JPH05123685A - Treatment of waste water containing organic coloring material - Google Patents

Treatment of waste water containing organic coloring material

Info

Publication number
JPH05123685A
JPH05123685A JP3507092A JP3507092A JPH05123685A JP H05123685 A JPH05123685 A JP H05123685A JP 3507092 A JP3507092 A JP 3507092A JP 3507092 A JP3507092 A JP 3507092A JP H05123685 A JPH05123685 A JP H05123685A
Authority
JP
Japan
Prior art keywords
radicals
organic dye
hydrogen peroxide
coloring material
waste water
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
JP3507092A
Other languages
Japanese (ja)
Inventor
Shin Hirayama
伸 平山
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.)
Mitsubishi Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy 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 Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP3507092A priority Critical patent/JPH05123685A/en
Publication of JPH05123685A publication Critical patent/JPH05123685A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To efficiently decolor waste water contg. org. coloring material without requiring the maintenance of a coloring material decomposing part of suspending the operation of an apparatus and to enable continuous economical operation by generating OH radicals in the waste water and decomposing the coloring material. CONSTITUTION:Free radicals of OH are generated in waste water contg. org. coloring material and this coloring material is decomposed. It has been made clear that this OH radical-generating system generates OH radicals according to a prescribed reaction formula and it is known that these OH radicals become active seeds. OH radicals and org. material react very rapidly with each other. The reaction mechanism of each OH radical is known as the cleavage of a double bond by the abstraction of H from an unsatd. bond or addition to a double bond or an arom. ring and OH radicals react with the chromophore of coloring materials by a similar mechanism to bring the coloring materials into oxidation decomposition.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は有機系色素含有廃水の処
理方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating organic dye-containing wastewater.

【0002】[0002]

【従来の技術】従来、有機系色素含有廃水の処理には
活性炭処理、過酸化水素添加処理及び紫外線照射処
理などが行われている。
2. Description of the Related Art Conventionally, activated carbon treatment, hydrogen peroxide addition treatment, ultraviolet irradiation treatment and the like have been carried out for treating organic dye-containing wastewater.

【0003】[0003]

【発明が解決しようとする課題】前記の活性炭処理は廃
水、廃液の処理を活性炭の吸着能力以上行うと、それ以
上の色素の吸着はできず、活性炭の再生処理が必要で、
その処理にはコストがかかり、しかも長時間を要し、そ
の処理によって装置の運転停止が必須であり連続的な処
理ができないという問題があった。また、運転停止を伴
わない処理としての過酸化水素の添加処理や紫外線照射
処理において、過酸化水素処理は単独では酸化力が弱い
ため廃水中の色素の分解は充分達成できず、また紫外線
照射処理は色素存在下では紫外線が色素自体に吸収さ
れ、液面内部まで透過しないため、廃水中の色素の分解
には限度があった。特に有機系色素の一種である難分解
性のフミン酸の分解は殆どできなかった。
In the above-mentioned activated carbon treatment, if the wastewater and the waste liquid are treated more than the adsorption capacity of the activated carbon, the dyes cannot be adsorbed further, and the activated carbon must be regenerated.
There is a problem in that the processing is costly and takes a long time, and the operation of the apparatus must be stopped due to the processing, and continuous processing cannot be performed. Also, in the hydrogen peroxide addition treatment and the ultraviolet irradiation treatment that do not involve shutdown, hydrogen peroxide treatment alone cannot achieve sufficient decomposition of the dye in the wastewater due to its weak oxidizing power. In the presence of a dye, ultraviolet rays are absorbed by the dye itself and do not penetrate to the inside of the liquid surface, so there was a limit to the decomposition of the dye in wastewater. In particular, almost no decomposition of humic acid, which is a kind of organic dye, is difficult to decompose.

【0004】本発明は、前記従来技術の有する問題点に
鑑み、廃水中のフミン酸を含め有機系色素を連続的、経
済的かつ高効率に分解することができる有機系色素含有
廃水の処理方法を提供しようとするものである。
In view of the above problems of the prior art, the present invention is a method for treating organic dye-containing wastewater capable of continuously, economically and highly efficiently decomposing organic dyes including humic acid in wastewater. Is to provide.

