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JP4508311B2 - Adjustment method of ozone concentration - Google Patents
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JP4508311B2 - Adjustment method of ozone concentration - Google Patents

Adjustment method of ozone concentration Download PDF

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JP4508311B2
JP4508311B2 JP14699199A JP14699199A JP4508311B2 JP 4508311 B2 JP4508311 B2 JP 4508311B2 JP 14699199 A JP14699199 A JP 14699199A JP 14699199 A JP14699199 A JP 14699199A JP 4508311 B2 JP4508311 B2 JP 4508311B2
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ozone
concentration
water
containing water
glass
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JP2000334468A (en
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和己 塚本
博志 森田
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Kurita Water Industries Ltd
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Kurita Water Industries Ltd
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Description

【0001】
【発明の属する技術分野】
本発明は、オゾン濃度の低減方法及び調整方法に関する。さらに詳しくは、本発明は、オゾンを含有する排水の処理において、メンテナンスを必要とすることなく、溶存オゾン濃度を低減することができるオゾン濃度の低減方法、及び、電子材料などのウエット洗浄工程において、ユースポイントに所望の溶存オゾン濃度のオゾン含有水を容易に供給することができるオゾン濃度の調整方法に関する。
【0002】
【従来の技術】
半導体用シリコン基板、液晶用ガラス基板、フォトマスク用石英基板などの電子材料の表面から、微粒子、有機物、金属などを除去することは、製品の品質と歩留まりを確保する上で極めて重要である。この目的のために、いわゆるRCA洗浄法と呼ばれる過酸化水素をベースとする濃厚薬液による高温でのウエット洗浄が行われ、アンモニアと過酸化水素水の混合溶液(APM)や塩酸と過酸化水素水の混合溶液(HPM)などが用いられていた。これらの洗浄方法を採用した場合の多大な薬液コスト、リンス用の超純水のコスト、廃液処理コスト、薬品蒸気を排気し新たに清浄空気を作る空調コストなどを低減し、さらに水の大量使用、薬物の大量廃棄、排ガスの放出などの環境への負荷を低減するために、近年ウエット洗浄工程の見直しが進められている。
本発明者らは、先に純水にオゾンを溶解した電子材料洗浄用のガス溶解洗浄水を開発した。純水にオゾンを溶解した洗浄水は、溶存オゾン濃度が数mg/リットル程度の低濃度でありながら、極めて高い酸化力を発揮し、電子材料表面に付着した有機物や金属などの不純物による汚染を除去する工程や、シリコン基板の表面を均一に酸化してケミカル酸化膜層を形成する工程で活用されている。純水にオゾンを溶解した洗浄水は、残留性がないので被洗浄物の表面を清浄に保ち、また、オゾンの分解又は除去により再び高純度の水となり、再利用できるという利点も有する。しかし、オゾンを溶解した洗浄水は、溶存オゾンが経時的に自己分解して酸素となるために、オゾン濃度の維持管理が容易ではない。
これに対し、本発明者らは、オゾン含有ガスと純水とを通水配管内で混合しつつ供給することにより、溶存オゾン濃度の低下が抑制されることを見いだし、オゾン濃度がほぼ一定したオゾン含有水を供給するシステムを開発した。すなわち、オゾン発生器でオゾンと酸素の混合ガスを製造し、オゾン溶解装置において純水中に送り込む。オゾンと酸素の混合ガスは、純水と混合して気液混合状態となり、オゾンが溶解してオゾン含有水が生成し、さらに気液混合状態のまま通水配管の中を流れる。水中に溶解したオゾンは、自己分解により経時的に酸素に変化していくが、自己分解による溶存オゾンの減少分は、気相中のオゾンが水中に溶解することにより補われるので、水中のオゾン濃度をほぼ一定に保つことができる。しかし、このシステムによっても、オゾン含有水をユースポイントへ導く分岐配管が複雑な配管経路を経由すると、オゾン濃度が低下する場合がある。また、ユースポイントによって、オゾン濃度の異なるオゾン含有水が必要とされる場合もある。
