JPH09117763A - Treatment of waste water from chemical/mechanical polishing - Google Patents

Treatment of waste water from chemical/mechanical polishing

Info

Publication number
JPH09117763A
JPH09117763A JP28024895A JP28024895A JPH09117763A JP H09117763 A JPH09117763 A JP H09117763A JP 28024895 A JP28024895 A JP 28024895A JP 28024895 A JP28024895 A JP 28024895A JP H09117763 A JPH09117763 A JP H09117763A
Authority
JP
Japan
Prior art keywords
hydrogen peroxide
tank
waste water
porous membrane
polymer porous
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.)
Withdrawn
Application number
JP28024895A
Other languages
Japanese (ja)
Inventor
Itsuki Koto
厳 古藤
Hirohisa Fukuda
博久 福田
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Asahi Chemical Industry Co Ltd
Original Assignee
Asahi Chemical Industry Co 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 Asahi Chemical Industry Co Ltd filed Critical Asahi Chemical Industry Co Ltd
Priority to JP28024895A priority Critical patent/JPH09117763A/en
Publication of JPH09117763A publication Critical patent/JPH09117763A/en
Withdrawn legal-status Critical Current

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  • Separation Using Semi-Permeable Membranes (AREA)
  • Removal Of Specific Substances (AREA)

Abstract

PROBLEM TO BE SOLVED: To lessen the deterioration of a high polymer porous membrane and to reuse filtered water when treating CPM waste water using the high polymer porous membrane filter by decomposing hydrogen peroxide in waste water in advance and feeding the waste water to the filter. SOLUTION: From a chemical/mechanical polishing (CPM) device 1, CPM waste water containing hydrogen peroxide and alumina abrasive grains is discharged to a pretreating tank 2. NaOH aqueous solution in a neutralizer tank 3 is injected by an injection pump 8 and hydrogen peroxide decomposing enzyme in a hydrogen peroxide decomposing agent tank 4 is injected by a fixed delivery injection pump 9, and the mixture is agitated by an agitator 6. The treated liquid in which hydrogen peroxide is thus decomposed in the pretreatment tank 2 is transferred to a circulation tank through liquid transfer piping 11 by a liquid transfer pump 10, and enters a high polymer membrane through a circulating pump, and is separated into filtrate and concentrate there. The filtrate is used as washing water through an ion exchange tower.

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、ケミカルメカニカ
ルポリッシング(以下、CMPと呼ぶ)装置から排出す
る廃水(以下、CMP廃水ともいう)の処理方法に関す
る。さらに詳しくは、前処理装置でCMP廃水中の過酸
化水素を過酸化水素分解酵素で分解した後に高分子多孔
質膜濾過装置を用いて濾過することにより、再利用でき
る濾過水と無機砥粒を含む濃縮水に分離処理する方法に
関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating wastewater (hereinafter also referred to as CMP wastewater) discharged from a chemical mechanical polishing (hereinafter referred to as CMP) device. More specifically, the hydrogen peroxide in the CMP waste water is decomposed by a hydrogen peroxide-decomposing enzyme in the pretreatment device, and then filtered using a polymer porous membrane filtration device to obtain reusable filtered water and inorganic abrasive particles. The present invention relates to a method of separating and processing concentrated water containing the same.

【0002】[0002]

【従来の技術】CMP装置から排出する酸系スラリー廃
水には、大きさが0.01〜3μmのSiO2 又はAl
2 3 或いはMgO等の無機砥粒とH2 SO4 又はHF
等の無機酸及び過酸化水素を含み、いずれも懸濁してい
るためそのままの状態では排出できない。
2. Description of the Related Art Acid-based slurry wastewater discharged from a CMP apparatus contains SiO 2 or Al having a size of 0.01 to 3 μm.
Inorganic abrasive grains such as 2 O 3 or MgO and H 2 SO 4 or HF
It cannot be discharged as it is because it contains inorganic acids such as and hydrogen peroxide and both are suspended.