【0005】[0005]

【課題を解決するための手段】本発明は (1)有機系色素を含有する廃水中にOHラジカルを生
成して、該有機系色素を分解することを特徴とする有機
系色素含有廃水処理方法。
The present invention provides (1) a method for treating organic dye-containing wastewater, which comprises decomposing the organic dye by producing OH radicals in the wastewater containing the organic dye. ..

【0006】(2)有機系色素を含有する廃水中に過酸
化水素を添加するとともに、紫外線を照射してOHラジ
カルを生成させ、該有機系色素を分解することを特徴と
する有機系色素含有廃水処理方法。
(2) An organic dye-containing material characterized by decomposing the organic dye by adding hydrogen peroxide to waste water containing the organic dye and irradiating ultraviolet rays to generate OH radicals. Wastewater treatment method.

【0007】(3)有機系色素を含有する廃水中に二酸
化チタン粉末を添加するとともに、紫外線を照射してO
Hラジカルを生成させ、該有機系色素を分解することを
特徴とする有機系色素含有廃水処理方法。
(3) Titanium dioxide powder is added to waste water containing an organic dye, and ultraviolet rays are radiated to produce O.
A method for treating organic dye-containing wastewater, which comprises generating H radicals and decomposing the organic dye.

【0008】(4)有機系色素を含有する廃水中に過酸
化水素を添加するとともに、2価の鉄イオンを含む化合
物または1価の銅イオンを含む化合物を添加し、紫外線
を照射してOHラジカルを生成させ、該有機系色素を分
解することを特徴とする有機系色素含有廃水処理方法。
である。
(4) Hydrogen peroxide is added to waste water containing an organic dye, a compound containing a divalent iron ion or a compound containing a monovalent copper ion is added, and ultraviolet rays are applied to OH. A method for treating organic dye-containing wastewater, which comprises generating radicals to decompose the organic dye.
Is.

【0009】本発明におけるOHラジカル発生の手段と
しては、例えば過酸化水素に鉄、銅やアスコルビン酸や
EDTA等のキレート剤を添加したり、過酸化水素に紫
外線を照射させたり、二酸化チタン(アナターゼ型)に
紫外線を照射させたりするものである。
Examples of means for generating OH radicals in the present invention include adding a chelating agent such as iron, copper, ascorbic acid and EDTA to hydrogen peroxide, irradiating hydrogen peroxide with ultraviolet rays, and titanium dioxide (anatase). The mold) is irradiated with ultraviolet rays.

【0010】[0010]

【作用】本発明で使用されるOHラジカル発生系は、次
のような反応式によってOHラジカルが発生することが
明らかにされている。
In the OH radical generating system used in the present invention, it has been clarified that OH radicals are generated by the following reaction formula.

【化1】 [Chemical 1]

【0011】これらの*OHが活性種となることが知ら
れている。このラジカル(遊離基)と有機物の反応は極
めて速い。OHラジカルの反応機構は不飽和結合のHの
ひき抜きによる二重結合の開裂反応や、二重結合や芳香
核への付加反応が知られており、同様な機構において、
色素発色団と反応し色素の酸化分解効果を発揮する。以
下に本発明の実施例について説明する。
It is known that these * OH are active species. The reaction of these radicals (free radicals) and organic substances is extremely fast. The reaction mechanism of the OH radical is known to be a cleavage reaction of a double bond by removing H of an unsaturated bond and an addition reaction to a double bond or an aromatic nucleus.
It reacts with the dye chromophore and exerts the oxidative decomposition effect of the dye. Examples of the present invention will be described below.

【0012】[0012]

【実施例】【Example】

(実施例1)実施例として、フェニルメタン系色素であ
るブリリアントグリーンとメチレンブルーを選定し、分
解試験を実施した。特にメチレンブルーは印刷時によく
用いられる色素である。試験結果の代表例として、過酸
化水素に紫外線を照射してOHラジカルを発生させた系
について以下に説明する。
(Example 1) As an example, phenylmethane dyes Brilliant Green and Methylene Blue were selected and a decomposition test was carried out. In particular, methylene blue is a dye often used at the time of printing. As a representative example of the test results, a system in which hydrogen peroxide is irradiated with ultraviolet rays to generate OH radicals will be described below.