特開平10−57907号公報には、一定濃度のオゾン水を安定的に供給し得る方法として、オゾン水製造手段で得られるオゾン水の供給量を、オゾン水の最大吐出量よりも高く設定し、オゾン水タンク内のオゾン水量が常時一定範囲になるように制御する方法が提案されている。しかし、このような方法では、制御が複雑で、大がかりな設備が必要となる。
半導体や液晶などの電子産業で使われるオゾン含有水は、オゾン以外の不純物に関しては非常に高い純度が要求されている。さらに、医薬品工業、食料品工業などの分野でも、オゾン含有水は、洗浄殺菌などに広く利用されているが、高い純度を保持したまま溶存オゾン濃度を調整する方法がほとんどないのが現状であり、容易に所望濃度のオゾン含有水を得ることができるオゾン濃度の調整方法が求められている。
一方、ユースポイントで使用されたオゾン含有水にもオゾンが残留しており、ユースポイントで使用されなかったオゾン含有水と同様に、活性炭、紫外線照射装置、触媒などを用いてオゾンの分解処理が行われている。しかし、紫外線照射は設備費と処理コストが高く、活性炭と触媒は劣化するために、定期的に交換が必要である。
【0003】
【発明が解決しようとする課題】
本発明は、オゾンを含有する排水の処理において、メンテナンスを必要とすることなく、溶存オゾン濃度を低減することができるオゾン濃度の低減方法、及び、電子材料などのウエット洗浄工程において、ユースポイントに所望の溶存オゾン濃度のオゾン含有水を容易に供給することができるオゾン濃度の調整方法を提供することを目的としてなされたものである。
【0004】
【課題を解決するための手段】
本発明者らは、上記の課題を解決すべく鋭意研究を重ねた結果、オゾン含有水をガラスと接触させることにより、溶存するオゾンの自己分解が促進されてオゾン濃度が低減し、さらに、オゾン含有水とガラスとの接触条件を選定することにより、オゾンの分解量を制御して所望濃度のオゾン含有水を得ることが可能となることを見いだし、この知見に基づいて本発明を完成するに至った。
すなわち、本発明は、
(1)使用予定の破砕ガラスを使用予定の破砕ガラス充填カラムに充填して、破砕ガラスの充填量及び破砕ガラスの粒径を変更して、使用予定の濃度のオゾン含有水を使用予定の通水速度で通水して、破砕ガラス充填カラム通過後のオゾン含有水のオゾン濃度を測定し、破砕ガラス充填カラム通過後のオゾン含有水のオゾン濃度が、所望の低減オゾン濃度になったときの破砕ガラスの充填量及び破砕ガラスの粒径において、使用予定の濃度のオゾン含有水を充填カラムの破砕ガラスと接触させ、所望の低減オゾン濃度のオゾン含有水とすることを特徴とするオゾン含有水のオゾン濃度の調整方法、及び、
(2)超純水タンクより、ポンプによって超純水を使用予定の通水速度でエジェクターに送り同時に、オゾンと酸素の混合ガスを該混合ガスの供給量を変更してエジェクターに吹き込み、破砕ガラス充填カラム通過前のオゾン含有水のオゾン濃度を測定して、使用予定のオゾン濃度になったときの混合ガスの供給量でエジェクターに吹き込むことにより、使用予定のオゾン濃度のオゾン含有水を、破砕ガラス充填カラムに通水する第(1)項記載のオゾン含有水のオゾン濃度の調整方法、
を提供するものである。
【0005】
【発明の実施の形態】
本発明のオゾン濃度の低減方法は、オゾン含有水をガラスと接触させるものであり、本発明のオゾン濃度の調整方法は、オゾン含有水をガラスと接触させて所望濃度のオゾン含有水とするものである。オゾン含有水をガラスと接触させることにより、オゾン含有水中の溶存オゾンの自己分解が促進されるので、オゾン含有排水などをガラスと接触させることにより、メンテナンスを必要とすることなく、溶存オゾン濃度を低減することができる。また、電子材料の洗浄工程などにおいて、ユースポイントにおける所望濃度以上のオゾンを溶解したオゾン含有水を製造し、ユースポイント近傍においてガラスと接触させ、溶存オゾン量を所望濃度まで低下させることができる。
本発明方法に用いるガラスの種類に特に制限はなく、例えば、ソーダ石灰ガラス、カリ石灰ガラス、ホウケイ酸ガラス、鉛ガラス、アルミノケイ酸塩ガラス、ホウ酸塩ガラス、リン酸塩ガラス、アルミン酸塩ガラス、チタン酸塩ガラス、フッ化物ガラス、カルコゲンガラスなどを挙げることができる。これらの中で、水及び酸に対する化学的耐久性に優れたホウケイ酸ガラスを好適に用いることができる。