【0003】先に、本発明者らは、この廃水の多孔質膜
による再生方法を提案したが、さらに検討した結果、処
理コスト、処理設備のスペース等の面から、多孔質膜と
しては無機系多孔質膜のものより高分子多孔質膜の方が
優れているものの、過酸化水素を含む酸系スラリー廃水
の場合は高分子多孔質膜が劣化するという問題点が明ら
かになった。
Previously, the present inventors have proposed a method for regenerating this wastewater using a porous membrane. As a result of further study, an inorganic type porous membrane is used as the porous membrane in terms of treatment cost, space for treatment equipment and the like. Although the polymer porous membrane is superior to that of the porous membrane, it has become clear that the polymer porous membrane is deteriorated in the case of the acid-based slurry wastewater containing hydrogen peroxide.

【0004】[0004]

【発明が解決しようとする課題】本発明の目的は、高分
子多孔質膜濾過装置を用いたCMP廃水処理方法が抱え
る問題点解決すること、すなわち、高分子多孔質膜の劣
化が少なく、濾過水が再利用できるCMP廃水の処理方
法を提供することにある。
SUMMARY OF THE INVENTION An object of the present invention is to solve the problems of the CMP wastewater treatment method using a polymer porous membrane filtration device, that is, to reduce the deterioration of the polymer porous membrane and to filter it. It is to provide a method for treating CMP wastewater in which water can be reused.

【0005】[0005]

【課題を解決するための手段】本発明者らは、鋭意検討
の結果、CMP廃水中の過酸化水素を過酸化水素分解剤
で分解することによって、前記の課題を解決しうること
を見出し、本発明をなすに至った。即ち、本発明は、C
MP廃水を高分子多孔質膜濾過装置を用いて処理するに
際し、該廃水中の過酸化水素を前処理装置であらかじめ
分解し、該濾過装置に供給することを特徴とするCMP
廃水処理方法であり、また、CMP廃水中の過酸化水素
を前処理装置であらかじめ分解するに際し、該廃水のp
Hを中性にした後に過酸化水素分解酵素を注入すること
を特徴とするCMP廃水処理方法である。
As a result of earnest studies, the present inventors have found that the above problems can be solved by decomposing hydrogen peroxide in CMP wastewater with a hydrogen peroxide decomposing agent. The present invention has been completed. That is, the present invention is C
When treating MP wastewater using a polymer porous membrane filtration device, hydrogen peroxide in the wastewater is decomposed in advance by a pretreatment device and supplied to the filtration device.
It is a wastewater treatment method, and when the hydrogen peroxide in the CMP wastewater is decomposed in advance by a pretreatment device, p
A method for treating CMP wastewater, which comprises injecting a hydrogen peroxide-decomposing enzyme after neutralizing H.

【0006】本発明において、前処理装置は、pH計、
攪拌機、液面レベル計、及び送液ポンプの付いた前処理
タンクと、定量注入ポンプの付いた過酸化水素分解剤タ
ンク及び注入ポンプの付いた中和剤タンクからなり、そ
れぞれの動きは、プログラマブルコントローラ(以下、
シーケンスと呼ぶ)で制御する。前処理タンクの大きさ
及び濃縮水と処理水に分離する高分子多孔質膜濾過装置
の循環タンクの大きさと送液速度は、CMP廃水の排出
速度と過酸化水素が分解するのに必要な滞留時間を考慮
して決めるとよい。過酸化水素分解酵素の場合は、10
分好ましくは30分の滞留時間をとるとよい。
In the present invention, the pretreatment device is a pH meter,
It consists of a pretreatment tank with a stirrer, a liquid level meter, and a liquid feed pump, a hydrogen peroxide decomposer tank with a metering injection pump, and a neutralizer tank with an injection pump. Controller (hereinafter,
Call it a sequence). The size of the pretreatment tank, the size of the circulation tank of the polymer porous membrane filtration device that separates the concentrated water and the treated water, and the feed rate are the discharge rate of CMP wastewater and the retention required for decomposition of hydrogen peroxide. It is good to decide in consideration of time. 10 for hydrogen peroxide degrading enzyme
The retention time is preferably 30 minutes.

