記問題点を解決するため、被処理
液中の溶存酸素(以下、DOという)を一定レベルに制
御することにより、第一鉄塩を過不足なく添加して、シ
アン化合物を高度に、しかも安定して処理することが可
能であり、処理液のシアン濃度を低くすることができる
シアン化合物含有液の処理方法および装置を提供するこ
とである。The purpose of this invention is to solve the above-mentioned problems by controlling the dissolved oxygen (hereinafter referred to as DO) in the liquid to be treated to a certain level, adding just the right amount of ferrous salt, and cyanide compound treatment. It is an object of the present invention to provide a method and apparatus for treating a cyanide-containing liquid, which can treat cyanide at a high level and stably, and can lower the cyanide concentration of the treatment liquid.
本発明は次のシアン化合物含有液の処理方法および装置
である。The present invention provides the following method and apparatus for treating a cyanide-containing liquid.
(1)シアン化合物含有液に第一鉄塩を添加し、前記シ
アン化合物を水不溶性塩として分離除去する方法におい
て、前記シアン化合物含有液に第一鉄塩を添加しながら
、または添加したのちに溶存酸素濃度を測定し、この溶
存酸素濃度値が急激に低下した時を第一鉄塩の添加の終
点とすることを特徴とするシアン化合物含有液の処理方
法。(1) In a method of adding a ferrous salt to a cyanide compound-containing liquid and separating and removing the cyanide compound as a water-insoluble salt, while or after adding the ferrous salt to the cyanide compound-containing liquid, 1. A method for treating a cyanide-containing liquid, the method comprising measuring the dissolved oxygen concentration, and determining the end point of addition of ferrous salt when the dissolved oxygen concentration value sharply decreases.
(2)シアン化合物含有液が連続的に流入する反応槽に
第一鉄塩を添加し、前記シアン化合物を水不溶性塩とし
て分離除去する方法において、反応槽内の溶存酸素濃度
を測定し、この溶存酸素濃度が所定値になるように第一
鉄塩を添加することを特徴とするシアン化合物含有液の
処理方法。(2) In a method in which a ferrous salt is added to a reaction tank into which a cyanide compound-containing liquid continuously flows, and the cyanide compound is separated and removed as a water-insoluble salt, the dissolved oxygen concentration in the reaction tank is measured, and the dissolved oxygen concentration in the reaction tank is measured. A method for treating a cyanide-containing liquid, which comprises adding a ferrous salt so that the dissolved oxygen concentration reaches a predetermined value.
(3)シアン化合物含有液を導入して第一鉄塩と反応さ
せる反応槽と、
この反応槽に第一鉄塩を添加する手段と、前記反応槽内
の溶存酸素濃度を測定する溶存酸素計と、
この溶存酸素計で測定された溶存酸素濃度値に基づいて
第一鉄塩の添加量を製御する制御装置とを備えたことを
特徴とするシアン化合物含有液の処理装置。(3) A reaction tank for introducing a cyanide compound-containing liquid to react with a ferrous salt, a means for adding the ferrous salt to the reaction tank, and a dissolved oxygen meter for measuring the dissolved oxygen concentration in the reaction tank. and a control device for controlling the amount of ferrous salt added based on the dissolved oxygen concentration value measured by the dissolved oxygen meter.
従来の処理方法においてバラツキが発生する原因につい
て検討した結果、処理液のシアン濃度とDoの間には密
接な関係があり、DOが一定レベルになるように第一鉄
塩の注入制御を実施すれば、安定した処理液が得られる
ことが明らかとなった。As a result of examining the causes of variations in conventional treatment methods, we found that there is a close relationship between the cyanide concentration of the treatment solution and Do, and that ferrous salt injection should be controlled to keep DO at a constant level. It has become clear that a stable processing solution can be obtained.
第一鉄塩とDoはpH5以上では容易に反応し、第一鉄
が次式により酸化されて第二鉄になり易い。Ferrous salt and Do easily react at pH 5 or higher, and ferrous iron is easily oxidized to ferric iron according to the following formula.