本発明方法に用いるガラスの形状に特に制限はなく、例えば、板ガラス、ガラス管、ガラスビーズ、ガラス繊維などを挙げることができる。本発明方法において、オゾン含有水とガラスを接触させる方法に特に制限はなく、例えば、オゾン含有水の通水経路の一部の接液材質をガラスとすることにより、オゾン含有水をガラスに接触させることができ、あるいは、オゾン含有水の通水経路に破砕したガラスを充填した容器を設置することにより、オゾン含有水をガラスに接触させることもできる。これらの中で、ガラスを数mm角程度に破砕した破砕ガラスは、取り扱いが容易であり、表面積が大きいので、好適に使用することができる。
【0006】
本発明のオゾン濃度の調整方法によれば、オゾン溶解装置において、純水に過剰のオゾンを溶解させ、ユースポイントにおいて使用される前に、オゾン含有水をガラスに接触させてオゾンの自己分解を促進し、オゾン含有水の濃度を容易に調整することができる。また、同様な手段により、オゾン含有排水中の溶存オゾン濃度を容易に低減することができる。すなわち、オゾン含有水とガラスの接触において、接触させるガラスの表面積、接触時間などを選定することにより、容易かつ正確にオゾン含有水の濃度を調整することができる。オゾン含有水と接触させるガラスの量を多くする、破砕ガラスの粒径を小さくする、通水速度を遅くするなどの手段により、オゾンの分解量を増大することができる。本発明方法の実施に当たっては、使用予定の破砕ガラスを用いて、ガラス充填量とオゾン分解量との関係、ガラス粒径とオゾン分解量との関係、通水速度とオゾン分解量との関係などを予め実験的に求めておき、低減すべきオゾン量に応じて任意の因子を制御することにより、所望のオゾン濃度とすることができる。また、オゾン分解量はオゾン含有水のオゾン濃度にも影響されるので、ガラスとの接触条件とオゾン分解量の関係を把握する場合、オゾン含有水のオゾン濃度を変化させて実験することが好ましい。
本発明方法によれば、電子材料工場などにおけるオゾン含有水の供給系において、オゾン含有水製造装置とオゾン含有水のユースポイントとの間に、破砕ガラスを充填した容器などを設けることにより、高濃度のオゾン含有水の溶存オゾン濃度を低減して、容易に所望濃度のオゾン含有水とすることができる。ガラスとの接触の間に、オゾン含有水が汚染されることがあってはならないので、オゾン含有水を通水する配管は、異物の溶出が極めて少なく、酸化力の強いオゾンとも反応しない、フッ素樹脂製のチューブなどを用いることが好ましい。同様に、破砕ガラスを充填する容器も、耐オゾン性の高い部材であることが好ましい。破砕ガラスを充填する容器自体を、ガラス製とすることもできる。
【0007】
本発明方法において、オゾン含有水をガラスと接触させることによりオゾンの自己分解が促進される機構は明確ではないが、ガラスに混入している微量の金属が作用しているものと推定される。しかし、その金属は、ガラスからの溶出はほとんどなく、分析を行っても検出限界以下であり、したがってガラスと接触させたオゾン含有水を電子材料などの洗浄に使用しても、金属が汚染源となるおそれはない。
図1は、本発明方法の実施の一態様の工程系統図である。超純水が、超純水タンク1からポンプ2によってエジェクター3に送られ、同時にオゾン発生器4で発生したオゾンと酸素の混合ガスがエジェクターに吹き込まれ、気液混合状態で通水配管5に送られる。通水配管には、ユースポイント6の近傍に破砕ガラス充填カラム7が設けられる。破砕ガラス充填カラムの前後に設けたサンプリングポイント8及び9において、オゾン含有水をサンプリングし、それぞれの溶存オゾン濃度を測定することにより、ユースポイントにおいて所望濃度のオゾン含有水が得られるように条件を設定する。
本発明のオゾン濃度の低減方法を、ユースポイントで使用されたオゾン含有水や、使用されなかったオゾン含有水の排水ラインで実施すると、従来の活性炭、紫外線照射、触媒などを用いる方法と異なり、完全にメンテナンスフリーのオゾン分解方法として、溶存オゾン濃度を低減することができる。本発明のオゾン濃度の調整方法を所望濃度のオゾン含有水を得るために実施すると、従来の活性炭や触媒と接触させてオゾンを分解させる方法と異なり、ガラスは活性炭や触媒のように劣化することがなく、また、異物が溶出してオゾン含有水の水質を低下させるおそれもない。
【0008】
【実施例】
以下に、実施例を挙げて本発明をさらに詳細に説明するが、本発明はこれらの実施例によりなんら限定されるものではない。
実施例1
図1に示す装置を用いて、オゾン含有水のオゾン濃度の調整を行った。
超純水タンク1より、ポンプ2により超純水を流量16リットル/分でエジェクター3に送り、同時に無声放電式オゾン発生器4で発生させたオゾンと酸素の混合ガスをエジェクターに吹き込み、気液混合状態で通水配管5に送った。通水配管には、ユースポイント6の近傍に破砕ガラス充填カラム7を設け、ほぼ3〜5mm角に破砕した厚さ1.2mmのガラス[コーニング社、パイレックス7740]500gを充填している。破砕ガラス充填カラムの前後に設けたサンプリングポイント8及び9において、オゾン含有水を1時間ごとに5回ずつサンプリングし、それぞれの溶存オゾン濃度を測定した。
