JPH1057974A - Treatment of iron-cyanide complex containing cyanic waste water - Google Patents

Treatment of iron-cyanide complex containing cyanic waste water

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Publication number
JPH1057974A
JPH1057974A JP21460396A JP21460396A JPH1057974A JP H1057974 A JPH1057974 A JP H1057974A JP 21460396 A JP21460396 A JP 21460396A JP 21460396 A JP21460396 A JP 21460396A JP H1057974 A JPH1057974 A JP H1057974A
Authority
JP
Japan
Prior art keywords
cyanide
iron
waste water
oxidizing agent
wastewater
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
JP21460396A
Other languages
Japanese (ja)
Inventor
Kishiyun Abe
阿部  貴春
Toshihiro Abe
智弘 安部
Hiroyuki Imamura
博幸 今村
Hiroji Miyagawa
博治 宮川
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.)
Mitsui Petrochemical Industries Ltd
Original Assignee
Mitsui Petrochemical Industries 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 Mitsui Petrochemical Industries Ltd filed Critical Mitsui Petrochemical Industries Ltd
Priority to JP21460396A priority Critical patent/JPH1057974A/en
Publication of JPH1057974A publication Critical patent/JPH1057974A/en
Pending legal-status Critical Current

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  • Physical Water Treatments (AREA)
  • Removal Of Specific Substances (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)

Abstract

PROBLEM TO BE SOLVED: To treat a cyanide in a waste water to low concn. by irradiating the waste water with UV rays to visible rays after adding an alkali agent and an oxidizing agent to a cyanic waste water containing an iron-cyanide complex, adjusting pH alkaline and oxidizing a free cyanide while separating and removing a precipitate from the waste water. SOLUTION: The cyanic waste water is irradiated with UV rays to visible rays in a reactor 16 provided with a light source 15 after adding the alkali agent to the cyanic waste water containing the iron-cyanide complex from an alkali agent feed device 12 to adjust pH adding the oxidizing agent from an oxidizing agent feed device 13. In this way, a decomposition and oxidation treatment of the iron-cyanide complex is allowed to progress by a two step reaction. That is, at the first step reaction, the iron-cyanide complex is executed by light energy to be decomposed to a free cyanide and iron ion. At the second step reaction, the free cyanide is oxidized with the oxidizing agent supplied from the oxidizing agent feed device 13 to convert it into a carbonate and nitrogen. The waste water with cyanide compd. decomposed and oxidized is discharged from a discharge pipe 17 as a treated water.

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、表面加工処理を行
うめっき工場、写真現像等で発生する難分解性な鉄シア
ン錯体化合物を含有する廃水の処理方法に関するが、産
業廃棄物処理から洩れた洩水あるいは、汚染水に含まれ
る鉄シアン錯体化合物の処理方法も可能である。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating wastewater containing a hardly decomposable iron cyanide complex compound generated in a plating factory for performing surface processing, photographic development, etc., but leaked from industrial waste treatment. A method for treating iron cyanide complex compounds contained in leaked water or contaminated water is also possible.

【0002】[0002]