2Fe” + O+ HzO→2Fe” + 208−
・・・(5)このため前記(1)式、(3)式
、(4)式の沈殿物中の鉄塩は全て第一鉄塩(Fe2+
)であり、添加した第一鉄塩の添加量が少過剰の場合は
DOにより酸化され、次式により再溶解する。2Fe" + O+ HzO→2Fe" + 208-
...(5) Therefore, the iron salts in the precipitates of formulas (1), (3), and (4) are all ferrous salts (Fe2+
), and if the amount of ferrous salt added is slightly excessive, it will be oxidized by DO and redissolved according to the following formula.
Fe、 [Fe(CN)s)a →3Fe”+2Fe(
CN)ニー −(6)FexCuy(Fe
(CN)、)z →xFe”+yCu”+zFe(CN
)’5−(7)FexCuy(Ag(CN)2)、 −
) xFe”+yCu”十zAg(CN)i −(8
)上記の点を実証するためORP制御による紺青法処理
を行ったところ、シアンの処理不全が生じた。Fe, [Fe(CN)s)a →3Fe”+2Fe(
CN) knee - (6) FexCuy (Fe
(CN), )z →xFe"+yCu"+zFe(CN
)'5-(7)FexCuy(Ag(CN)2), -
) xFe”+yCu” zAg(CN)i −(8
) In order to prove the above point, when a deep blue method processing using ORP control was performed, cyan processing failure occurred.
この結果は後記の実施例に示すが、シアン錯体を完全に
難溶化するためには、反応光景以上の第一鉄塩が必要で
あり、その過剰斌はDOが一定レベル以下になるまでの
添加量が必要なことがわかった。This result will be shown in the example below, but in order to completely make the cyanide complex insoluble, more ferrous salt than the reaction figure is required, and the excess amount must be added until DO falls below a certain level. I found out that I needed a lot.
本発明において処理の対象となるシアン化合物含有液は
、遊離シアンイオンや金属シアン錯イオンを有する液体
であり、具体的には、フエロシアンイオン(Fe(CN
)2−)、フェリシアンイオン[Fe(CN)ffi−
3等の鉄シアン錯イオンを含む水や銀シアン錯イオン(
Ag(CN)i)を含む水のほか、カリウム、ナトリウ
ム、銅、ニッケル、亜鉛などの他の金属イオンがシアン
イオンと共存する水などがあげられる。The cyanide compound-containing liquid to be treated in the present invention is a liquid containing free cyanide ions and metal cyanide complex ions, specifically, ferrocyanide ions (Fe(CN
)2-), ferricyanion [Fe(CN)ffi-
Water containing iron cyanide complex ions of grade 3 and silver cyanide complex ions (
In addition to water containing Ag(CN)i), examples include water in which other metal ions such as potassium, sodium, copper, nickel, and zinc coexist with cyanide ions.
上記シアン化合物含有液に添加す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。The ferrous salt added to the cyanide-containing solution is as follows:
Ferrous chloride, ferrous sulfate, etc. can be used.
本発明においては、被処理液中のシアン化合物を水不溶
性塩とするために、第一鉄塩を添加して反応させる。こ
の場合、シアン化合物含有液に第一鉄塩を単独で添加す
ることもできるが、第一鉄塩とともに銅塩を添加するの
が好ましい。In the present invention, in order to convert the cyanide compound in the liquid to be treated into a water-insoluble salt, a ferrous salt is added and reacted. In this case, although the ferrous salt can be added alone to the cyanide-containing liquid, it is preferable to add the copper salt together with the ferrous salt.
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。The copper salt may be any water-soluble salt, and may be either a monovalent copper salt or a divalent copper salt, but monovalent copper salts are generally poorly soluble and easily oxidized by air, so they are not commercially available. divalent copper salts such as copper sulfate, copper chloride, and copper nitrate are available.