破砕ガラス充填カラム通過前のオゾン含有水の溶存オゾン濃度は25〜26mg/リットルであり、破砕ガラス充填カラム通過後のオゾン含有水の溶存オゾン濃度は14〜15mg/リットルであった。
実施例2
オゾンと酸素の混合ガスの供給量を減少した以外は、実施例1と同じ操作を繰り返した。
破砕ガラス充填カラム通過前のオゾン含有水の溶存オゾン濃度は15〜17mg/リットルであり、破砕ガラス充填カラム通過後のオゾン含有水の溶存オゾン濃度は8〜9mg/リットルであった。
実施例3
オゾンと酸素の混合ガスの供給量をさらに減少した以外は、実施例1と同じ操作を繰り返した。
破砕ガラス充填カラム通過前のオゾン含有水の溶存オゾン濃度は10〜12mg/リットルであり、破砕ガラス充填カラム通過後のオゾン含有水の溶存オゾン濃度は6〜7mg/リットルであった。
実施例4
オゾン含有排水の処理を想定して、図1に示す装置における破砕ガラス充填量を増やし、供給するオゾン含有水の溶存オゾン濃度を低下させた。
破砕ガラス充填カラムに充填するガラスの量を600gとし、オゾンと酸素の混合ガスの供給量を減少した以外は、実施例1と同じ操作を繰り返した。
破砕ガラス充填カラム通過前のオゾン含有水の溶存オゾン濃度は5〜7mg/リットルであり、破砕ガラス充填カラム通過後のオゾン含有水の溶存オゾン濃度は3〜4mg/リットルであった。
実施例5
オゾンと酸素の混合ガスの供給量をさらに減少した以外は、実施例4と同じ操作を繰り返した。
破砕ガラス充填カラム通過前のオゾン含有水の溶存オゾン濃度は2〜3mg/リットルであり、破砕ガラス充填カラム通過後のオゾン含有水の溶存オゾン濃度は1〜2mg/リットルであった。
実施例6
破砕ガラスの充填量を1,000gに増やした以外は、実施例5と同じ操作を繰り返した。
破砕ガラス充填カラム通過前のオゾン含有水の溶存オゾン濃度は2〜3mg/リットルであり、破砕ガラス充填カラム通過後のオゾン含有水の溶存オゾン濃度は0.3〜0.4mg/リットルであった。
実施例1〜6の結果を、第1表に示す。
【0009】
【表1】

Figure 0004508311
【0010】
第1表に見られるように、溶存オゾン濃度の高いオゾン含有水を破砕ガラスを充填したカラムに通水してガラスと接触させることにより、溶存オゾン濃度が低下し、かつ5回の溶存オゾン濃度の測定値のばらつきが1mg/リットル程度であることから、本発明方法によりオゾン含有水の溶存オゾン濃度を正確に制御し得ることが分かる。また、溶存オゾン濃度の低いオゾン含有水を通水した実施例4〜6の結果から、本発明方法は、オゾン含有排水の処理にも有効であり、実施例5と実施例6を比較すると、カラムに充填する破砕ガラスの量を増すことにより、処理水中の溶存オゾンの分解量を効果的に増大し得ることが分かる。
【0011】
【発明の効果】
本発明方法によれば、高濃度のオゾン含有水を製造し、ごく簡単な処理により溶存オゾンを分解して、正確に安定して所望濃度のオゾン含有水に調整することができる。また、オゾン含有排水の処理においても、メンテナンスフリーの装置を用いて、溶存オゾン濃度を低減することが可能となる。
【図面の簡単な説明】
【図1】図1は、本発明方法の実施の一態様の工程系統図である。
【符号の説明】
1 超純水タンク
2 ポンプ
3 エジェクター
4 オゾン発生器
5 通水配管
6 ユースポイント
7 破砕ガラス充填カラム
8 サンプリングポイント
9 サンプリングポイント[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a method for reducing and adjusting an ozone concentration. More specifically, the present invention relates to a method for reducing the concentration of ozone that can reduce the concentration of dissolved ozone without requiring maintenance in the treatment of wastewater containing ozone, and a wet cleaning process for electronic materials and the like. The present invention relates to a method for adjusting ozone concentration, which can easily supply ozone-containing water having a desired dissolved ozone concentration to a use point.