【従来の技術】金属の表面加工処理を行うめっき工場や
化学、石油、ガス工業等において発生するシアン化合物
を含有する廃水(シアン廃水)は、シアン化合物が生態
系に強い悪影響を及ぼすため、そのまま放出することは
できない。そのため、シアン廃水はシアン化合物の除去
を行い、国の環境排出基準値以下にし、無害化してから
下水等に放出する必要がある。一般的に遊離シアンまた
はそれを生成しやすいシアン化合物は酸化処理が容易で
ある。そのようなシアン廃水の処理方法は、アルカリに
調整した後で次亜塩素酸ナトリウム等の塩素系の酸化剤
を用いて酸化処理を行うアルカリ塩素法が一般的な処理
方法として実用化されている。しかしながら、遊離シア
ン等と異なり、化学的に安定な構造を持つ鉄シアン錯体
化合物を含有するシアン廃水の処理には、上記のアルカ
リ塩素法では酸化剤の酸化力が弱く、通常酸化処理が困
難である。このような難分解性の鉄シアン錯体化合物を
含有するシアン廃水の処理方法として、シアン廃水に紫
外線〜可視光線を照射し、鉄シアン錯体化合物を酸化処
理が容易な遊離シアンと鉄イオンに分解し、その遊離シ
アンを酸化剤によって酸化処理する方法が行われてい
る。
2. Description of the Related Art Wastewater containing cyanide (cyanide wastewater) generated in plating factories that perform metal surface treatment and in the chemical, petroleum, and gas industries, etc., has a strong adverse effect on ecosystems because cyanide has a strong adverse effect on ecosystems. It cannot be released. Therefore, it is necessary to remove the cyanide from the cyanide wastewater, make it below the national standard for environmental emissions, detoxify the wastewater, and discharge it to sewage. Generally, free cyanide or a cyan compound which easily produces it is easily oxidized. As a method for treating such cyan wastewater, an alkali chlorine method of performing an oxidation treatment using a chlorine-based oxidizing agent such as sodium hypochlorite after adjusting to alkali has been put to practical use as a general treatment method. . However, unlike the free cyanide and the like, in the treatment of cyanide wastewater containing an iron cyanide complex compound having a chemically stable structure, the oxidizing power of the oxidizing agent is weak in the above-mentioned alkali chlorine method, and the oxidation treatment is usually difficult. is there. As a method of treating cyan waste water containing such a hardly decomposable iron cyan complex compound, the cyan waste water is irradiated with ultraviolet to visible light to decompose the iron cyan complex compound into free cyanide and iron ions which are easily oxidized. A method of oxidizing the free cyanide with an oxidizing agent has been used.

【0003】〔図1〕に、従来より行われている酸化剤
の存在下のもとで、紫外線〜可視光線を照射して鉄シア
ン錯体化合物を分解および酸化処理を実施するための装
置を示す(以後、従来法と呼ぶ)。3は酸化剤供給装
置、6は紫外線〜可視光線の光源5を備えた反応槽、1
はシアン廃水の供給配管、7は処理水の放出配管であ
る。1のシアン廃水の供給配管を介して送入されてきた
シアン廃水を、3の酸化剤供給装置から供給された酸化
剤と共に反応槽6へ送入し、紫外線〜可視光線を照射す
る。鉄シアン錯体化合物の分解および酸化処理は一般的
に2段反応で進行する。すなわち、1段目の反応では、
鉄シアン錯体化合物は照射された光エネルギーによって
励起され、酸化処理が容易な遊離シアンと鉄イオンに分
解される。2段目の反応では、かくして分解によって生
成した遊離シアンは3の酸化剤供給装置から供給された
酸化剤によって酸化され、炭酸塩と窒素へと変換され
る。シアン化合物を分解および酸化処理された廃水は、
7の処理水の放出配管へ放出される。酸化剤が処理水に
残存している場合は、必要に応じて工業的に使用されて
いる処理方法で別途処理を行う。
FIG. 1 shows a conventional apparatus for decomposing and oxidizing an iron cyanide complex by irradiating ultraviolet to visible light in the presence of an oxidizing agent. (Hereinafter referred to as the conventional method). 3 is an oxidant supply device, 6 is a reaction vessel equipped with a light source 5 for ultraviolet to visible light, 1
Is a supply pipe for cyan wastewater, and 7 is a discharge pipe for treated water. The cyan wastewater sent through the supply pipe of cyan wastewater 1 is sent to the reaction tank 6 together with the oxidant supplied from the oxidant supply device 3 and irradiated with ultraviolet to visible light. The decomposition and oxidation treatment of the iron cyanide complex compound generally proceeds in a two-stage reaction. That is, in the first-stage reaction,
The iron cyanide complex compound is excited by the irradiated light energy and is decomposed into free cyanide and iron ions which are easily oxidized. In the second-stage reaction, the free cyanide thus generated by the decomposition is oxidized by the oxidizing agent supplied from the oxidizing agent supply device 3 and converted into carbonate and nitrogen. Wastewater that has undergone decomposition and oxidation treatment of cyanide
The treated water is discharged to the discharge pipe of No. 7. If the oxidizing agent remains in the treated water, it is separately treated as required by a treatment method used industrially.