第一鉄塩は反応の時点あるいはその後に第二鉄に酸化さ
れると水不溶性塩が生成しにくくなるので、反応時にお
ける空気酸化は避けるのが望まし%N。If ferrous salt is oxidized to ferric iron during or after the reaction, it becomes difficult to form a water-insoluble salt, so it is desirable to avoid air oxidation during the reaction.
第一鉄塩を添加して反応させる際、水不溶性塩を効率よ
く生成するため、pH調整剤を添加して反応液をPH5
〜11に調整するのが好ましい、 PH調整剤としては
塩酸、硫酸等の酸や、水酸化ナトリウム、水酸化カルシ
ウム等のアルカリが使用できる。When adding and reacting ferrous salts, in order to efficiently generate water-insoluble salts, a pH adjuster is added to adjust the reaction solution to pH 5.
It is preferable to adjust the pH to 11. As the pH adjuster, acids such as hydrochloric acid and sulfuric acid, and alkalis such as sodium hydroxide and calcium hydroxide can be used.
反応液がP)15より低い場合には第一鉄イオンと溶存
酸素の反応が起り易く、またpH11より高い場合には
水不溶性塩が生成しにくくなる。If the reaction solution has a pH lower than P) 15, the reaction between ferrous ions and dissolved oxygen tends to occur, and if the pH is higher than 11, it becomes difficult to form water-insoluble salts.
本発明によるシアン化合物含有液の処理は、反応槽にシ
アン化合物含有液を導入し、これに第一鉄塩を添加して
、被処理液のシアン化合物と反応させ、水不溶性塩を生
成させる6回分式に処理を行う場合、第一鉄塩を添加し
ながら、DO計によりDO濃度を測定し、または第一鉄
塩を適意添加したのち、Do濃度を測定する操作を繰返
す。そしてDO濃度の値が急激に低下した時をもって第
一鉄塩の添加の終点とする。In the treatment of a cyanide-containing liquid according to the present invention, a cyanide-containing liquid is introduced into a reaction tank, a ferrous salt is added thereto, and the ferrous salt is reacted with the cyanide compound in the liquid to be treated to produce a water-insoluble salt. When the treatment is carried out in a batch manner, the operation of measuring the DO concentration using a DO meter while adding the ferrous salt, or adding the ferrous salt appropriately and then measuring the Do concentration is repeated. The end point of the addition of ferrous salt is when the value of DO concentration suddenly decreases.
連続式の場合は、DO濃度が所定値になるように、すな
わち回分処理における急激に低下した時のり。In the case of a continuous type, the DO concentration is adjusted to a predetermined value, that is, when the DO concentration suddenly decreases in batch processing.
濃度の値と同じになるように、第一鉄塩を添加して水不
溶性塩を効率よく生成させることができる。Ferrous salts can be added to efficiently generate water-insoluble salts so that the concentration values are the same.
こうして反応液中に生成する水不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−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 water-insoluble salts thus generated in the reaction solution are separated into solid-liquid as they are, but it is preferable to perform coagulation-sedimentation separation by adding a flocculant such as a polymer flocculant. They may be added at the same time or may be added later. Further, the above reaction and aggregation treatment may be performed simultaneously in one reaction tank or may be performed at different times. Solid-liquid separation can be performed by known separation means such as precipitation and filtration.
本発明では、シアン化合物含有液中に、遊離シアンまた
は易分解性のシアン化合物が共存している場合、予めこ
れらのイオンをアルカリ塩素法等で分解しておくと分離
除去効率がよくなる。アルカリ塩素法の場合には、まず
pH10以上で塩素剤を添加して1次分解を行い、その
後pHを低下させて再度塩素剤を添加して2次分解を行
う二段処理法が好ましい。In the present invention, when free cyanide or easily decomposable cyanide compounds coexist in the cyanide-containing liquid, separation and removal efficiency can be improved by decomposing these ions in advance by an alkali chlorine method or the like. In the case of the alkali chlorine method, a two-stage treatment method is preferred, in which a chlorine agent is first added at pH 10 or higher to perform primary decomposition, and then the pH is lowered and a chlorine agent is added again to perform secondary decomposition.
