JP3246011B2 - Method for treating semiconductor manufacturing wastewater containing hydrogen peroxide - Google Patents

Method for treating semiconductor manufacturing wastewater containing hydrogen peroxide

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Publication number
JP3246011B2
JP3246011B2 JP32353092A JP32353092A JP3246011B2 JP 3246011 B2 JP3246011 B2 JP 3246011B2 JP 32353092 A JP32353092 A JP 32353092A JP 32353092 A JP32353092 A JP 32353092A JP 3246011 B2 JP3246011 B2 JP 3246011B2
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JP
Japan
Prior art keywords
hydrogen peroxide
catalase
semiconductor manufacturing
wastewater containing
containing hydrogen
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 - Fee Related
Application number
JP32353092A
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Japanese (ja)
Other versions
JPH06170355A (en
Inventor
博司 宮田
一郎 伊藤
哲朗 深瀬
孝男 沼倉
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Kurita Water Industries Ltd
Original Assignee
Kurita Water Industries Ltd
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Publication date
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Priority to JP32353092A priority Critical patent/JP3246011B2/en
Publication of JPH06170355A publication Critical patent/JPH06170355A/en
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Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】本発明は過酸化水素をカタラーゼ
により分解除去する過酸化水素を含む半導体製造排水の
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 semiconductor manufacturing wastewater containing hydrogen peroxide, which decomposes and removes hydrogen peroxide with catalase.

【0002】[0002]

【従来の技術】半導体製造工場から排出される排水には
過酸化水素を含むものがある。排水中に過酸化水素が含
まれていると、排水を処理する際に凝集沈殿汚泥の浮上
を引き起こしたり、またCOD源となる等の理由から、
過酸化水素を排水中から除去する必要がある。
2. Description of the Related Art Some wastewater discharged from a semiconductor manufacturing plant contains hydrogen peroxide. If hydrogen peroxide is contained in the wastewater, it may cause the flocculation and settling sludge to float when the wastewater is treated, or it may become a COD source.
It is necessary to remove hydrogen peroxide from wastewater.

【0003】従来、このような過酸化水素を含む排水中
の過酸化水素を除去するために、亜硫酸ナトリウム、亜
硫酸水素ナトリウム等の還元剤や、過酸化水素を特異的
に分解する酵素であるカタラーゼを用いた処理が行われ
ている。
Conventionally, in order to remove hydrogen peroxide in wastewater containing hydrogen peroxide, reducing agents such as sodium sulfite and sodium hydrogen sulfite, and catalase, an enzyme that specifically decomposes hydrogen peroxide, have been used. Is performed.

【0004】しかし、亜硫酸ナトリウムまたは亜硫酸水
素ナトリウムを使用する方法では、過酸化水素1モルに
対して1モルの亜硫酸ナトリウムまたは亜硫酸水素ナト
リウムが反応するので、大量の薬剤を添加する必要があ
り、このためコスト高になるとともに、塩類濃度が上昇
するという問題点がある。また変動する過酸化水素濃度
に応じて必要量の薬剤を添加するのが難しく、過剰に添
加すると残存する亜硫酸ナトリウムまたは亜硫酸水素ナ
トリウムが処理水のCOD値を上昇させるという問題点
もある。
However, in the method using sodium sulfite or sodium bisulfite, one mole of sodium sulfite or sodium bisulfite reacts with respect to 1 mole of hydrogen peroxide, so that it is necessary to add a large amount of a drug. Therefore, there is a problem that the cost increases and the salt concentration increases. In addition, it is difficult to add a required amount of a chemical according to the fluctuating hydrogen peroxide concentration, and there is also a problem that if added excessively, the remaining sodium sulfite or sodium hydrogen sulfite increases the COD value of the treated water.