【0007】本発明で用いる過酸化水素分解剤は、亜硫
酸、亜燐酸、蓚酸、過マンガン酸、チオ硫酸、及び第一
鉄等の無機塩或いは過酸化水素分解酵素であるが、特に
過酸化水素分解酵素が好ましい。無機塩の添加量は、過
酸化水素の規定濃度と等量入れるとよい。また、過酸化
水素分解酵素の場合は、過酸化水素質量濃度の1/10
0以上、好ましくは1/30以上の濃度でよい。
The hydrogen peroxide decomposing agent used in the present invention is an inorganic salt such as sulfurous acid, phosphorous acid, oxalic acid, permanganic acid, thiosulfuric acid and ferrous iron, or a hydrogen peroxide decomposing enzyme. Degradative enzymes are preferred. The inorganic salt may be added in an amount equal to the specified concentration of hydrogen peroxide. In the case of hydrogen peroxide-degrading enzyme, 1/10 of hydrogen peroxide mass concentration
The concentration may be 0 or higher, preferably 1/30 or higher.

【0008】本発明において、過酸化水素分解剤として
過酸化水素分解酵素を用いる場合は、過酸化水素の分解
率を上げるために、中和剤を用いてCMP廃水のpHを
中性にすることが好ましい。中和剤としては、KOH、
NaOH、Ca(OH)2 、及びNH4 OH等のアルカ
リ性水溶液がよい。該中和剤のいずれかを用いて、CM
P廃水のpHを5〜11、好ましくは6〜8になるよう
にする。
In the present invention, when a hydrogen peroxide-decomposing enzyme is used as a hydrogen peroxide-decomposing agent, a neutralizing agent is used to neutralize the pH of CMP wastewater in order to increase the decomposition rate of hydrogen peroxide. Is preferred. As a neutralizing agent, KOH,
Alkaline aqueous solutions such as NaOH, Ca (OH) 2 and NH 4 OH are preferable. CM using any of the neutralizing agents
The pH of the P waste water is adjusted to 5 to 11, preferably 6 to 8.

【0009】本発明において、中和剤と過酸化水素分解
酵素の添加順番はいずれが先でもかまわないが、中和剤
を先に添加したほうがより好ましい。本発明において、
前処理装置で過酸化水素が分解されたCMP廃水は、前
処理タンクの送液ポンプで高分子多孔質膜濾過装置に送
液される。本発明に用いる高分子多孔質膜濾過装置は、
液面レベル計の付いた循環タンク、濾液タンク、及び濃
縮液タンク、循環ポンプ及び逆洗ポンプ、高分子多孔質
膜、積算流量計、積算流量指示計、流量計、、圧力トラ
ンスミッタ、圧力計、温度計、濁度検知器、濁度計、電
導度計、pH計、自動弁、及びイオン交換樹脂塔と制御
盤からなり、シーケンス制御されるが、以上述べた計器
類を全て備える必要はなく、目的に応じて備えるとよ
い。タンクの材質、形状に制限はない。又、ポンプも特
に制限はないが、廃水中の砥粒でシール部が破損しにく
い構造のものを選択するとよい。
In the present invention, the neutralizing agent and the hydrogen peroxide-decomposing enzyme may be added in any order, but it is more preferable to add the neutralizing agent first. In the present invention,
The CMP wastewater in which hydrogen peroxide has been decomposed in the pretreatment device is fed to the polymer porous membrane filtration device by the liquid feed pump of the pretreatment tank. The polymer porous membrane filtration device used in the present invention is
Circulation tank with liquid level meter, filtrate tank, and concentrate tank, circulation pump and backwash pump, polymer porous membrane, integrated flow meter, integrated flow indicator, flow meter, pressure transmitter, pressure gauge, It consists of a thermometer, turbidity detector, turbidity meter, conductivity meter, pH meter, automatic valve, and ion exchange resin tower and control panel, and is sequence-controlled, but it is not necessary to have all the above-mentioned instruments. It is good to prepare according to the purpose. There are no restrictions on the material and shape of the tank. The pump is also not particularly limited, but it is preferable to select one having a structure in which the seal portion is not easily damaged by the abrasive grains in the waste water.