以上のようにしてシアン化合物含有液を処理すると、反
応液のDo濃度が低下しているので、水不溶性塩中の第
一鉄が溶存酸素により第二鉄に酸化されず、再溶解する
ことがない。そのため、処理液中にシアンイオンがリー
クすることがなく、高度の処理を安定して行うことがで
きる。When a cyanide-containing solution is treated as described above, the Do concentration in the reaction solution is reduced, so that the ferrous iron in the water-insoluble salt is not oxidized to ferric iron by dissolved oxygen and can be redissolved. do not have. Therefore, cyan ions do not leak into the processing liquid, and high-level processing can be performed stably.
以下、本発明の実施例について説明する。 Examples of the present invention will be described below.
第1図は実施例のシアン化合物含有液処理装置を示す系
統図である。図において、1は反応槽であり、被処理液
管2から被処理液を導入して第一鉄塩と反応させ1反応
液3を処理液として処理液管4から取出すようになって
いる1反応槽1には、第一鉄塩供給管5、銅塩供給管6
、酸供給管7、アルカリ供給管8が連絡し、それぞれに
設けられたポンプP1、P2、P3.P4が制御装置9
により制御されるようになっている。反応液3中には、
モータMにより回転する攪拌機10、DO計11、pH
計12が設けられており、それぞれ制御装置9に接続し
ている。FIG. 1 is a system diagram showing a cyanide compound-containing liquid processing apparatus according to an embodiment. In the figure, reference numeral 1 denotes a reaction tank, in which a liquid to be treated is introduced from a liquid to be treated tube 2, reacted with ferrous salt, and a reaction liquid 3 is taken out from a treated liquid tube 4 as a treatment liquid. The reaction tank 1 includes a ferrous salt supply pipe 5 and a copper salt supply pipe 6.
, acid supply pipe 7, and alkali supply pipe 8 communicate with each other, and pumps P1, P2, P3 . P4 is the control device 9
It is now controlled by. In reaction solution 3,
Stirrer 10 rotated by motor M, DO meter 11, pH
A total of 12 are provided, each connected to the control device 9.
上記の処理装置によるシアン化合物含有液の処理方法は
、反応槽1に被処理液管2から被処理液を導入し、制御
装置9によりポンプP□、P2を駆動して、第一鉄塩供
給管5から第一鉄塩を添加し、銅塩供給管6から銅塩を
添加し、攪拌機10を回転させて反応させ、水不溶性塩
を生成させる。この間pH計12により反応液3のPH
を測定し、そのp)I値によりポンプp3またはP、を
駆動して酸またはアルカリを添加し、反応液3のp)I
を5〜11に制御する。The method for treating a cyanide-containing liquid using the above-mentioned processing apparatus is to introduce the liquid to be treated into the reaction tank 1 from the liquid to be treated pipe 2, and to supply ferrous salt by driving the pumps P□ and P2 by the control unit 9. Ferrous salt is added through tube 5, copper salt is added through copper salt supply tube 6, and the stirrer 10 is rotated to cause a reaction and produce a water-insoluble salt. During this time, the pH of the reaction solution 3 was measured by the pH meter 12.
is measured, and depending on the p)I value, pump p3 or P is driven to add acid or alkali, and the p)I of reaction solution 3 is
is controlled to 5-11.
Do計11では反応液3のDO濃度を測定し、そのDO
濃度値を制御装置9に入力する。制御装置9には予めビ
ーカーテスト等によりDO濃度値が急激に低下する時点
のDO濃度を設定しておき、そのDo濃度になる時点を
第一鉄塩添加の終点とするようにポンプP1を制御する
。DOが6mg/Q以下、好ましくは3m1g/Q以下
、さらに好ましくは2 rag/Q以下となる時点を終
点とするように制御することもできる。The DO meter 11 measures the DO concentration of the reaction solution 3 and calculates the DO concentration.