【0005】カタラーゼを使用する方法は、カタラーゼ
が優れた生物触媒であり、常温での処理効率が非常に高
いという利点があるが、半導体製造工場より排出される
ウエハープロセス排水等にはフッ素イオン等のカタラー
ゼ阻害物質が含有されており、過酸化水素の分解速度が
大きく低下する場合がある。この対策として、フッ素イ
オンに耐性のあるカタラーゼを使用したり、アルカリ性
カルシウム化合物を添加して排水中のフッ素イオンをフ
ッ化カルシウムとして固液分離した後にカタラーゼと接
触させる方法が採用されている。しかし、フッ素イオン
を除去しても、カタラーゼが有効に作用しない場合があ
り、効率よく過酸化水素が除去できないという問題点が
ある。
The method using catalase has the advantage that catalase is an excellent biocatalyst and has a very high treatment efficiency at normal temperature. In some cases, the decomposition rate of hydrogen peroxide may be greatly reduced. As a countermeasure, a method of using catalase which is resistant to fluorine ions or a method of adding an alkaline calcium compound to solid-liquid separation of fluorine ions in waste water as calcium fluoride and then contacting with catalase is adopted. However, even if fluorine ions are removed, catalase may not work effectively, and there is a problem that hydrogen peroxide cannot be removed efficiently.

【0006】[0006]

【発明が解決しようとする課題】本発明の目的は、上記
問題点を解決するため、カタラーゼ阻害物質を含有する
排水においても、カタラーゼを有効に作用させて、簡単
に、しかも効率よく過酸化水素を分解除去できる過酸化
水素を含む半導体製造排水の処理方法を提案することで
ある。
SUMMARY OF THE INVENTION An object of the present invention is to solve the above-mentioned problems by simply making catalase act effectively even in wastewater containing a catalase inhibitor, so that hydrogen peroxide is easily and efficiently obtained. Of the present invention is to propose a method for treating semiconductor manufacturing wastewater containing hydrogen peroxide which can decompose and remove hydrogen.

【0007】[0007]

【課題を解決するための手段】通常のカタラーゼの作用
最適pHは中性付近にある(「化学大辞典」、共立出版
(株)、1987年2月15日発行、「カタラーゼ」の
項)。従って、カタラーゼ阻害物質を含まない排水を処
理する場合は、中性付近にpH調整すれば酵素活性には
ほとんど差はなく、カタラーゼにより過酸化水素を分解
できる。しかし、半導体製造排水を処理する場合、排水
をカタラーゼの作用最適pHに調整して処理してもカタ
ラーゼが有効に作用しない場合がある。この原因を調査
した結果、このような半導体製造排水にはカタラーゼ阻
害物質が含まれており、この阻害物質がカタラーゼを阻
害していることが判明した。さらに、このような阻害の
程度はpHにより大きく影響されることが判明した。本
発明者らはこのような知見に基づいて本発明を完成し
た。
The optimum pH for normal catalase action is around neutral ("Chemical Encyclopedia", published by Kyoritsu Shuppan Co., Ltd., February 15, 1987, "Catalase"). Therefore, when treating wastewater containing no catalase inhibitor, there is almost no difference in enzyme activity if the pH is adjusted to around neutrality, and hydrogen peroxide can be decomposed by catalase. However, when treating semiconductor manufacturing wastewater, catalase may not work effectively even if the wastewater is adjusted to the optimal pH for catalase action and treated. As a result of investigating the cause, it has been found that such a semiconductor manufacturing wastewater contains a catalase inhibitor, and this inhibitor inhibits catalase. Furthermore, it has been found that the degree of such inhibition is greatly affected by pH. The present inventors have completed the present invention based on such findings.

【0008】すなわち本発明は、過酸化水素を含む半導
体製造排水をカタラーゼと接触させて過酸化水素を分解
除去する排水の処理方法において、前記過酸化水素を含
む半導体製造排水をpHを9を越え11以下にpH調
整することを特徴とする過酸化水素を含む半導体製造排
水の処理方法である。
[0008] The present invention provides a method of treating a semiconductor manufacturing waste water is contacted with catalase to decompose and remove the hydrogen peroxide wastewater containing hydrogen peroxide, the semiconductor manufacturing waste water containing the hydrogen peroxide, the pH 9 A method for treating semiconductor manufacturing wastewater containing hydrogen peroxide, wherein the pH is adjusted to 11 or less .