[0002]
[Prior art]
Removal of fine particles, organic substances, metals, and the like from the surface of electronic materials such as a semiconductor silicon substrate, a liquid crystal glass substrate, and a photomask quartz substrate is extremely important for ensuring product quality and yield. For this purpose, wet cleaning at a high temperature with a concentrated chemical solution based on hydrogen peroxide called the so-called RCA cleaning method is performed, and a mixed solution (APM) of ammonia and hydrogen peroxide solution or hydrochloric acid and hydrogen peroxide solution. A mixed solution (HPM) or the like was used. Reduces the cost of chemicals when using these cleaning methods, the cost of ultrapure water for rinsing, the cost of waste liquid treatment, the cost of air conditioning to exhaust chemical vapor and create new clean air, and use a large amount of water In recent years, the wet cleaning process has been reviewed in order to reduce environmental burdens such as mass disposal of drugs and emission of exhaust gas.
The present inventors have previously developed a gas-dissolved cleaning water for cleaning electronic materials in which ozone is dissolved in pure water. Washing water in which ozone is dissolved in pure water exhibits extremely high oxidizing power despite the low concentration of dissolved ozone of several mg / liter, and is contaminated by impurities such as organic substances and metals attached to the surface of electronic materials. It is used in the step of removing and the step of uniformly oxidizing the surface of the silicon substrate to form a chemical oxide film layer. Washing water in which ozone is dissolved in pure water has the advantage that the surface of the object to be cleaned is kept clean because it has no persistence, and it becomes high-purity water again by decomposition or removal of ozone and can be reused. However, the cleaning water in which ozone is dissolved is not easy to maintain and maintain the ozone concentration because the dissolved ozone self-decomposes with time and becomes oxygen.
On the other hand, the present inventors have found that the decrease in the dissolved ozone concentration is suppressed by supplying the ozone-containing gas and pure water while mixing them in the water pipe, and the ozone concentration is almost constant. A system for supplying ozone-containing water was developed. That is, a mixed gas of ozone and oxygen is produced by an ozone generator and fed into pure water in an ozone dissolving apparatus. The mixed gas of ozone and oxygen is mixed with pure water to be in a gas-liquid mixed state, ozone is dissolved to generate ozone-containing water, and further flows in the water flow pipe in the gas-liquid mixed state. Ozone dissolved in water changes to oxygen over time due to self-decomposition, but the decrease in dissolved ozone due to self-decomposition is compensated for by dissolving ozone in the gas phase in water. The concentration can be kept almost constant. However, even with this system, the ozone concentration may decrease when the branch piping that leads the ozone-containing water to the use point passes through a complicated piping route. Moreover, ozone-containing water having different ozone concentrations may be required depending on the use point.
In JP-A-10-57907, as a method for stably supplying ozone water having a constant concentration, the supply amount of ozone water obtained by the ozone water production means is set higher than the maximum discharge amount of ozone water. A method for controlling the amount of ozone water in the ozone water tank so as to always be within a certain range has been proposed. However, in such a method, control is complicated and a large-scale installation is required.
Ozone-containing water used in the electronics industry such as semiconductors and liquid crystals is required to have a very high purity with respect to impurities other than ozone. In addition, ozone-containing water is widely used for cleaning and sterilization in fields such as the pharmaceutical industry and food industry, but there are few methods for adjusting the dissolved ozone concentration while maintaining high purity. Therefore, there is a demand for a method for adjusting the ozone concentration, which can easily obtain ozone-containing water having a desired concentration.
On the other hand, ozone remains in the ozone-containing water used at the point of use. Like the ozone-containing water that was not used at the point of use, ozone can be decomposed using activated carbon, ultraviolet irradiation equipment, catalysts, etc. Has been done. However, ultraviolet irradiation has high equipment costs and processing costs, and the activated carbon and the catalyst deteriorate, so that they must be replaced regularly.
[0003]
[Problems to be solved by the invention]
In the treatment of wastewater containing ozone, the present invention is a use point in a method for reducing ozone concentration that can reduce dissolved ozone concentration without requiring maintenance, and in a wet cleaning process for electronic materials, etc. An object of the present invention is to provide a method for adjusting the ozone concentration, which can easily supply ozone-containing water having a desired dissolved ozone concentration.
[0004]
[Means for Solving the Problems]
As a result of intensive studies to solve the above problems, the present inventors have brought ozone-containing water into contact with glass, thereby promoting the self-decomposition of dissolved ozone and reducing the ozone concentration. By selecting the contact condition between the contained water and the glass, it has been found that it is possible to obtain ozone-containing water having a desired concentration by controlling the decomposition amount of ozone, and to complete the present invention based on this knowledge. It came.