The concentration value is input to the control device 9. The control device 9 is set in advance by a beaker test or the like to set the DO concentration at the point in time when the DO concentration value rapidly decreases, and the pump P1 is controlled so that the point at which the Do concentration is reached is the end point of ferrous salt addition. do. It can also be controlled so that the end point is the point in time when the DO becomes 6 mg/Q or less, preferably 3 ml g/Q or less, more preferably 2 rag/Q or less.
第一鉄塩の添加とDo濃度値の測定は連続的に行っても
よく、また適当量の第一鉄塩を添加して反応させた後、
Do濃度を測定する操作を繰返えしてもよい0反応後、
反応液3を処理液として処理液管4から取出し、固液分
離により水不溶性塩を生成させる。The addition of the ferrous salt and the measurement of the Do concentration value may be performed continuously, or after adding an appropriate amount of the ferrous salt and reacting,
After the 0 reaction, the operation of measuring the Do concentration may be repeated.
The reaction liquid 3 is taken out as a treatment liquid from the treatment liquid pipe 4, and a water-insoluble salt is generated by solid-liquid separation.
上記の反応はバッチ式で行ってもよく、連続式で行って
もよい。バッチ式の場合はDo濃度値の急激な低下の時
点を検出するのに適している。連続式の場合は反応槽が
完全混合型ならばDO濃度値が所定の値になるように第
一鉄塩を添加すればよく、また反応槽が押し出し流れ型
ならば、液の流れに沿って複数個のDO計を設置し、最
下流のDO計のDO濃度値が所定の値になるように第一
鉄塩を添加することにより、第一鉄塩の添加量制御が可
能である。The above reaction may be carried out batchwise or continuously. The batch type is suitable for detecting the point of sudden decrease in the Do concentration value. In the case of a continuous type reaction tank, if the reaction tank is a complete mixing type, ferrous salt should be added so that the DO concentration value becomes the specified value, and if the reaction tank is a push-flow type, ferrous salt should be added along the flow of the liquid. The amount of ferrous salt added can be controlled by installing a plurality of DO meters and adding ferrous salt so that the DO concentration value of the most downstream DO meter becomes a predetermined value.
実施例1および比較例1 紺青処理
鉄シアン錯イオンを含むメツキ廃水(全CN 65wa
g/Q、 Zn 28IIgIQ、 Fg 8B/Q)
を通常のアルカリ塩素性二段処理(−次: pH10,
5、ORP 500■■、20分間反応、二次:p)1
8、ORP 750■■、30分間反応)で処理して、
全CNを25rag/(lにした後、第一鉄塩としてF
e50.・7H20を添加し、pH6に調整して紺青処
理を行った。このときのDo濃度値、ORP値、および
処理水全シアンとFe50.・7H20添加量との関係
を第2図に示す。Example 1 and Comparative Example 1 Metsuki wastewater containing dark blue treated iron cyanide complex ions (total CN 65wa
g/Q, Zn 28IIgIQ, Fg 8B/Q)
was subjected to the usual alkali-chlorinated two-stage treatment (-Next: pH 10,
5, ORP 500 ■■, reaction for 20 minutes, secondary: p) 1
8. ORP 750■■, 30 minutes reaction)
After making the total CN 25 rag/(l), F as ferrous salt
e50.・7H20 was added, the pH was adjusted to 6, and a dark blue treatment was performed. At this time, Do concentration value, ORP value, treated water total cyanide and Fe50. - Figure 2 shows the relationship with the amount of 7H20 added.
比較例1はORP制御による方法であり、第一鉄塩の添
加ON −OFFの電位設定は、ORP値変比変化配の
急な範囲から選ばれる。例えば第2図において。Comparative Example 1 is a method based on ORP control, and the ON-OFF potential setting of ferrous salt addition is selected from a steep range of ORP value ratio change distribution. For example, in FIG.