【0010】本発明で分離に用いる高分子多孔質膜は、
20〜500オングストロームのUF膜(限外濾過膜)
及び0.05〜1μmのMF膜(精密濾過膜)と呼ばれ
ている膜の中から、砥粒の大きさより小さい孔径のもの
を用いるとよい。又、過酸化水素分解酵素も濃縮除去し
たい時はUF膜を用いるとよい。高分子多孔質膜の材質
としては、ポリアクリロニトリル、ポリスルフォン、ポ
リエチレン、ポリプロピレン、ポリフッ化ビニリデン、
ポリテトラフルオロエチレン、酢酸セルロース、ポリア
ミド、ポリビニリデンクロライド、ポリエーテルサルフ
ォン等が挙げられる。 膜の形状は、管状膜、平板膜、
スパイラル膜、中空糸膜等いずれの形状を選択してもよ
い。
The polymer porous membrane used for separation in the present invention is
20 to 500 angstrom UF membrane (ultrafiltration membrane)
Also, it is preferable to use a film having a pore size smaller than the size of the abrasive grains from the film called MF film (microfiltration film) having a thickness of 0.05 to 1 μm. Further, when the hydrogen peroxide-decomposing enzyme is also desired to be concentrated and removed, a UF membrane may be used. As the material of the polymer porous film, polyacrylonitrile, polysulfone, polyethylene, polypropylene, polyvinylidene fluoride,
Examples thereof include polytetrafluoroethylene, cellulose acetate, polyamide, polyvinylidene chloride, and polyether sulfone. The shape of the membrane is tubular membrane, flat membrane,
Any shape such as a spiral membrane or a hollow fiber membrane may be selected.

【0011】本発明の、高分子多孔質膜濾過装置を用い
る廃水処理法においては、膜濾過面と直交するように濾
過水を流す方法と膜濾過面と平行に濾過水を流す方法
(クロスフロー方式)が知られているが、クロスフロー
方式が好ましい。操作圧力は膜の耐圧性と濾過速度及び
濾過安定性を考慮して最適な値を定めるとよい。循環流
量は多い方がよく、1〜3m/秒の流速になるようにす
るとよい。
In the wastewater treatment method using the porous polymer membrane filtration device of the present invention, a method of flowing filtered water so as to be orthogonal to the membrane filtration surface and a method of flowing filtered water parallel to the membrane filtration surface (cross flow) Method is known, but the cross-flow method is preferable. The operating pressure may be set to an optimum value in consideration of the pressure resistance of the membrane, the filtration rate and the filtration stability. The circulation flow rate is preferably high, and the flow rate may be 1 to 3 m / sec.

【0012】本発明に用いる高分子多孔質膜で、設定し
た濾液量を濾過し目的の濃度まで濃縮された液は、循環
ポンプによって濃縮液タンクに排出される。一方、濾過
水は、カチオン樹脂とアニオン樹脂からなるイオン交換
樹脂塔に通水され、イオン性物質が除去される。いうま
でもなく、イオン性物質の除去が必要でない時は交換樹
脂塔を必要としない。
The liquid obtained by filtering the set amount of filtrate with the polymer porous membrane used in the present invention and concentrating it to the desired concentration is discharged to the concentrated liquid tank by the circulation pump. On the other hand, the filtered water is passed through an ion exchange resin tower composed of a cation resin and an anion resin to remove ionic substances. Needless to say, an exchange resin tower is not required when the removal of ionic substances is not required.