【0009】本発明において処理の対象となる排水は、
半導体製造過程から排出され、過酸化水素のほかに、カ
タラーゼの酵素活性を阻害するカタラーゼ阻害物質を含
有する排水である。半導体製造過程で排出される排水中
に含まれるカタラーゼ阻害物質は、ヒドロキシルアミン
その他の還元物質であると認められる。本発明の処理方
法が適用できる過酸化水素を含む半導体製造排水の具体
的なものとして、半導体プロセス排水等の半導体製造工
場から排出される排水などがあげられる。
The wastewater to be treated in the present invention is:
Wastewater discharged from the semiconductor manufacturing process and containing, in addition to hydrogen peroxide, a catalase inhibitor that inhibits the enzyme activity of catalase. The catalase inhibitor contained in the wastewater discharged in the semiconductor manufacturing process is recognized to be hydroxylamine and other reducing substances. Specific examples of the semiconductor manufacturing wastewater containing hydrogen peroxide to which the treatment method of the present invention can be applied include wastewater discharged from a semiconductor manufacturing plant, such as semiconductor process wastewater.

【0010】本発明の処理方法は、被処理水をカタラー
ゼと接触させ、カタラーゼの酵素活性により被処理水中
の過酸化水素を分解する際、被処理水のpHを9を越え
11以下にpH調整して行う方法である。このようにカ
タラーゼの作用可能なpH範囲内であって、強アルカリ
性側のpHにおいてカタラーゼ処理することにより、阻
害物質による阻害の程度を大幅に軽減することができ
る。pHが9以下になると阻害軽減の程度が小さく、ま
た11を超えると、通常カタラーゼの作用可能なpH範
囲外となるため好ましくない。
In the treatment method of the present invention, when the water to be treated is brought into contact with catalase to decompose hydrogen peroxide in the water to be treated by the enzymatic activity of catalase, the pH of the water to be treated exceeds 9
In this method, the pH is adjusted to 11 or less . By performing catalase treatment in a pH range within which the catalase can operate and within a strongly alkaline pH range, the degree of inhibition by the inhibitor can be significantly reduced. If the pH is 9 or less , the degree of inhibition reduction is small, and if it exceeds 11, it is usually out of the pH range in which catalase can act, which is not preferable.

【0011】pHの調整はpH調整剤を被処理水中に添
加して行う。これはカタラーゼ処理する前に行うことも
できるし、カタラーゼ処理と同時に行うこともできる。
pH調整剤としては、水酸化ナトリウム、水酸化カリウ
ム、水酸化カルシウム等のアルカリ;塩酸、硫酸等の
酸;pH緩衝液などがあげられる。
The pH is adjusted by adding a pH adjuster to the water to be treated. This can be carried out before the catalase treatment or simultaneously with the catalase treatment.
Examples of the pH adjuster include alkalis such as sodium hydroxide, potassium hydroxide and calcium hydroxide; acids such as hydrochloric acid and sulfuric acid; and pH buffers.

【0012】カタラーゼ処理は公知の方法を採用でき、
例えば10万ユニット/mlのカタラーゼの場合、ほぼ
次の量のカタラーゼを添加して行うことができる。なお
1ユニットは過酸化水素濃度が150mg/lのとき、
30℃で1分間に1マイクロモルの過酸化水素を分解す
る酵素量である。
For the catalase treatment, a known method can be adopted.
For example, in the case of catalase of 100,000 units / ml, it can be carried out by adding approximately the following amount of catalase. One unit has a hydrogen peroxide concentration of 150 mg / l.
It is the amount of enzyme that decomposes 1 micromole of hydrogen peroxide per minute at 30 ° C.