【0004】しかしながら、本発明者らが検討したとこ
ろによると、上記の従来法で鉄シアン錯体化合物を分解
および酸化処理を行う方法では、1段反応において鉄シ
アン錯体から解離した鉄イオンは溶解性の低い水酸化物
などの微細な沈澱物を形成する。その微細な沈澱物は広
範囲の波長の光エネルギーを吸収する。1段目の反応の
進行に伴って微細な沈澱物が増加すると、光エネルギー
の吸収量が増加し、遊離シアン生成に消費される光エネ
ルギーが減少することを見いだした。ゆえに、処理の進
行に伴い、1段目の反応の鉄シアン錯体化合物から遊離
シアンへの分解は遅くなる。例えば、〔表1〕に示す比
較例は、従来法における処理方法で、鉄シアン錯体化合
物を含有するシアン廃水に、過酸化水素を添加して処理
を行った結果である。シアン化合物の分解処理速度は、
シアン化合物の分解処理の進行に伴って、きわめて遅く
なっているのがわかる。また、この条件で廃水中のシア
ン化合物の濃度を環境排出基準値以下である1mg/L
以下まで処理するには、光エネルギーのコストが大幅に
増加するので経済的な処理方法ではない。
However, according to the study by the present inventors, in the above-described method of decomposing and oxidizing an iron cyanide compound by the conventional method, iron ions dissociated from the iron cyanide complex in a one-step reaction are soluble. Form fine precipitates, such as low hydroxides. The fine precipitate absorbs a wide range of wavelengths of light energy. It was found that when the amount of fine precipitates increased with the progress of the first-stage reaction, the amount of light energy absorbed increased, and the light energy consumed for the production of free cyan decreased. Therefore, as the treatment proceeds, the decomposition of the iron cyanide complex compound into free cyan in the first-stage reaction is delayed. For example, the comparative example shown in [Table 1] is a result obtained by adding hydrogen peroxide to cyan wastewater containing an iron cyanide complex compound and performing the treatment by the conventional treatment method. The decomposition rate of cyanide is
It can be seen that the progress has been extremely slow with the progress of the decomposition treatment of the cyanide compound. Further, under this condition, the concentration of the cyanide in the wastewater is adjusted to 1 mg / L which is equal to or less than the environmental emission standard value.
Processing below is not an economical processing method because the cost of light energy is greatly increased.

【0005】[0005]

【発明が解決しようとする課題】本発明の目的は、鉄シ
アン錯体化合物の分解に利用される光エネルギーの有効
利用率を高度に保持した状態で、廃水中のシアン濃度を
低濃度まで処理を可能にした鉄シアン錯体化合物含有シ
アン廃水の新しい処理技術を提供することにある。
SUMMARY OF THE INVENTION An object of the present invention is to reduce the cyanide concentration in wastewater to a low concentration while maintaining the effective utilization of light energy used for the decomposition of the iron cyanide complex compound at a high level. It is an object of the present invention to provide a new treatment technology of cyan wastewater containing an iron cyanide complex compound.

【0006】[0006]

