JPH0231888A - Treatment of heavy metal waste water containing cyanide - Google Patents

Treatment of heavy metal waste water containing cyanide

Info

Publication number
JPH0231888A
JPH0231888A JP18150688A JP18150688A JPH0231888A JP H0231888 A JPH0231888 A JP H0231888A JP 18150688 A JP18150688 A JP 18150688A JP 18150688 A JP18150688 A JP 18150688A JP H0231888 A JPH0231888 A JP H0231888A
Authority
JP
Japan
Prior art keywords
waste water
cyanide
heavy metal
contg
heavy metals
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
JP18150688A
Other languages
Japanese (ja)
Inventor
Shunichi Ema
江間 俊一
Takashi Yoshida
崇 吉田
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.)
NEC Corp
Original Assignee
NEC 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 NEC Corp filed Critical NEC Corp
Priority to JP18150688A priority Critical patent/JPH0231888A/en
Publication of JPH0231888A publication Critical patent/JPH0231888A/en
Pending legal-status Critical Current

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  • Removal Of Specific Substances (AREA)

Abstract

PURPOSE:To treat heavy metal waste water contg. cyanide discharged from university, etc., by adding chloride and permanganate ions to the waste water, by heating and aerating, by introducing the produced gas to an alkali soln., by decomposing at a specified pH, by adding iron(II) iton to the remaining waste water, by oxidizing heavy metals at specified pH and by removing the produced spinel compds. contg. heavy metals. CONSTITUTION:The pH value of the waste water contg. Fe, Cu, Zn, cyanide, etc., is adjusted to <= 2 with H2SO4 and the waste water is added with NaCl and potassium permanganate and aerated while heating. The aerated air is introduced to a NaOH soln. and the pH value of the soln. is kept at 7.5-8 to decompose the recovered cyanic acid. On the other hand, the remaining waste water is added with FeSO4 and oxidized at <= 6 pH value to produce the spinel compds. contg. heavy metals, and thus, the heavy metals are removed. Thereby, the waste water can be efficiently treated without the residue of cyanogen complex and an expensive equipment.

Description

【発明の詳細な説明】 [産業上の利用分野] 本発明は各種研究機関、大学等から排出されるシアン含
有重金属廃水の処理方法に関するものである。
[Detailed Description of the Invention] [Industrial Application Field] The present invention relates to a method for treating cyanide-containing heavy metal wastewater discharged from various research institutes, universities, etc.

[従来の技術およびその課題] 従来、各種研究機関、大学等から排出される廃液は、主
にフェライト法、中和凝沈法による処理が行われてきた
。フェライト法は、特に種々の重金属が混入する廃液の
一括処理に対して有効であるが、シアンが含有されてい
る場合には、このシアンをあらかじめ分別しておくこと
が原則である。
[Prior art and its problems] Conventionally, waste liquid discharged from various research institutes, universities, etc. has been mainly treated by the ferrite method and the neutralization coagulation method. The ferrite method is particularly effective for bulk treatment of waste liquids containing various heavy metals, but if cyanide is contained, it is a general rule to separate this cyanide in advance.

即ち、重金属廃液中にシアンが混入している場合、この
ような廃液にフェライト法を適用した時には、処理液に
重金属のシアノ錯体が残存する。
That is, when cyanide is mixed in the heavy metal waste liquid, when the ferrite method is applied to such waste liquid, the heavy metal cyano complex remains in the treated liquid.

従って二次処理として焼却処分またはアルカリ塩素法等
のシアン分解処理が必要となる。
Therefore, as a secondary treatment, cyanide decomposition treatment such as incineration or an alkali chlorine method is required.

焼却処分する場合には、高価な設備が必要であるばかり
でなく、多大な時間を要する。またアルカリ塩素法によ
る場合には、鉄シアノ錯体の分解効率が悪く、また使用
する次亜塩素酸は安定性に欠けるため保存に問題がある
Incineration not only requires expensive equipment but also takes a lot of time. Furthermore, when using the alkali chlorine method, the decomposition efficiency of the iron cyano complex is poor, and the hypochlorous acid used lacks stability, resulting in storage problems.

ざらにシアノ錯体に亜鉛塩の存在下で還元剤を作用させ
て、フェロシアン化亜鉛として沈澱・除去する方法も提
案されているが、処理工程が複雑となり、フェライト法
の2次処理としては実用化が困難である。
A method has also been proposed in which the cyano complex is treated with a reducing agent in the presence of a zinc salt to precipitate and remove it as zinc ferrocyanide, but the treatment process is complicated and it is not practical as a secondary treatment for the ferrite method. It is difficult to

本発明はこのような問題点を解決するためになされたも
ので、安定な試薬を用いて効率良くシアンを分解するこ
とのできるシアン含有重金属廃水の処理方法を提供する
ことを目的とする。
The present invention was made to solve these problems, and an object of the present invention is to provide a method for treating cyanide-containing heavy metal wastewater that can efficiently decompose cyanide using a stable reagent.