設定電位は300〜70(laVの範囲で選定され、3
00■■で第一鉄塩の添加OFF、400■■でONと
いうような制御を行った。ところがこのような設定値を
選定した場合は、第2図から明らかなように、シアンの
難溶化はまだ完了していない。このためさらに第一鉄塩
が添加されるようなORP値を選定する必要があるが、
ORP値300■■以下では、第一鉄塩添加量に対する
ORPの変化が緩慢であり、制御が困難である。シアン
処理の安全を見込んで、低いORP値を設定した場合は
第一鉄塩の過剰注入となり実用的でない。The set potential is selected in the range of 300 to 70 (laV, 3
Control was performed such that the addition of ferrous salt was turned off at 00■■ and turned on at 400■■. However, when such a setting value is selected, as is clear from FIG. 2, cyanide is not yet completely rendered insoluble. Therefore, it is necessary to select an ORP value that allows further addition of ferrous salt.
When the ORP value is less than 300■■, the change in ORP with respect to the amount of ferrous salt added is slow and control is difficult. If a low ORP value is set in consideration of the safety of cyanogen treatment, excessive ferrous salt will be injected, which is impractical.
一方、実施例1はDo濃度値により第一鉄塩の添加を制
御する方法であり、この方法では、シアン錯イオンが低
レベルまで処理された後、Do濃度値が急激に低下して
おり、例えばDO濃度が3 mgIQ以下になるまで第
一鉄塩を添加すれば、全シアン濃度1 yag/Q以下
の処理水が得られることが分かる。On the other hand, Example 1 is a method in which the addition of ferrous salt is controlled by the Do concentration value, and in this method, after the cyanide complex ions are treated to a low level, the Do concentration value rapidly decreases. For example, it can be seen that if ferrous salt is added until the DO concentration becomes 3 mgIQ or less, treated water with a total cyanide concentration of 1 yag/Q or less can be obtained.
施例2および比較例2 銀シアン、鉄シアンを含む廃水
の処理
銀シアン、鉄シアンを含むメツキ廃水を通常のようにア
ルカリ塩素処理後、pH8〜8.5で第一鉄塩としてF
e50.・7H20を添加して処理した。アルカリ塩素
処理後の水質はpH7〜7.5、全CN 5.8〜10
mg/Q、 Cu 20mg/Q、 Ag 5.Omg
/Q、 Fe 3mg/Qであり、処理水量は5ポ/h
rである。Example 2 and Comparative Example 2 Treatment of wastewater containing silver cyanide and iron cyanide After the metallurgical wastewater containing silver cyanide and iron cyanide was treated with alkaline chlorine as usual, it was treated with F as a ferrous salt at pH 8 to 8.5.
e50. - Treated by adding 7H20. Water quality after alkali chlorine treatment is pH 7-7.5, total CN 5.8-10
mg/Q, Cu 20mg/Q, Ag 5. Omg
/Q, Fe 3mg/Q, and the amount of treated water is 5 points/h
It is r.
比較例2では200■■ テ第−鉄塩添加OFF、30
0■■でONの運転を行った。In Comparative Example 2, 200 ■■ Te ferrous salt addition OFF, 30
The ON operation was performed at 0■■.
一方、実施例2では、ORP計の替りにDO計を使って
第一鉄塩添加の制御を行った。ORP値およびDo濃度
値と第−鉄塩添加量の関係を第3図に示す。On the other hand, in Example 2, a DO meter was used instead of an ORP meter to control the addition of ferrous salt. FIG. 3 shows the relationship between the ORP value, the Do concentration value, and the amount of ferrous salt added.
また第3図の結果に基づき、DO濃度値3BIQで第一
鉄塩の添加ON、2 mg#lでOFFとした。ORP
計で制御した場合とDO計で制御した場合の沈殿槽出口
の処理水を濾紙Nn5Aで濾過した濾液の分析結果を表
1に示す。Furthermore, based on the results shown in FIG. 3, the addition of ferrous salt was turned on at a DO concentration of 3BIQ, and turned off at a DO concentration of 2 mg#l. ORP
Table 1 shows the analysis results of the filtrate obtained by filtering the treated water at the outlet of the sedimentation tank through filter paper Nn5A when the water was controlled by a DO meter and when it was controlled by a DO meter.