That is, the present invention
(1) Pack the crushed glass to be used into the crushed glass packed column to be used, change the filling amount of the crushed glass and the particle size of the crushed glass, and use the ozone-containing water at the concentration to be used. Pass water at a water speed, measure the ozone concentration of ozone-containing water after passing through the crushed glass packed column, and when the ozone concentration of ozone-containing water after passing through the crushed glass packed column reaches the desired reduced ozone concentration in the particle size of the loading and crushing glass crushing glass, ozone-containing water having a concentration of scheduled use in contact with the crushed glass packed column, the ozone-containing, wherein to Rukoto and ozone-containing water having a desired reduced ozone concentration Adjustment method of ozone concentration of water, and
(2) Ultrapure water is pumped from the ultrapure water tank to the ejector at a water flow rate that is scheduled to be used, and simultaneously, the mixed gas of ozone and oxygen is blown into the ejector by changing the supply amount of the mixed gas. By measuring the ozone concentration of the ozone-containing water before passing through the packed column and blowing it into the ejector with the amount of mixed gas supplied when the ozone concentration is scheduled to be used, the ozone-containing water with the ozone concentration scheduled to be used is crushed. The method for adjusting the ozone concentration of ozone-containing water as described in item (1), which is passed through a glass-filled column ,
Is to provide.
[0005]
DETAILED DESCRIPTION OF THE INVENTION
The ozone concentration reducing method of the present invention is to bring ozone-containing water into contact with glass. The ozone concentration adjusting method of the present invention is to bring ozone-containing water into contact with glass to obtain ozone-containing water having a desired concentration. It is. By bringing ozone-containing water into contact with glass, self-decomposition of dissolved ozone in ozone-containing water is promoted. By bringing ozone-containing wastewater into contact with glass, the dissolved ozone concentration can be reduced without requiring maintenance. Can be reduced. In addition, ozone-containing water in which ozone at a concentration higher than the desired concentration at the use point is dissolved in the electronic material cleaning step, etc., is brought into contact with the glass in the vicinity of the use point, and the amount of dissolved ozone can be reduced to the desired concentration.
There is no restriction | limiting in particular in the kind of glass used for this invention method, For example, soda lime glass, potash lime glass, borosilicate glass, lead glass, aluminosilicate glass, borate glass, phosphate glass, aluminate glass , Titanate glass, fluoride glass, chalcogen glass, and the like. In these, the borosilicate glass excellent in the chemical durability with respect to water and an acid can be used suitably.
There is no restriction | limiting in particular in the shape of the glass used for this invention method, For example, plate glass, a glass tube, a glass bead, glass fiber etc. can be mentioned. In the method of the present invention, there is no particular limitation on the method of bringing the ozone-containing water into contact with the glass. For example, by making the liquid contact material of a part of the flow path of the ozone-containing water into glass, the ozone-containing water is brought into contact with the glass. Alternatively, ozone-containing water can be brought into contact with the glass by installing a container filled with crushed glass in the flow path of the ozone-containing water. Among these, crushed glass obtained by crushing glass into several mm square is easy to handle and has a large surface area, and therefore can be suitably used.
[0006]
According to the ozone concentration adjusting method of the present invention, in an ozone dissolving apparatus, excess ozone is dissolved in pure water, and before being used at a point of use, ozone-containing water is brought into contact with glass to perform self-decomposition of ozone. And can easily adjust the concentration of ozone-containing water. Moreover, the dissolved ozone density | concentration in ozone containing waste water can be reduced easily by the same means. That is, in the contact between the ozone-containing water and the glass, the concentration of the ozone-containing water can be adjusted easily and accurately by selecting the surface area of the glass to be contacted, the contact time, and the like. The amount of ozone decomposed can be increased by means such as increasing the amount of glass brought into contact with the ozone-containing water, reducing the particle size of the crushed glass, and slowing the water flow rate. In carrying out the method of the present invention, using the crushed glass to be used, the relationship between the glass filling amount and the ozone decomposition amount, the relationship between the glass particle size and the ozone decomposition amount, the relationship between the water flow rate and the ozone decomposition amount, etc. Can be obtained experimentally in advance, and a desired ozone concentration can be obtained by controlling an arbitrary factor according to the amount of ozone to be reduced. Moreover, since the amount of ozone decomposition is also affected by the ozone concentration of ozone-containing water, it is preferable to experiment by changing the ozone concentration of ozone-containing water when grasping the relationship between the contact condition with glass and the amount of ozone decomposition. .
According to the method of the present invention, in a supply system of ozone-containing water in an electronic material factory or the like, by providing a container filled with crushed glass between the ozone-containing water production apparatus and the ozone-containing water use point, The dissolved ozone concentration of ozone-containing water having a concentration can be reduced to easily obtain ozone-containing water having a desired concentration. Since ozone-containing water must not be contaminated during contact with glass, the piping that passes ozone-containing water has very little elution of foreign substances and does not react with ozone, which has strong oxidizing power. It is preferable to use a resin tube or the like. Similarly, the container filled with crushed glass is also preferably a member having high ozone resistance. The container itself filled with the crushed glass can be made of glass.