【課題を解決するための手段】本発明者らは、従来法に
おいて鉄シアン錯体化合物から解離した鉄イオンが微細
な水酸化物などの沈澱物を生成させ、その沈澱物が光エ
ネルギーを吸収することで、シアン化合物の分解処理を
遅くさせている比較例のごとき新奇な知見から、以下に
記す本発明に至った。すなわち本発明は、(1) 鉄シ
アン錯体化合物含有シアン廃水に予め、アルカリ剤と酸
化剤を添加し、pHをアルカリに調整した後、紫外線〜
可視光線を照射し、鉄シアン錯体化合物の分解によって
解離した鉄イオンから生成する水酸化物等の沈澱物を廃
水中から随時分離除去しながら遊離シアンの酸化処理を
行うことを特徴とする廃水処理方法、(2) 鉄シアン
錯体化合物含有シアン廃水のpHが、7.5以上12以
下であることを特徴とする(1)記載の方法、(3)
酸化剤としてオゾンを含有する気体もしくは過酸化水素
を含有する水溶液もしくは塩素系酸化剤を用いることを
特徴とする(1)記載の方法である。
SUMMARY OF THE INVENTION The present inventors have found that iron ions dissociated from an iron cyanide complex compound in the conventional method form fine precipitates such as hydroxides, and the precipitates absorb light energy. Thus, the present invention described below has been made from novel findings such as Comparative Examples in which the decomposition treatment of the cyanide is delayed. That is, the present invention provides (1) an alkali agent and an oxidizing agent which are added in advance to an iron-cyan complex compound-containing cyanine wastewater, and the pH is adjusted to alkali;
Wastewater treatment characterized by oxidizing free cyanide while irradiating visible light and separating and removing precipitates such as hydroxides generated from iron ions dissociated by decomposition of the iron cyanide complex compound from wastewater as needed. Method (2) The method according to (1), wherein the pH of the cyanide wastewater containing the iron cyanide complex compound is 7.5 or more and 12 or less, (3)
The method according to (1), wherein a gas containing ozone, an aqueous solution containing hydrogen peroxide, or a chlorine-based oxidizing agent is used as the oxidizing agent.

【0007】1段目の反応で解離した鉄イオンから生成
する水酸化物等の沈澱物を廃水中から随時分離除去しな
がら遊離シアンの酸化処理を行うために、予め、鉄シア
ン錯体化合物含有シアン廃水にアルカリ剤と酸化剤を添
加し、pHをアルカリに調整する。紫外線〜可視光線の
照射による1段目の反応で鉄シアン錯体から解離した鉄
イオンはかくして水酸化物等の沈澱物を形成する。この
水酸化物等の沈澱物を廃水中から随時分離除去しながら
処理を行うことで、1段目の反応における紫外線〜可視
光線の光エネルギーの有効利用を損なわずに処理が行
え、かつ、廃水中のシアン化合物の濃度を低濃度まで処
理できるのである。
[0007] In order to oxidize free cyanide while separating and removing precipitates such as hydroxides generated from iron ions dissociated in the first stage reaction from wastewater as needed, a cyanide containing an iron cyanide complex compound must be prepared in advance. An alkaline agent and an oxidizing agent are added to the wastewater to adjust the pH to alkaline. The iron ions dissociated from the iron cyanide complex in the first-stage reaction by irradiation of ultraviolet light to visible light thus form a precipitate such as a hydroxide. By performing treatment while separating and removing precipitates such as hydroxides from wastewater as needed, the treatment can be performed without impairing the effective use of light energy from ultraviolet to visible light in the first-stage reaction, and It is possible to process the cyanide in the medium down to a low concentration.

【0008】[0008]