【0013】被処理水中の過酸化水素濃度が10〜15
0mg/lのときの添加量:50mg/l、被処理水中
の過酸化水素濃度が150〜250mg/lのときの添
加量:100mg/l、被処理水中の過酸化水素濃度が
250〜500mg/lのときの添加量:300mg/
l以上。
The concentration of hydrogen peroxide in the water to be treated is 10 to 15
Addition amount at 0 mg / l: 50 mg / l, hydrogen peroxide concentration in the water to be treated is 150 to 250 mg / l, addition amount: 100 mg / l, hydrogen peroxide concentration in the water to be treated is 250 to 500 mg / l l when added: 300 mg /
l or more.

【0014】カタラーゼ添加時、水温は0〜50℃、好
ましくは25〜37℃とするのが望ましい。このような
条件においてカタラーゼの酵素活性は高くなる。
When adding catalase, the water temperature is preferably 0 to 50 ° C, preferably 25 to 37 ° C. Under such conditions, the enzymatic activity of catalase increases.

【0015】カタラーゼ添加した被処理水は、撹拌下に
5〜30分間、好ましくは10〜15分間反応させるこ
とにより、過酸化水素はカタラーゼにより分解除去され
る。このとき被処理水のpHは前記範囲に調整されてい
るので、阻害物質による阻害の程度は大幅に軽減されて
おり、このため効率よく過酸化水素の分解除去が行われ
る。
The water to be treated to which catalase has been added is reacted with stirring for 5 to 30 minutes, preferably 10 to 15 minutes, so that hydrogen peroxide is decomposed and removed by catalase. At this time, since the pH of the water to be treated is adjusted to the above range, the degree of inhibition by the inhibitor is greatly reduced, and therefore, hydrogen peroxide is efficiently decomposed and removed.

【0016】カタラーゼで過酸化水素を分解除去した後
は、例えば金属を除去するため、カルシウム化合物、ア
ルミニウム化合物、鉄化合物等の無機凝集剤および/ま
たはポリアクリルアミド等の高分子凝集剤などを添加し
て凝集沈殿処理を行うことができる。なお凝集剤として
アルミニウム塩、鉄塩等を用いた場合、凝集沈殿処理は
通常pH6.5〜7.5で行われるので、pHの再調整
が必要であるが、凝集剤として石灰等を用いる場合はさ
らに高いpH範囲で凝集処理が行われるので、pHの再
調整は必要なくなる。
After decomposing and removing hydrogen peroxide with catalase, for example, an inorganic coagulant such as a calcium compound, an aluminum compound or an iron compound and / or a polymer coagulant such as polyacrylamide are added to remove metals. To carry out the coagulation sedimentation process. When an aluminum salt, an iron salt, or the like is used as a coagulant, the coagulation and precipitation treatment is usually performed at a pH of 6.5 to 7.5, so it is necessary to readjust the pH. Since the coagulation treatment is performed in a higher pH range, it is not necessary to readjust the pH.

【0017】[0017]

【実施例】次に本発明の実施例について説明する。 比較例1 水道水に過酸化水素を150mg/lとなるように溶解
し、リン酸緩衝液および炭酸緩衝液でpHを表1に示す
値に調整した。これに栗田工業(株)製のカタラーゼ
クリバータK300(登録商標、酵素活性100000
ユニット/ml、最適pH6〜11)を50mg/lと
なるように添加し、30℃で過酸化水素の分解を行っ
た。5分後の反応速度(K)を下式より求めた。結果を
表1に示す。 ln(C/C0)=−Kt C0:初期過酸化水素濃度 C :t分後の過酸化水素濃度K :反応速度 t :時間(分)
Next, an embodiment of the present invention will be described. Comparative Example 1 Hydrogen peroxide was dissolved in tap water to a concentration of 150 mg / l, and the pH was adjusted to the value shown in Table 1 with a phosphate buffer and a carbonate buffer. Catalase manufactured by Kurita Water Industries Ltd.
Krivata K300 (registered trademark, enzyme activity 100000)
Unit / ml, optimal pH 6 to 11) was added at 50 mg / l, and hydrogen peroxide was decomposed at 30 ° C. The reaction rate (K) after 5 minutes was determined by the following equation. Table 1 shows the results. ln (C / C 0 ) = − Kt C 0 : initial hydrogen peroxide concentration C: hydrogen peroxide concentration after t minutes K: reaction rate t: time (minutes)