[課題を解決するための手段] 本発明は、シアン含有重金属廃水に塩素イオンおよび過
マンガン酸イオンを加え、p(12以下で加熱しながら
通気してシアンを気散させた後、前記シアン含有通気カ
スについては、前記ガスをアルカリ液中に導入してシア
ン成分をシアン酸として回収した後、回収液のpHを7
.5〜8に保持()て前記シアン酸を分解・除去し、残
存重金属廃水中の重金属については、前記廃水中に第1
鉄イオンを添加し、pH6以上で酸化して重金属イオン
を含むスピネル化合物を作成することにより除去するこ
とを特徴とするシアン含有重金属廃水の処理方法である
[Means for Solving the Problems] The present invention includes adding chlorine ions and permanganate ions to cyanide-containing heavy metal wastewater, aerating the wastewater while heating at p(12 or less) to diffuse cyanide, and then dissolving the cyanide-containing heavy metal wastewater. Regarding ventilation scum, after introducing the gas into an alkaline solution and recovering the cyanide component as cyanic acid, the pH of the recovered solution was adjusted to 7.
.. 5 to 8 () to decompose and remove the cyanic acid, and remove residual heavy metals from the wastewater.
This is a method for treating cyanide-containing heavy metal wastewater, which is characterized in that iron ions are added and removed by oxidation at pH 6 or higher to create a spinel compound containing heavy metal ions.

[作用] 金属シアノ錯体の酸性溶液は加熱処理することで、成分
中のシアンが気散されやすくなり、また、空気等のガス
を通気することで気散速度も増大する。
[Function] By heating the acidic solution of the metal cyano complex, the cyanide in the component becomes easily diffused, and by aerating gas such as air, the rate of vaporization increases.

一方、過マンガン酸イオンは酸性溶液中で強力な酸化剤
として働き、塩素イオンを塩素ガスとして気散ざける。
On the other hand, permanganate ions act as strong oxidizing agents in acidic solutions, dissipating chlorine ions as chlorine gas.

気散した塩素ガスは、空気ガス中の中性水蒸気ミスト中
でシアンの一部をシアン酸に分解する。また未分解のシ
アンもアルカリ溶液中に吸収され、次亜塩素酸により、
シアン酸に分解する。その時の反応式は次に示す如くな
る。
The diffused chlorine gas decomposes some of the cyanide into cyanic acid in the neutral water vapor mist in the air gas. In addition, undecomposed cyanide is absorbed into the alkaline solution, and hypochlorous acid
Decomposes into cyanic acid. The reaction formula at that time is as shown below.

CJ2+ 820 −+ HCf2+H(、e。CJ2+ 820 -+ HCf2+H (, e.

CN−+HIJO→CNα+OH− →哩 十HOCN シアン酸はpHを中性にすることでざらに分解され、炭
酸ガス、窒素ガスおよび水に分解される。
CN−+HIJO→CNα+OH− →哩 10HOCN Cyanic acid is roughly decomposed by making the pH neutral, and is decomposed into carbon dioxide gas, nitrogen gas, and water.

一方、シアンを気散・除去した重金属廃液は第1鉄イオ
ンを添加し、t)86以上で酸化する通常のフェライト
法により、処理が可能となる。この時、過剰に添加され
たマンカンはフェライト反応の妨害にはならない。
On the other hand, the heavy metal waste liquid from which cyanide has been diffused and removed can be treated by the usual ferrite method in which ferrous ions are added and oxidized at t) 86 or more. At this time, excessively added mankan does not interfere with the ferrite reaction.

[実施例] 次に本発明の実施例について説明する。[Example] Next, examples of the present invention will be described.

Fe 100mMI 、Cu 50mq/N 、Zn 
50mq#! 、全シアン3m(]/j’を含む模擬廃
水20(7!を500alt?パラプルフラスコに取り
、50%tt2SO4でDH1,5にした後、NarU
29、過マンガン酸カリウム19を加え、98°Cに加
熱しながら空気をo、57/minの速度で30分間通
気してシアンを気散・除去した。
Fe 100mMI, Cu 50mq/N, Zn
50mq#! , 20 (7!) of simulated wastewater containing 3 m(]/j' of total cyanide was taken into a 500 alt? Paraple flask, and after adjusting the DH to 1.5 with 50% tt2SO4, NarU
29. Potassium permanganate 19 was added, and while heating to 98°C, air was passed through at a rate of 57/min for 30 minutes to diffuse and remove cyanide.