【発明の実施の形態】以下、本発明を実施する装置の一
例の概略図を示す〔図2〕にもとづいて説明する。12
はアルカリ剤供給装置、13は酸化剤供給装置、14は
ラインミキサー、16は紫外線〜可視光線の光源15を
備えた反応槽、18は濾過装置、11はシアン廃水の供
給配管、17は処理水の放出配管である。11のシアン
廃水の供給配管を介して送入された鉄シアン錯体化合物
を含有するシアン廃水に予め、12のアルカリ剤供給装
置によりpHを好ましくは7.5以上12以下に調整
し、酸化剤を添加した後で、シアン廃水に紫外線〜可視
光線を照射する。鉄シアン錯体化合物の分解および酸化
処理は2段反応で進行する。1段目の反応では、鉄シア
ン錯体化合物は照射された光エネルギーによって励起さ
れ、酸化処理が容易な遊離シアンと鉄イオンに分解され
る。鉄イオンから生成した水酸化物等の沈澱物は、18
の濾過装置によって、随時濾別除去される。濾過装置は
フィルタープレス、砂濾過等、工業的に使用される装置
で良く、また、濾布等のポアサイズは数ミクロンから数
十ミクロン程度で良い。2段目の反応では、分解によっ
て生成した遊離シアンが13の酸化剤供給装置から供給
された酸化剤によって酸化され、炭酸塩(炭酸ガス)と
窒素へと変換される。かくしてシアン化合物を分解およ
び酸化処理された廃水は、17の処理水の放出配管へ放
出される。ここで酸化剤としては、オゾンを含有する気
体、過酸化水素を含有する水溶液、次亜塩素酸ソーダ、
過酸化ソーダなどの塩素系酸化剤が挙げられ、特にオゾ
ンを含有する気体、過酸化水素を含有する水溶液が好ま
しい。酸化剤が処理水に残存している場合は、必要に応
じて工業的に使用されている公知の処理方法により別途
処理を行う。
BRIEF DESCRIPTION OF THE DRAWINGS FIG. 1 is a schematic diagram showing an example of an apparatus for carrying out the present invention. 12
Is an alkali agent supply device, 13 is an oxidant supply device, 14 is a line mixer, 16 is a reaction tank provided with a light source 15 for ultraviolet to visible light, 18 is a filtration device, 11 is a supply pipe for cyan wastewater, and 17 is treated water. Discharge pipe. The pH of the cyan waste water containing the iron cyan complex compound fed through the supply pipe of the cyan waste water of No. 11 is preferably adjusted to 7.5 or more and 12 or less in advance with the alkali agent supply device of 12 to adjust the oxidizing agent. After the addition, the cyan wastewater is irradiated with ultraviolet to visible light. The decomposition and oxidation treatment of the iron cyanide complex compound proceeds in a two-stage reaction. In the first-stage reaction, the iron-cyan complex compound is excited by the irradiated light energy and decomposed into free cyanide and iron ions, which are easily oxidized. Precipitates such as hydroxides formed from iron ions are 18
Is optionally filtered off. The filtration device may be a device used industrially, such as a filter press or sand filtration, and the pore size of the filter cloth or the like may be several microns to several tens microns. In the second-stage reaction, free cyan generated by the decomposition is oxidized by the oxidizing agent supplied from the 13 oxidizing agent supply devices, and is converted into carbonate (carbon dioxide) and nitrogen. The wastewater in which the cyanide has been decomposed and oxidized is discharged to the discharge pipe for the 17 treated water. Here, as the oxidizing agent, a gas containing ozone, an aqueous solution containing hydrogen peroxide, sodium hypochlorite,
A chlorine-based oxidizing agent such as sodium peroxide may be mentioned, and a gas containing ozone and an aqueous solution containing hydrogen peroxide are particularly preferable. When the oxidizing agent remains in the treated water, it is separately treated as necessary by a known treatment method used industrially.