【0018】[0018]

【表1】 [Table 1]

【0019】表1から、水道水の場合は酵素の最適pH
であるpH6〜11の範囲で反応速度が速く(酵素活性
が高く)、特にpH6〜7でも反応速度が速く、pH6
〜11の範囲において反応速度にあまり差がないことが
わかる。pH5.5および11.5の場合は、酵素の最
適pHの範囲外なので反応速度が遅い。
From Table 1, the optimum pH of the enzyme for tap water
The reaction rate is high (enzyme activity is high) in the range of pH 6 to 11, which is particularly high.
It can be seen that there is not much difference in the reaction rate in the range of ~ 11. In the case of pH 5.5 and 11.5, the reaction rate is low because it is outside the range of the optimum pH of the enzyme.

【0020】実施例1 水道水の代りに半導体製造排水(過酸化水素含有量15
0mg/l、pH2.5)を用いて比較例1と同様にし
て反応速度を求めた。なおpHの調整は塩酸または水酸
化ナトリウムにより行った。結果を表2に示す。
Example 1 Instead of tap water, semiconductor manufacturing wastewater (having a hydrogen peroxide content of 15
0 mg / l, pH 2.5) in the same manner as in Comparative Example 1. The pH was adjusted with hydrochloric acid or sodium hydroxide. Table 2 shows the results.

【0021】[0021]

【表2】 [Table 2]

【0022】表2から、半導体製造排水の場合は酵素の
最適pHの範囲内であってもpH6〜7においては反応
速度が遅く、酵素が阻害されていることがわかる。とこ
ろがpH8〜11の範囲では、pH6〜7に比べて反応
速度は速く、阻害の程度が大幅に軽減されていることが
わかる。
From Table 2, it can be seen that, in the case of semiconductor manufacturing wastewater, the reaction rate is slow at pH 6 to 7 even within the optimum pH range of the enzyme, and the enzyme is inhibited. However, it can be seen that the reaction rate is higher in the pH range of 8 to 11 than in the pH range of 6 to 7, and the degree of inhibition is greatly reduced.

【0023】表1と表2の結果を比較すると、pH8〜
11の範囲においても表2の結果が表1の結果に比べて
小さくなっており、阻害が完全に取り除かれたわけでは
ないが、pH6〜7における落ち込みに比べればその程
度は小さく、特に10〜11の範囲において阻害の程度
が大幅に軽減されていることがわかる。
When the results in Tables 1 and 2 are compared, pH 8 to
In the range of 11, the results in Table 2 were smaller than those in Table 1, and the inhibition was not completely removed. However, the degree was smaller than the drop at pH 6 to 7, and the degree was particularly small, particularly 10 to 11 It can be seen that the extent of inhibition was significantly reduced in the range of.

【0024】実施例2 実施例1と同じ半導体製造排水に他の市販のカタラーゼ
を5000ユニット/liter添加し、比較例1と同様に
して反応速度を求めた。結果を表3に示す。
Example 2 Another commercially available catalase was added to the same semiconductor production waste water as in Example 1 at 5000 units / liter, and the reaction rate was determined in the same manner as in Comparative Example 1. Table 3 shows the results.