表1
表2
処理水分析値(液温26℃)
表1に示すように、ORP計で制御した場合の処理水の
水質の変動は大きいが、DO計で制御した場合は安定し
て良好な水質の処理水が得られ、DO計による制御の有
効性が実証された。Table 1 Table 2 Analytical values of treated water (liquid temperature 26°C) As shown in Table 1, the quality of treated water fluctuates widely when controlled with an ORP meter, but is stable and good when controlled with a DO meter. Treated water of high quality was obtained, demonstrating the effectiveness of control using the DO meter.
実施例3
遊離シアン5 WAGED (CNとして)とフェロシ
アン2mg、1(CNとして)を含む廃水に、第一鉄塩
FeSO4・7H20と銅塩CuSO4を添加し、Do
計により制御して処理を行った。結果を表2に示す。Example 3 Ferrous salt FeSO4.7H20 and copper salt CuSO4 were added to wastewater containing free cyanide 5 WAGED (as CN) and ferrocyanide 2 mg, 1 (as CN), and Do
The treatment was controlled by a meter. The results are shown in Table 2.
表2に示すように、銅塩を併用し、DO濃度値を指標と
して第一鉄塩の添加量を適正な値に制御すれば、遊離シ
アンを含む廃水の処理も可能であることがわかる。As shown in Table 2, it is found that it is possible to treat wastewater containing free cyanide if a copper salt is used in combination and the amount of ferrous salt added is controlled to an appropriate value using the DO concentration value as an index.
以上の通り、本発明によれば、Do濃度の値を指標とし
て第一鉄塩の添加量を制御するようにしたので、第一鉄
塩を過不足なく添加して、シアン化合物含有液を効率よ
く高度に、しかも安定して処理することができ、シアン
濃度の低い処理液を得ることができる。As described above, according to the present invention, since the amount of ferrous salt added is controlled using the Do concentration value as an index, the amount of ferrous salt added is just the right amount, and the cyanide-containing liquid is efficiently controlled. Processing can be carried out highly and stably, and a processing solution with a low cyan concentration can be obtained.
第1図は実施例の処理装置を示す系統図、第2図および
第3図は実施例の結果を示すグラフである。
1:反応槽、2:被処理液管、3:反応液、4:処理液
管、5:第一鉄塩供給管、9:制御装置、10:攪拌機
、11 : Do計、12 : p)l計。
第3図
°代理人 弁理士 柳 原 成FIG. 1 is a system diagram showing the processing apparatus of the example, and FIGS. 2 and 3 are graphs showing the results of the example. 1: reaction tank, 2: treated liquid pipe, 3: reaction liquid, 4: treated liquid pipe, 5: ferrous salt supply pipe, 9: control device, 10: stirrer, 11: Do meter, 12: p) L total. Figure 3 ° Agent Patent attorney Sei Yanagihara
Claims (3)
アン化合物を水不溶性塩として分離除去する方法におい
て、前記シアン化合物含有液に第一鉄塩を添加しながら
、または添加したのちに溶存酸素濃度を測定し、この溶
存酸素濃度値が急激に低下した時を第一鉄塩の添加の終
点とすることを特徴とするシアン化合物含有液の処理方
法。(1) In a method of adding a ferrous salt to a cyanide compound-containing liquid and separating and removing the cyanide compound as a water-insoluble salt, while or after adding the ferrous salt to the cyanide compound-containing liquid, 1. A method for treating a cyanide-containing liquid, the method comprising measuring the dissolved oxygen concentration, and determining the end point of addition of ferrous salt when the dissolved oxygen concentration value sharply decreases.
第一鉄塩を添加し、前記シアン化合物を水不溶性塩とし
て分離除去する方法において、反応槽内の溶存酸素濃度
を測定し、この溶存酸素濃度が所定値になるように第一
鉄塩を添加することを特徴とするシアン化合物含有液の
処理方法。(2) In a method in which a ferrous salt is added to a reaction tank into which a cyanide compound-containing liquid continuously flows, and the cyanide compound is separated and removed as a water-insoluble salt, the dissolved oxygen concentration in the reaction tank is measured, and the dissolved oxygen concentration in the reaction tank is measured. A method for treating a cyanide-containing liquid, which comprises adding a ferrous salt so that the dissolved oxygen concentration reaches a predetermined value.