【0009】上記処理方法は連続式ではあるが、この方
法に限定されず、回分式等で行うこともできる。すなわ
ち、〔図3〕に本発明の実施例と比較例を実施した装置
の概略図を示す。〔表1〕に示す本発明の実施例1、2
および比較例は回分式で行ったテストの結果である。以
下、光源25(1kWの中圧水銀灯ランプ)を備えた反
応槽26に、鉄シアン錯体化合物を含有するシアン廃水
をシアン廃水の供給配管21から送入して、アルカリ剤
供給装置22からアルカリ剤を添加しpHを調整して、
酸化剤を酸化剤供給装置23より添加した後、撹拌装置
30で撹拌しながら、紫外線を照射した。また、処理中
は水酸化物の沈澱物が廃水中に析出するので処理中の廃
水をポンプで循環し、随時濾過装置28で濾別除去しな
がら、鉄シアン錯体化合物の分解および酸化処理工程を
行った。アルカリ剤としては、アルカリ金属、アルカリ
土類金属、アンモニウムを含む公知のアルカリ剤が用い
られる。濾別除去のための濾材は日本ポール社製のフィ
ルターカートリッジ(ポアサイズ10ミクロン)を使用
した。なお、比較例は上記の水酸化物等の沈澱物の濾別
除去操作を行わないで、光源25(1kWの中圧水銀灯
ランプ)を備えた反応槽26に鉄シアン錯体化合物を含
有するシアン廃水を送入して酸化剤を添加した後、撹拌
しながら、紫外線を照射して鉄シアン錯体化合物の分解
および酸化処理工程を行った場合である。
Although the above-mentioned processing method is a continuous method, it is not limited to this method, but may be a batch method or the like. That is, FIG. 3 shows a schematic view of an apparatus embodying the embodiment of the present invention and the comparative example. Examples 1 and 2 of the present invention shown in Table 1
And Comparative Examples are the results of tests performed in a batch system. Hereinafter, cyan wastewater containing an iron cyan complex compound is fed into a reaction tank 26 equipped with a light source 25 (1 kW medium-pressure mercury lamp) from a supply pipe 21 of cyan wastewater, and an alkali agent is supplied from an alkali agent supply device 22. To adjust the pH,
After the oxidizing agent was added from the oxidizing agent supply device 23, the mixture was irradiated with ultraviolet rays while being stirred by the stirring device 30. Also, during the treatment, the precipitate of hydroxide precipitates in the wastewater, so that the wastewater during the treatment is circulated by a pump, and is filtered and removed by a filtration device 28 as needed. went. As the alkali agent, a known alkali agent containing an alkali metal, an alkaline earth metal, and ammonium is used. A filter cartridge (pore size: 10 microns) manufactured by Pall Corporation was used as a filter medium for removal by filtration. In the comparative example, the cyan wastewater containing the iron cyan complex compound was placed in a reaction tank 26 equipped with a light source 25 (1 kW medium-pressure mercury lamp) without performing the filtration and removal operation of the precipitates such as hydroxides. , An oxidizing agent was added thereto, and then ultraviolet irradiation was performed with stirring to decompose and oxidize the iron cyanide complex compound.

【0010】[0010]

【実施例】【Example】

(実施例1)シアン濃度として120mg/Lあるフェ
ロシアン化カリウムを含有するシアン廃水に水酸化ナト
リウム溶液を添加し、pHを9に調整し、過酸化水素を
1000mg/Lになるように添加し、紫外線を照射し
て鉄シアン錯体化合物の分解および酸化処理工程を行っ
た。反応時間に対する残留シアン濃度を、サンプリング
口29より採取し、測定した。その結果を〔表1〕に示
す。
(Example 1) A sodium hydroxide solution was added to cyan wastewater containing potassium ferrocyanide having a cyan concentration of 120 mg / L, the pH was adjusted to 9, hydrogen peroxide was added to 1000 mg / L, and ultraviolet light was added. To decompose and oxidize the iron cyanide complex compound. The residual cyan concentration with respect to the reaction time was sampled from the sampling port 29 and measured. The results are shown in [Table 1].

【0011】(実施例2)シアン濃度として120mg
/Lあるフェロシアン化カリウムを含有するシアン廃水
に水酸化ナトリウム溶液を添加し、pHを11に調整
し、次亜塩素酸ナトリウムを1000mg/Lになるよ
うに添加し、紫外線を照射して鉄シアン錯体化合物の分
解および酸化処理工程を行った。
(Embodiment 2) Cyan concentration of 120 mg
/ L: Add sodium hydroxide solution to cyan wastewater containing potassium ferrocyanide, adjust pH to 11, add sodium hypochlorite to 1000 mg / L, irradiate ultraviolet rays Compound decomposition and oxidation treatment steps were performed.