【0013】(1)試験方法 ブリリアントグリーンとメチレンブルーの色度の指標と
して吸光度の極大吸収点を指標とした。 (a)ブリリアントグリーンはO.D630nm 、メチレン
ブルーはO.D660nm を色度の指標に決定した。 (b)用いる過酸化水素濃度:0.5mM、紫外線:キ
セノン−水銀ランプを光源とする紫外線照射装置、光源
と色素含有液との距離35mmを基本条件に決定し、色
素分解評価試験を行った。 (c)OHラジカルの検出は電子スピン共鳴装置(ES
R)によるスピントラップ法によった。
(1) Test Method The maximum absorption point of the absorbance was used as an index of the chromaticity of brilliant green and methylene blue. (A) Brilliant green is O. D 630nm , methylene blue is O.D. D 660 nm was determined as an index of chromaticity. (B) Hydrogen peroxide concentration used: 0.5 mM, ultraviolet rays: an ultraviolet irradiation device using a xenon-mercury lamp as a light source, a distance of 35 mm between the light source and the dye-containing liquid was determined as a basic condition, and a dye decomposition evaluation test was performed. .. (C) OH radicals can be detected by electron spin resonance (ES)
R) according to the spin trap method.

【0014】(2)評価試験結果 過酸化水素に紫外線を照射して、OHラジカルが生じる
か否かを調べた。 (a)過酸化水素に紫外線を照射してOHラジカルを発
生している条件を検討の上求めた。OHラジカルの代表
的なESRシグナルを図1に示した。 (b)過酸化水素単独、紫外線単独および過酸化水素+
紫外線の各条件下で色素の分解・漂白試験を実施し処理
時間毎に吸光度を測定した。その結果を図2と図3に示
した。なお、過酸化水素は光や容器に混在する金属によ
り分解するため、ポリエチレン容器に調製、ストックし
たものを使用した。
(2) Evaluation Test Results Hydrogen peroxide was irradiated with ultraviolet rays to examine whether or not OH radicals were generated. (A) It was determined after examining the conditions under which hydrogen peroxide was irradiated with ultraviolet rays to generate OH radicals. A typical ESR signal of OH radical is shown in FIG. (B) Hydrogen peroxide alone, ultraviolet light alone and hydrogen peroxide +
A dye decomposition / bleaching test was carried out under each condition of ultraviolet rays, and the absorbance was measured at each treatment time. The results are shown in FIGS. 2 and 3. Since hydrogen peroxide decomposes due to light and metals mixed in the container, a polyethylene container prepared and stocked was used.

【0015】図2はブリリアントグリーンの分解結果で
あるが、紫外線単独では色度増加の逆効果がある。ま
た、過酸化水素単独では吸光度に変化はなく、全く分解
されない。一方、過酸化水素+紫外線のOHラジカル発
生条件下では、30分で約60%が分解され、さらに6
0分処理では、約96%の分解が可能である。
FIG. 2 shows the result of decomposition of brilliant green, and UV alone has the opposite effect of increasing chromaticity. In addition, when hydrogen peroxide is used alone, the absorbance does not change and is not decomposed at all. On the other hand, under the condition of OH radical generation of hydrogen peroxide + ultraviolet rays, about 60% is decomposed in 30 minutes, and
With 0 minute treatment, about 96% decomposition is possible.

【0016】図3はメチレンブルーの分解例であるが、
紫外線単独では30分において約4%の分解しかおこら
ない。また過酸化水素単独では全く分解がおこらない
が、過酸化水素+紫外線の条件下では30分処理では約
65%が分解され、さらに60分処理では、約95%が
分解可能である。 (c)OHラジカル消去剤として知られているエタノー
ルを過酸化水素+紫外線の系に添加すると、メチレンブ
ルーの分解はほぼ完全に抑制され、本法の作用がOHラ
ジカルによることが確認された(図3参照)。
FIG. 3 shows an example of decomposition of methylene blue.
UV light alone decomposes only about 4% in 30 minutes. Further, although hydrogen peroxide alone does not decompose at all, under the condition of hydrogen peroxide + ultraviolet ray, about 65% can be decomposed by the treatment for 30 minutes and about 95% can be decomposed by the treatment for 60 minutes. (C) When ethanol, which is known as an OH radical scavenger, was added to the system of hydrogen peroxide + ultraviolet rays, the decomposition of methylene blue was almost completely suppressed, and it was confirmed that the action of this method was due to OH radicals (Fig. 3).