廃液中の全シアンは0.05m’j/f!であった。The total cyanide in the waste liquid is 0.05 m'j/f! Met.

通気した後の空気を2 N NaOH50威に導入して
洗浄・回収を行った。その後、塩酸でpHを7.5〜7
.7に調整して60分間放置した。この溶液の全シアン
は0.1my/lであった。
The air after ventilation was introduced into 50% of 2N NaOH for washing and recovery. Then, adjust the pH to 7.5-7 with hydrochloric acid.
.. 7 and left for 60 minutes. The total cyanide in this solution was 0.1 my/l.

空気通気後の廃液にFeSO4・7t12011 ’j
を添加し、Na叶温溶液pHを9.5に保ち、温度65
°Cで空気を1 R/minの速度で通気してフェライ
ト反応を行った。90分間後、黒色の磁性体が得られ、
上澄水の分析を行うと、FeO,54#2以下、1ri
0.1mg/j以下、Cu 0.1mg/f!、全シア
ン0.01m’j/1以下であった。
FeSO4・7t12011'j in the waste liquid after air ventilation
was added, the pH of the Na leaf solution was kept at 9.5, and the temperature was 65.
The ferrite reaction was carried out at °C by passing air at a rate of 1 R/min. After 90 minutes, a black magnetic material was obtained,
Analysis of the supernatant water revealed that FeO, 54#2 or less, 1ri
0.1mg/j or less, Cu 0.1mg/f! , total cyan was less than 0.01 m'j/1.

以上のようにして効率よくシアン含有重金属廃水を処理
することができた。
As described above, cyanide-containing heavy metal wastewater could be efficiently treated.

[発明の効果] 以上説明したように、本発明によれば、シアンを含有す
る重金属廃水に対して、複雑な工程を要することなく、
効率の良いフェライト化処理か可能となる。さらに、従
来のように保存性の悪い次亜塩素酸ナトリウムを用いる
ことなく、NaCl!、K)In04等の安定で汎用性
のある試薬を用いてシアンを分解・除去することができ
るので工業的に有利でおる。
[Effects of the Invention] As explained above, according to the present invention, heavy metal wastewater containing cyanide can be treated without requiring complicated processes.
Efficient ferrite processing becomes possible. Furthermore, instead of using sodium hypochlorite, which has poor storage stability as in the past, NaCl! , K) It is industrially advantageous because cyanide can be decomposed and removed using a stable and versatile reagent such as In04.

Claims (1)

【特許請求の範囲】[Claims] (1)シアン含有重金属廃水に塩素イオンおよび過マン
ガン酸イオンを加え、pH2以下で加熱しながら通気し
てシアンを気散させた後、前記シアン含有通気ガスにつ
いては、前記ガスをアルカリ液中に導入してシアン成分
をシアン酸として回収した後、回収液のpHを7.5〜
8に保持して前記シアン酸を分解・除去し、残存重金属
廃水中の重金属については、前記廃水中に第1鉄イオン
を添加し、pH6以上で酸化して重金属イオンを含むス
ピネル化合物を作成することにより除去することを特徴
とするシアン含有重金属廃水の処理方法。
(1) Add chlorine ions and permanganate ions to cyanide-containing heavy metal wastewater, and diffuse cyanide by aeration while heating at pH 2 or below. After cyanide is introduced and the cyanide component is recovered as cyanic acid, the pH of the recovered solution is adjusted to 7.5 to 7.5.
8 to decompose and remove the cyanic acid, and for residual heavy metals in the wastewater, ferrous ions are added to the wastewater and oxidized at pH 6 or higher to create a spinel compound containing heavy metal ions. A method for treating cyanide-containing heavy metal wastewater, the method comprising removing heavy metal wastewater by removing cyanide.
JP18150688A 1988-07-22 1988-07-22 Treatment of heavy metal waste water containing cyanide Pending JPH0231888A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP18150688A JPH0231888A (en) 1988-07-22 1988-07-22 Treatment of heavy metal waste water containing cyanide

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP18150688A JPH0231888A (en) 1988-07-22 1988-07-22 Treatment of heavy metal waste water containing cyanide

Publications (1)

Publication Number Publication Date
JPH0231888A true JPH0231888A (en) 1990-02-01

Family

ID=16101954

Family Applications (1)

Application Number Title Priority Date Filing Date
JP18150688A Pending JPH0231888A (en) 1988-07-22 1988-07-22 Treatment of heavy metal waste water containing cyanide

Country Status (1)

Country Link
JP (1) JPH0231888A (en)

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