【0012】(比較例)シアン濃度として102mg/
Lあるフェロシアン化カリウムを含有するシアン廃水中
に過酸化水素を1000mg/Lになるように添加し、
紫外線を照射して鉄シアン錯体化合物の分解および酸化
処理工程を行った。
(Comparative Example) A cyan concentration of 102 mg /
L: Add hydrogen peroxide to cyan wastewater containing potassium ferrocyanide at a concentration of 1000 mg / L;
Irradiation with ultraviolet light was performed to decompose and oxidize the iron cyanide complex compound.

【0013】[0013]

【表1】 [Table 1]

【0014】本発明の処理方法である実施例−1、2と
従来法の処理方法である比較例とを比較すると本発明を
用いることにより、光エネルギーの有効利用を損なわず
にシアン化合物の分解および酸化処理の処理速度を格段
に向上させることが解る。また、シアン化合物の残留濃
度も0.1mg/Lまで容易に処理することができる。
A comparison between Examples 1 and 2, which are the processing method of the present invention, and a Comparative Example, which is a conventional processing method, shows that the use of the present invention makes it possible to decompose the cyan compound without impairing the effective use of light energy. It can be seen that the processing speed of the oxidation treatment is remarkably improved. In addition, the residual concentration of the cyanide can be easily reduced to 0.1 mg / L.

【0015】[0015]

【発明の効果】本発明は鉄シアン錯体化合物を含有する
シアン廃水の新しい処理技術を提供するものであり、鉄
シアン錯体化合物の処理の途中で生成した水酸化物等の
沈澱物を随時濾別除去することで、鉄シアン錯体化合物
を遊離シアンと鉄イオンに分解するための光エネルギー
の有効利用を損なわず、かつ、廃水中のシアン濃度を低
濃度まで効率よく処理することができる。
Industrial Applicability The present invention provides a new technology for treating cyanide wastewater containing an iron cyanide complex compound. The precipitate such as a hydroxide formed during the treatment of the iron cyanide complex compound is optionally filtered off. By removing it, the effective use of light energy for decomposing the iron cyanide complex compound into free cyanide and iron ions is not impaired, and the cyanide concentration in the wastewater can be efficiently treated to a low concentration.

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

【図1】従来の方法を実施するための装置を示す説明図FIG. 1 is an explanatory view showing an apparatus for implementing a conventional method.

【図2】本発明の方法を実施するための装置を示す説明
FIG. 2 is an explanatory diagram showing an apparatus for performing the method of the present invention.

【図3】実施例、比較例を実施した装置を示す説明図FIG. 3 is an explanatory view showing an apparatus in which an example and a comparative example are implemented.

【符号の説明】[Explanation of symbols]

1 シアン廃水の供給配管 3 酸化剤供給装置 5 光源 6 紫外線〜可視光線の光源を備えた反応槽 7 処理水の放出配管 11 シアン廃水の供給配管 12 アルカリ剤供給装置 13 酸化剤供給装置 14 ラインミキサー 15 光源 16 紫外線〜可視光線の光源を備えた反応槽 17 処理水の放出配管 18 濾過装置 21 シアン廃水の供給配管 22 アルカリ剤供給装置 23 酸化剤供給装置 25 光源 26 紫外線〜可視光線の光源を備えた反応槽 27 処理水の放出配管 28 濾過装置 29 サンプリング口 30 撹拌装置 31 撹拌羽根 REFERENCE SIGNS LIST 1 supply pipe for cyan wastewater 3 oxidant supply apparatus 5 light source 6 reaction tank provided with a light source for ultraviolet to visible light 7 discharge pipe for treated water 11 supply pipe for cyan wastewater 12 alkali agent supply apparatus 13 oxidant supply apparatus 14 line mixer Reference Signs List 15 light source 16 reaction tank provided with ultraviolet to visible light source 17 treated water discharge pipe 18 filtration device 21 cyan wastewater supply pipe 22 alkaline agent supply device 23 oxidant supply device 25 light source 26 equipped with ultraviolet to visible light source Reaction tank 27 treated water discharge pipe 28 filtration device 29 sampling port 30 stirring device 31 stirring blade