【0017】また、他のOHラジカル発生系である二酸
化チタンに紫外線を照射する系についての色素分解結果
を図4に示した。その評価色素として、ブリリアントグ
リーンを用いた。
FIG. 4 shows the result of dye decomposition in another system in which titanium dioxide, which is an OH radical generating system, is irradiated with ultraviolet rays. Brilliant green was used as the evaluation dye.

【0018】2mlのブリリアントグリーン溶液中に3
mgの二酸化チタンを入れて、紫外線を照射し、その分
解作用を反応時間毎に調べた。同様に二酸化チタンの
み、紫外線のみの試験を行った。図4から、二酸化チタ
ン、紫外線照射条件下で色素の分解が顕著で、20分で
約53%の色度低下が生じたことがわかる。
3 in 2 ml brilliant green solution
Titanium dioxide (mg) was added, and the titanium dioxide was irradiated with ultraviolet rays, and the decomposition action was examined every reaction time. Similarly, only titanium dioxide and ultraviolet rays were tested. From FIG. 4, it can be seen that the decomposition of the dye was remarkable under the conditions of irradiation with titanium dioxide and ultraviolet rays, and a decrease in chromaticity of about 53% occurred in 20 minutes.

【0019】(実施例2)実施例として、フミン酸をア
ルカリ溶液下で可溶化させた後、水で一定の色度に調製
したものを分解試験に用いた。試験結果の代表例とし
て、過酸化水素にFeを添加し、紫外線を照射してOH
ラジカルを発生させた系について主として以下に説明す
る。
Example 2 As an example, humic acid was solubilized in an alkaline solution and then prepared with water to a certain chromaticity, and used in a decomposition test. As a typical example of the test results, Fe is added to hydrogen peroxide, and ultraviolet rays are irradiated to OH.
The system in which radicals are generated will be mainly described below.

【0020】(1)試験方法 フミン酸の色度の指標として吸光度の極大吸収に近い点
を指標とした。 (a)フミン酸はO.D400nmを色度の指標に決定し
た。 (b)用いる過酸化水素濃度:2.5mM、用いるFe
SO4・7H2O濃度:10μM、紫外線:キセノン−水
銀ランプを光源とする紫外線照射装置、光源と色素含有
液との距離:35mmを基本条件に決定し、フミン酸分
解評価試験を行った。 (c)OHラジカルの検出は電子スピン共鳴装置(ES
R)によるスピントラップ法によった。
(1) Test method As an index of chromaticity of humic acid, a point close to the maximum absorption of absorbance was used as an index. (A) Humic acid is O. D400 nm was determined as an index of chromaticity. (B) Hydrogen peroxide concentration used: 2.5 mM, Fe used
SO 4 · 7H 2 O concentration: 10 [mu] M, UV: Xenon - ultraviolet irradiation apparatus according to a mercury lamp light source, the light source and the distance between the dye-containing solution: a 35mm determines the basic conditions and subjected to humic acid degradation evaluation test. (C) OH radicals can be detected by electron spin resonance (ES)
R) according to the spin trap method.

【0021】(2)評価試験結果 過酸化水素にFeを添加し、紫外線を照射して、OHラ
ジカルがより効率的に生じるかどうかを検討した。 (a)過酸化水素に紫外線を照射した系と、さらにFe
を加えた系におけるOHラジカル発生の相対量を比較し
て図5に示した。これによると過酸化水素+Fe+紫外
線の系が効率よくOHラジカルを発生させることが確認
された。 (b)過酸化水素単独、紫外線単独、過酸化水素+紫外
線および過酸化水素+紫外線+Feの各条件下でフミン
酸の分解・漂白試験を実施、処理時間毎に吸光度を測定
した。その結果を図6に示した。なお、過酸化水素は光
や容器に混在する金属により分解するため、ポリエチレ
ン容器に調製、ストックしたものを使用した。
(2) Evaluation test results Fe was added to hydrogen peroxide and irradiated with ultraviolet rays to examine whether or not OH radicals were generated more efficiently. (A) A system in which hydrogen peroxide is irradiated with ultraviolet rays, and further Fe
The relative amount of OH radical generation in the system to which is added is compared and shown in FIG. According to this, it was confirmed that the system of hydrogen peroxide + Fe + ultraviolet efficiently generates OH radicals. (B) A humic acid decomposition / bleaching test was carried out under the conditions of hydrogen peroxide alone, ultraviolet light alone, hydrogen peroxide + ultraviolet and hydrogen peroxide + ultraviolet + Fe, and the absorbance was measured at each treatment time. The results are shown in Fig. 6. Since hydrogen peroxide decomposes due to light and metals mixed in the container, a polyethylene container prepared and stocked was used.