【0025】[0025]

【表3】 [Table 3]

【0026】[0026]

【発明の効果】以上の通り、本発明によれば、過酸化水
素を含む半導体製造排水をpHを9を越え11以下
調整してカタラーゼと接触させるようにしたので、簡単
で、しかも効率よく過酸化水素を分解除去できる。
As described above, according to the present invention, the semiconductor manufacturing wastewater containing hydrogen peroxide is brought into contact with catalase by adjusting the pH to more than 9 to 11 or less. Hydrogen peroxide can be decomposed and removed well.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 沼倉 孝男 東京都新宿区西新宿3丁目4番7号 栗 田工業株式会社内 (56)参考文献 特開 昭63−270595(JP,A) 特開 平2−222773(JP,A) 特開 昭60−175504(JP,A) 特開 平6−63531(JP,A) 特開 平6−86988(JP,A) 特開 昭58−6299(JP,A) 特開 昭64−11689(JP,A) 特開 平3−143598(JP,A) 特開 平3−86297(JP,A) (58)調査した分野(Int.Cl.7,DB名) C02F 1/00 C02F 1/58 ──────────────────────────────────────────────────続 き Continuation of front page (72) Inventor Takao Numakura 3-4-7 Nishishinjuku, Shinjuku-ku, Tokyo Kurita Kogyo Co., Ltd. (56) References JP-A-63-270595 (JP, A) JP-A-2-222773 (JP, A) JP-A-60-175504 (JP, A) JP-A-6-63531 (JP, A) JP-A-6-86988 (JP, A) JP-A-58-6299 (JP, A) JP-A-64-11689 (JP, A) JP-A-3-143598 (JP, A) JP-A-3-86297 (JP, A) (58) Fields investigated (Int. Cl. 7 , DB Name) C02F 1/00 C02F 1/58

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 過酸化水素を含む半導体製造排水をカタ
ラーゼと接触させて過酸化水素を分解除去する排水の処
理方法において、 前記過酸化水素を含む半導体製造排水をpHを9を越
11以下にpH調整することを特徴とする過酸化水素
を含む半導体製造排水の処理方法。
1. A method for treating wastewater that decomposes and removes hydrogen peroxide by bringing the semiconductor production wastewater containing hydrogen peroxide into contact with catalase, wherein the semiconductor production wastewater containing hydrogen peroxide has a pH of more than 9.
A method for treating semiconductor manufacturing wastewater containing hydrogen peroxide, wherein the pH is adjusted to 11 or less .
JP32353092A 1992-12-03 1992-12-03 Method for treating semiconductor manufacturing wastewater containing hydrogen peroxide Expired - Fee Related JP3246011B2 (en)

Priority Applications (1)

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JP32353092A JP3246011B2 (en) 1992-12-03 1992-12-03 Method for treating semiconductor manufacturing wastewater containing hydrogen peroxide

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP32353092A JP3246011B2 (en) 1992-12-03 1992-12-03 Method for treating semiconductor manufacturing wastewater containing hydrogen peroxide

Publications (2)

Publication Number Publication Date
JPH06170355A JPH06170355A (en) 1994-06-21
JP3246011B2 true JP3246011B2 (en) 2002-01-15

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JP3617544B2 (en) * 1994-11-10 2005-02-09 三菱瓦斯化学株式会社 Treatment method for wastewater containing hydrogen peroxide
JP4527896B2 (en) * 2001-03-26 2010-08-18 オルガノ株式会社 Wastewater treatment equipment
JP4132851B2 (en) * 2002-02-06 2008-08-13 オルガノ株式会社 Method for treating wastewater containing fluorine and hydrogen peroxide
JP4820663B2 (en) * 2006-02-22 2011-11-24 パナソニック環境エンジニアリング株式会社 Method and apparatus for treating hydrogen peroxide-containing waste liquid
JP6085155B2 (en) * 2012-11-27 2017-02-22 オルガノ株式会社 Ammonia-containing wastewater treatment apparatus and ammonia-containing wastewater treatment method
JP6368767B2 (en) * 2016-12-16 2018-08-01 オルガノ株式会社 Ammonia-containing wastewater treatment apparatus and ammonia-containing wastewater treatment method

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