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 C02F 1/78 ZAB C02F 1/78 ZAB (72)発明者 宮川 博治 神奈川県横浜市栄区笠間町1190番地 三井 東圧化学株式会社内──────────────────────────────────────────────────続 き Continuation of the front page (51) Int.Cl. 6 Identification code Agency reference number FI Technical display location C02F 1/78 ZAB C02F 1/78 ZAB (72) Inventor Hiroharu Miyagawa Kasama-cho, Sakae-ku, Yokohama, Kanagawa Prefecture 1190 Mitsui Toatsu Chemical Co., Ltd.

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 鉄シアン錯体化合物含有シアン廃水に予
め、アルカリ剤と酸化剤を添加し、pHをアルカリに調
整した後、紫外線〜可視光線を照射し、鉄シアン錯体化
合物の分解によって解離した鉄イオンから生成する水酸
化物等の沈澱物を廃水中から随時分離除去しながら遊離
シアンの酸化処理を行うことを特徴とする廃水処理方
法。
1. An iron and cyanide complex-containing cyanide wastewater is added with an alkali agent and an oxidizing agent in advance to adjust the pH to alkali, and then irradiated with ultraviolet to visible light to dissociate iron by decomposition of the iron cyanide complex compound. A wastewater treatment method comprising oxidizing free cyanide while separating and removing precipitates such as hydroxides generated from ions from wastewater as needed.
【請求項2】 鉄シアン錯体化合物含有シアン廃水のp
Hが、7.5以上12以下であることを特徴とする請求
項1記載の方法。
2. A p-cyanide wastewater containing an iron-cyan complex compound
2. The method according to claim 1, wherein H is not less than 7.5 and not more than 12.
【請求項3】 酸化剤としてオゾンを含有する気体もし
くは過酸化水素を含有する水溶液もしくは塩素系酸化剤
を用いることを特徴とする請求項1記載の方法。
3. The method according to claim 1, wherein a gas containing ozone, an aqueous solution containing hydrogen peroxide or a chlorine-based oxidizing agent is used as the oxidizing agent.
JP21460396A 1996-08-14 1996-08-14 Treatment of iron-cyanide complex containing cyanic waste water Pending JPH1057974A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP21460396A JPH1057974A (en) 1996-08-14 1996-08-14 Treatment of iron-cyanide complex containing cyanic waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP21460396A JPH1057974A (en) 1996-08-14 1996-08-14 Treatment of iron-cyanide complex containing cyanic waste water

Publications (1)

Publication Number Publication Date
JPH1057974A true JPH1057974A (en) 1998-03-03

Family

ID=16658454

Family Applications (1)

Application Number Title Priority Date Filing Date
JP21460396A Pending JPH1057974A (en) 1996-08-14 1996-08-14 Treatment of iron-cyanide complex containing cyanic waste water

Country Status (1)

Country Link
JP (1) JPH1057974A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5739443A (en) * 1996-04-01 1998-04-14 Saunders; Roger I. Carrier for a monitoring device
JP2006341229A (en) * 2005-06-10 2006-12-21 Sumitomo Precision Prod Co Ltd Advanced treating method of cyanide compound-containing drain
JP2011212578A (en) * 2010-03-31 2011-10-27 Ube Industries Ltd Wastewater treatment apparatus
JP2012157798A (en) * 2011-01-31 2012-08-23 Jfe Steel Corp Method for treating cyanide-containing wastewater

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5739443A (en) * 1996-04-01 1998-04-14 Saunders; Roger I. Carrier for a monitoring device
JP2006341229A (en) * 2005-06-10 2006-12-21 Sumitomo Precision Prod Co Ltd Advanced treating method of cyanide compound-containing drain
JP2011212578A (en) * 2010-03-31 2011-10-27 Ube Industries Ltd Wastewater treatment apparatus
JP2012157798A (en) * 2011-01-31 2012-08-23 Jfe Steel Corp Method for treating cyanide-containing wastewater

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