せる反応槽と、 この反応槽に第一鉄塩を添加する手段と、 前記反応槽内の溶存酸素濃度を測定する溶存酸素計と、 この溶存酸素計で測定された溶存酸素濃度値に基づいて
第一鉄塩の添加量を制御する制御装置とを備えたことを
特徴とするシアン化合物含有液の処理装置。(3) A reaction tank for introducing a cyanide compound-containing liquid to react with a ferrous salt, a means for adding the ferrous salt to this reaction tank, and a dissolved oxygen meter for measuring the dissolved oxygen concentration in the reaction tank. and a control device for controlling the amount of ferrous salt added based on the dissolved oxygen concentration value measured by the dissolved oxygen meter.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2196664A JPH0675707B2 (en) | 1990-07-25 | 1990-07-25 | Method and apparatus for treating liquid containing cyanide compound |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2196664A JPH0675707B2 (en) | 1990-07-25 | 1990-07-25 | Method and apparatus for treating liquid containing cyanide compound |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH0483590A true JPH0483590A (en) | 1992-03-17 |
| JPH0675707B2 JPH0675707B2 (en) | 1994-09-28 |
Family
ID=16361545
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2196664A Expired - Lifetime JPH0675707B2 (en) | 1990-07-25 | 1990-07-25 | Method and apparatus for treating liquid containing cyanide compound |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0675707B2 (en) |
Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH05277473A (en) * | 1992-04-01 | 1993-10-26 | Ebara Infilco Co Ltd | Treatment method and treatment apparatus for reducing agent-containing wastewater |
| JP2011173046A (en) * | 2010-02-23 | 2011-09-08 | Jfe Steel Corp | Cyanide-containing wastewater treatment method and apparatus |
| JP2013208551A (en) * | 2012-03-30 | 2013-10-10 | Kurita Water Ind Ltd | Method for treating cyanogen-containing waste water |
| JP2013208550A (en) * | 2012-03-30 | 2013-10-10 | Kurita Water Ind Ltd | Method for treating cyanogen-containing waste water |
| US10661444B2 (en) | 2014-03-31 | 2020-05-26 | Intelligrated Headquarters, Llc | Autonomous truck loader and unloader |
| WO2022039182A1 (en) * | 2020-08-19 | 2022-02-24 | 栗田工業株式会社 | Method and apparatus for treating cyanogen-containing water |
-
1990
- 1990-07-25 JP JP2196664A patent/JPH0675707B2/en not_active Expired - Lifetime
Cited By (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH05277473A (en) * | 1992-04-01 | 1993-10-26 | Ebara Infilco Co Ltd | Treatment method and treatment apparatus for reducing agent-containing wastewater |
| JP2011173046A (en) * | 2010-02-23 | 2011-09-08 | Jfe Steel Corp | Cyanide-containing wastewater treatment method and apparatus |
| JP2013208551A (en) * | 2012-03-30 | 2013-10-10 | Kurita Water Ind Ltd | Method for treating cyanogen-containing waste water |
| JP2013208550A (en) * | 2012-03-30 | 2013-10-10 | Kurita Water Ind Ltd | Method for treating cyanogen-containing waste water |
| US10661444B2 (en) | 2014-03-31 | 2020-05-26 | Intelligrated Headquarters, Llc | Autonomous truck loader and unloader |
| WO2022039182A1 (en) * | 2020-08-19 | 2022-02-24 | 栗田工業株式会社 | Method and apparatus for treating cyanogen-containing water |
| JP2022034874A (en) * | 2020-08-19 | 2022-03-04 | 栗田工業株式会社 | Treatment method and treatment device of cyanogen-containing water |
Also Published As
| Publication number | Publication date |
|---|---|
| JPH0675707B2 (en) | 1994-09-28 |
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