【0022】図6はフミン酸の分解結果であるが、過酸
化水素単独、紫外線単独では120分処理後でもフミン
酸の分解は生じない。また、過酸化水素+紫外線の系で
は、120分後に約26%のフミン酸分解が生じたに過
ぎない。これに対し、過酸化水素+Fe+紫外線の系で
は、120分後の分解率は74%に達し、Fe添加によ
ってOHラジカル発生効率を上げた系では高い分解効率
を発揮することを確認している。
FIG. 6 shows the result of decomposition of humic acid. However, hydrogen peroxide alone and ultraviolet light alone do not decompose humic acid even after 120 minutes of treatment. Further, in the system of hydrogen peroxide + ultraviolet rays, about 120% of humic acid decomposition occurred only after 120 minutes. On the other hand, in the system of hydrogen peroxide + Fe + ultraviolet, the decomposition rate after 120 minutes reached 74%, and it was confirmed that the system in which the OH radical generation efficiency was increased by adding Fe exhibited high decomposition efficiency.

【0023】本発明者は、使用する過酸化水素の濃度を
上げることで、フミン酸分解に要する時間を短縮するこ
とを確認した。
The present inventor has confirmed that the time required for humic acid decomposition can be shortened by increasing the concentration of hydrogen peroxide used.

【0024】上記実施例では2価鉄イオンを含む化合物
であるFeSO4・7H2Oを使用したが、1価銅イオン
を含む化合物である臭化銅、塩化銅、ロダン銅を用いて
も同様の結果が得られた。
Although FeSO 4 .7H 2 O, which is a compound containing divalent iron ions, was used in the above-mentioned examples, the same applies when compounds such as copper bromide, copper chloride, and copper rhodanide containing monovalent copper ions are used. The result was obtained.

【0025】以上、特定の有機系色素の処理についての
実施例により本発明の効果を立証したが、本発明者は他
のOHラジカル発生系においても同様に、多くの有機系
色素の分解が生じ、OHラジカルによる有機系色素の分
解が有効であることを確認した。
As described above, the effect of the present invention was proved by the examples of treatment of specific organic dyes. However, the present inventor similarly decomposes many organic dyes in other OH radical generating systems. It was confirmed that decomposition of organic dyes by OH radicals was effective.

【0026】[0026]

【発明の効果】本発明によれば、OHラジカルを効率的
に発生させることにより、有機系色素、特にフミン酸の
分解・脱色が可能となり、色素分解部分のメンテを必要
とせず装置運転の停止を伴わずして、高効率で色素を
分解脱色でき、しかも、操作は連続的かつ経済的に行
うことができる効果を奏する。
EFFECTS OF THE INVENTION According to the present invention, by efficiently generating OH radicals, organic dyes, especially humic acid, can be decomposed and decolorized, and maintenance of the device can be stopped without requiring maintenance of the dye decomposition part. It is possible to decompose and decolorize the dye with high efficiency without the need for, and to perform the operation continuously and economically.

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

【図1】過酸化水素に紫外線を照射してOHラジカルの
発生を確認する電子スピン共鳴装置のシグナル図表。
FIG. 1 is a signal diagram of an electron spin resonance apparatus for confirming the generation of OH radicals by irradiating hydrogen peroxide with ultraviolet rays.

【図2】紫外線照射、過酸化水素添加及び過酸化水素+
紫外線照射によるブリリアントグリーンの分解率を示す
図表
[Figure 2] UV irradiation, hydrogen peroxide addition and hydrogen peroxide +
Chart showing decomposition rate of Brilliant Green by UV irradiation

【図3】紫外線照射、過酸化水素添加及び過酸化水素+
紫外線照射によるメチレンブルーの分解率を示す図表
[Figure 3] UV irradiation, hydrogen peroxide addition and hydrogen peroxide +
Chart showing the decomposition rate of methylene blue by UV irradiation

【図4】二酸化チタン添加、紫外線照射及び二酸化チタ
ン+紫外線照射によるブリリアントグリーンの分解率を
示す図表
FIG. 4 is a graph showing the decomposition rate of brilliant green by the addition of titanium dioxide, ultraviolet irradiation, and titanium dioxide + ultraviolet irradiation.