[0007]
In the method of the present invention, the mechanism by which ozone self-decomposition is promoted by bringing ozone-containing water into contact with glass is not clear, but it is presumed that a trace amount of metal mixed in the glass is acting. However, the metal has almost no elution from the glass, and even if it is analyzed, it is below the detection limit. Therefore, even if ozone-containing water contacted with the glass is used for cleaning electronic materials, the metal is not a source of contamination. There is no fear of becoming.
FIG. 1 is a process flow diagram of one embodiment of the method of the present invention. Ultrapure water is sent from the ultrapure water tank 1 to the ejector 3 by the pump 2, and simultaneously, a mixed gas of ozone and oxygen generated by the ozone generator 4 is blown into the ejector, and into the water pipe 5 in a gas-liquid mixed state. Sent. A crushing glass packed column 7 is provided in the vicinity of the use point 6 in the water flow pipe. Sampling points 8 and 9 provided before and after the crushed glass packed column sample the ozone-containing water and measure the respective dissolved ozone concentrations, so that the ozone-containing water at the desired concentration can be obtained at the use point. Set.
When the ozone concentration reduction method of the present invention is carried out in the drainage line of ozone-containing water used at the point of use or ozone-containing water that has not been used, unlike conventional methods using activated carbon, ultraviolet irradiation, catalyst, etc., As a completely maintenance-free ozonolysis method, the dissolved ozone concentration can be reduced. When the ozone concentration adjustment method of the present invention is carried out to obtain ozone-containing water of a desired concentration, glass deteriorates like activated carbon or catalyst, unlike the conventional method of decomposing ozone by contacting with activated carbon or catalyst. In addition, there is no possibility that foreign matter is eluted and the quality of ozone-containing water is lowered.
[0008]
【Example】
Hereinafter, the present invention will be described in more detail with reference to examples, but the present invention is not limited to these examples.
Example 1
The ozone concentration of the ozone-containing water was adjusted using the apparatus shown in FIG.
Ultrapure water is sent from the ultrapure water tank 1 to the ejector 3 by a pump 2 at a flow rate of 16 liters / min. At the same time, a mixed gas of ozone and oxygen generated by the silent discharge ozone generator 4 is blown into the ejector. The mixed state was sent to the water flow pipe 5. The water flow pipe is provided with a crushed glass packed column 7 in the vicinity of the use point 6 and filled with 500 g of 1.2 mm thick glass [Corning, Pyrex 7740] crushed to approximately 3 to 5 mm square. At sampling points 8 and 9 provided before and after the crushed glass packed column, the ozone-containing water was sampled five times every hour, and the dissolved ozone concentration was measured.
The dissolved ozone concentration of ozone-containing water before passing through the crushed glass packed column was 25 to 26 mg / liter, and the dissolved ozone concentration of ozone-containing water after passing through the crushed glass packed column was 14 to 15 mg / liter.
Example 2
The same operation as in Example 1 was repeated except that the supply amount of the mixed gas of ozone and oxygen was reduced.
The dissolved ozone concentration of ozone-containing water before passing through the crushed glass packed column was 15 to 17 mg / liter, and the dissolved ozone concentration of ozone-containing water after passing through the crushed glass packed column was 8 to 9 mg / liter.
Example 3
The same operation as in Example 1 was repeated except that the supply amount of the mixed gas of ozone and oxygen was further reduced.
The dissolved ozone concentration of ozone-containing water before passing through the crushed glass packed column was 10 to 12 mg / liter, and the dissolved ozone concentration of ozone-containing water after passing through the crushed glass packed column was 6 to 7 mg / liter.
Example 4
Assuming the treatment of ozone-containing wastewater, the amount of crushed glass in the apparatus shown in FIG. 1 was increased, and the dissolved ozone concentration of the supplied ozone-containing water was reduced.
The same operation as in Example 1 was repeated except that the amount of the glass packed in the crushed glass packed column was 600 g and the supply amount of the mixed gas of ozone and oxygen was decreased.
The dissolved ozone concentration of the ozone-containing water before passing through the crushed glass packed column was 5 to 7 mg / liter, and the dissolved ozone concentration of the ozone-containing water after passing through the crushed glass packed column was 3 to 4 mg / liter.
Example 5
The same operation as in Example 4 was repeated except that the supply amount of the mixed gas of ozone and oxygen was further reduced.
The dissolved ozone concentration of the ozone-containing water before passing through the crushed glass packed column was 2-3 mg / liter, and the dissolved ozone concentration of the ozone-containing water after passing through the crushed glass packed column was 1-2 mg / liter.