【図5】過酸化水素+紫外線照射及び過酸化水素+Fe
+紫外線照射によるOHラジカル発生量の比較図。
Fig. 5 Hydrogen peroxide + UV irradiation and hydrogen peroxide + Fe
+ Comparison diagram of the amount of OH radicals generated by UV irradiation.

【図6】過酸化水素単独、紫外線照射単独、過酸化水素
+紫外線照射、過酸化水素+Fe+紫外線照射のフミン
酸の分解率を示す図表。
FIG. 6 is a chart showing the decomposition rate of humic acid by hydrogen peroxide alone, ultraviolet irradiation alone, hydrogen peroxide + ultraviolet irradiation, hydrogen peroxide + Fe + ultraviolet irradiation.

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 有機系色素を含有する廃水中にOHラジ
カルを生成して、該有機系色素を分解することを特徴と
する有機系色素含有廃水処理方法。
1. A method for treating organic dye-containing wastewater, which comprises generating OH radicals in wastewater containing an organic dye to decompose the organic dye.
【請求項2】 有機系色素を含有する廃水中に過酸化水
素を添加するとともに、紫外線を照射してOHラジカル
を生成させ、該有機系色素を分解することを特徴とする
有機系色素含有廃水処理方法。
2. An organic dye-containing wastewater, characterized in that hydrogen peroxide is added to wastewater containing an organic dye and OH radicals are generated by irradiation with ultraviolet rays to decompose the organic dye. Processing method.
【請求項3】 有機系色素を含有する廃水中に二酸化チ
タン粉末を添加するとともに、紫外線を照射してOHラ
ジカルを生成させ、該有機系色素を分解することを特徴
とする有機系色素含有廃水処理方法。
3. An organic dye-containing wastewater, characterized by adding titanium dioxide powder to wastewater containing an organic dye, and irradiating ultraviolet rays to generate OH radicals to decompose the organic dye. Processing method.
【請求項4】 有機系色素を含有する廃水中に過酸化水
素を添加するとともに、2価の鉄イオンを含む化合物ま
たは1価の銅イオンを含む化合物を添加し、紫外線を照
射してOHラジカルを生成させ、該有機系色素を分解す
ることを特徴とする有機系色素含有廃水処理方法。
4. An OH radical is obtained by adding hydrogen peroxide to waste water containing an organic dye, adding a compound containing a divalent iron ion or a compound containing a monovalent copper ion, and irradiating with ultraviolet rays. Is generated and the organic dye is decomposed, and an organic dye-containing wastewater treatment method is characterized.
JP3507092A 1991-09-10 1992-02-21 Treatment of waste water containing organic coloring material Pending JPH05123685A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP3507092A JPH05123685A (en) 1991-09-10 1992-02-21 Treatment of waste water containing organic coloring material

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
JP3-230063 1991-09-10
JP23006391 1991-09-10
JP3507092A JPH05123685A (en) 1991-09-10 1992-02-21 Treatment of waste water containing organic coloring material

Publications (1)

Publication Number Publication Date
JPH05123685A true JPH05123685A (en) 1993-05-21

Family

ID=26373980

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3507092A Pending JPH05123685A (en) 1991-09-10 1992-02-21 Treatment of waste water containing organic coloring material

Country Status (1)

Country Link
JP (1) JPH05123685A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2012017862A (en) * 2010-07-06 2012-01-26 Hitachi Appliances Inc Refrigerator
CN102701318A (en) * 2012-06-12 2012-10-03 常州大学 Device and method for removing humic acid in potable water
CN105776414A (en) * 2016-04-15 2016-07-20 东南大学 Device for removing nitrogenous substances in water jointly with AG/TiO2 and humic acid

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2012017862A (en) * 2010-07-06 2012-01-26 Hitachi Appliances Inc Refrigerator
CN102701318A (en) * 2012-06-12 2012-10-03 常州大学 Device and method for removing humic acid in potable water
CN105776414A (en) * 2016-04-15 2016-07-20 东南大学 Device for removing nitrogenous substances in water jointly with AG/TiO2 and humic acid

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