Example 6
The same operation as in Example 5 was repeated except that the amount of crushed glass was increased to 1,000 g.
The dissolved ozone concentration of ozone-containing water before passing through the crushed glass packed column was 2-3 mg / liter, and the dissolved ozone concentration of ozone-containing water after passing through the crushed glass packed column was 0.3-0.4 mg / liter. .
The results of Examples 1-6 are shown in Table 1.
[0009]
[Table 1]
Figure 0004508311
[0010]
As can be seen in Table 1, by passing ozone-containing water with a high dissolved ozone concentration through a column filled with crushed glass and bringing it into contact with the glass, the dissolved ozone concentration is lowered and the dissolved ozone concentration is 5 times. Since the variation of the measured value is about 1 mg / liter, it is understood that the dissolved ozone concentration of the ozone-containing water can be accurately controlled by the method of the present invention. In addition, from the results of Examples 4 to 6 in which ozone-containing water having a low dissolved ozone concentration was passed, the method of the present invention is also effective for the treatment of ozone-containing wastewater, and when Example 5 and Example 6 are compared, It can be seen that the amount of dissolved ozone decomposed in the treated water can be effectively increased by increasing the amount of crushed glass packed in the column.
[0011]
【The invention's effect】
According to the method of the present invention, high-concentration ozone-containing water can be produced, dissolved ozone can be decomposed by a very simple treatment, and accurately and stably adjusted to ozone-containing water having a desired concentration. Further, in the treatment of ozone-containing wastewater, it is possible to reduce the dissolved ozone concentration using a maintenance-free device.
[Brief description of the drawings]
FIG. 1 is a process flow diagram of one embodiment of the method of the present invention.
[Explanation of symbols]
1 Ultrapure water tank 2 Pump 3 Ejector 4 Ozone generator 5 Water flow pipe 6 Use point 7 Broken glass packed column 8 Sampling point 9 Sampling point

Claims (2)

使用予定の破砕ガラスを使用予定の破砕ガラス充填カラムに充填して、破砕ガラスの充填量及び破砕ガラスの粒径を変更して、使用予定の濃度のオゾン含有水を使用予定の通水速度で通水して、破砕ガラス充填カラム通過後のオゾン含有水のオゾン濃度を測定し、破砕ガラス充填カラム通過後のオゾン含有水のオゾン濃度が、所望の低減オゾン濃度になったときの破砕ガラスの充填量及び破砕ガラスの粒径において、使用予定の濃度のオゾン含有水を充填カラムの破砕ガラスと接触させ、所望の低減オゾン濃度のオゾン含有水とすることを特徴とするオゾン含有水のオゾン濃度の調整方法。 Pack the crushed glass to be used into the crushed glass packed column to be used, change the amount of crushed glass and the particle size of the crushed glass, and use ozone-containing water with the concentration to be used at the water flow rate to be used. Pass the water, measure the ozone concentration of the ozone-containing water after passing through the crushed glass packed column, and the ozone concentration of the ozone-containing water after passing through the crushed glass packed column becomes the desired reduced ozone concentration. in the particle size of the loading and crushing the glass, the water containing ozone at a concentration of scheduled use in contact with the crushed glass packed column, the ozone of the ozone-containing water, wherein to Rukoto and ozone-containing water having a desired reduced ozone concentration How to adjust the density. 超純水タンクより、ポンプによって超純水を使用予定の通水速度でエジェクターに送り同時に、オゾンと酸素の混合ガスを該混合ガスの供給量を変更してエジェクターに吹き込み、破砕ガラス充填カラム通過前のオゾン含有水のオゾン濃度を測定して、使用予定のオゾン濃度になったときの混合ガスの供給量でエジェクターに吹き込むことにより、使用予定のオゾン濃度のオゾン含有水を、破砕ガラス充填カラムに通水する請求項1記載のオゾン含有水のオゾン濃度の調整方法。 Ultrapure water is sent from the ultrapure water tank to the ejector at a flow rate that is planned to be used by the pump. At the same time, a mixed gas of ozone and oxygen is blown into the ejector after changing the supply amount of the mixed gas, and passes through the crushed glass packed column By measuring the ozone concentration of the previous ozone-containing water and blowing it into the ejector with the supply amount of the mixed gas when the ozone concentration is scheduled to be used, the ozone-containing water whose ozone concentration is scheduled to be used is crushed glass packed column The method for adjusting the ozone concentration of ozone-containing water according to claim 1, wherein water is passed through the water.
JP14699199A 1999-05-26 1999-05-26 Adjustment method of ozone concentration Expired - Fee Related JP4508311B2 (en)

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