【0013】本発明で用いる高分子多孔質膜の濾過水の
水質は、必要に応じて、濁度検知器、濁度計、電導度計
及びpH計等を設置して監視するとよい。
The quality of the filtered water of the polymer porous membrane used in the present invention may be monitored by installing a turbidity detector, a turbidity meter, an electric conductivity meter, a pH meter and the like, if necessary.

【0014】[0014]

【発明の実施の形態】以下、図面を参照しつつ、本発明
の実施例および比較例によって具体的に説明する。
BEST MODE FOR CARRYING OUT THE INVENTION Embodiments of the present invention and comparative examples will be specifically described below with reference to the drawings.

【0015】[0015]

【実施例1】図1は、CMP廃水を前処理する装置の概
略フロー図であり、図中、1はCMP装置、2は前処理
タンク、3は中和剤タンク、4は過酸化水素分解剤タン
ク、5は液面レベル計、6は攪拌機、7はpH計、8は
中和剤注入ポンプ、9は過酸化水素分解剤注入ポンプ、
10は送液ポンプ、11は前処理されたCMP廃水を図
2の高分子多孔質膜濾過装置に送る送液配管を示す。図
2は前処理されたCMP廃水を処理する高分子多孔質膜
濾過装置であり、12は液面レベル計、13は積算流量
計と流量センサー、14は高分子多孔質膜、15はイオ
ン交換塔、16は循環ポンプ、17は循環タンク、濃縮
液タンクを示す。いずれの装置もシーケンス制御で作動
する装置である。
EXAMPLE 1 FIG. 1 is a schematic flow chart of an apparatus for pretreatment of CMP wastewater, in which 1 is a CMP apparatus, 2 is a pretreatment tank, 3 is a neutralizer tank, and 4 is hydrogen peroxide decomposition. Agent tank, 5 liquid level meter, 6 stirrer, 7 pH meter, 8 neutralizer injection pump, 9 hydrogen peroxide decomposer injection pump,
Reference numeral 10 is a liquid feed pump, and 11 is a liquid feed pipe for feeding the pretreated CMP wastewater to the polymer porous membrane filtration device of FIG. FIG. 2 shows a polymer porous membrane filtration device for treating pretreated CMP wastewater, 12 is a liquid level meter, 13 is an integrating flowmeter and a flow sensor, 14 is a polymer porous membrane, and 15 is ion exchange. A column, 16 is a circulation pump, 17 is a circulation tank, and a concentrate tank. Both devices are devices that operate under sequence control.

【0016】過酸化水素濃度は過マンガン酸カリウム滴
定法で測定した。CMP装置1から、過酸化水素とアル
ミナ砥粒を含むCMP廃水が前処理タンク2に100リ
ットル排出された。CMP廃水は白濁しており、pH
4.0、電気伝導度(以下ECと呼ぶ)240μs/c
m、過酸化水素濃度は1500mg/リットルであっ
た。
The hydrogen peroxide concentration was measured by the potassium permanganate titration method. From the CMP apparatus 1, 100 liters of CMP wastewater containing hydrogen peroxide and alumina abrasive grains was discharged to the pretreatment tank 2. CMP wastewater is cloudy and has a pH
4.0, electric conductivity (hereinafter referred to as EC) 240 μs / c
m and hydrogen peroxide concentration were 1500 mg / liter.

【0017】攪拌機6が回転し、中和剤タンク3中の1
%のNaOH水溶液が注入ポンプ8を経て前処理タンク
に注入された。その量は、pH計7からの電気信号を受
けて、pH計の指示値が7になるまで注入ポンプが作動
するようシーケンス制御して、添加された。次に、過酸
化水素分解剤タンク4中の一定量の過酸化水素分解酵素
が定量注入ポンプ9で前処理タンクに送られた。過酸化
水素分解酵素は、洛東化成工業株式会社製のエンチロン
OL−50を用い、CMP廃水100リットル中の過酸
化水素の1/20の質量に相当する7.5グラムを添加
した。10分間攪拌した後の過酸化水素濃度は45mg
/リットルであり、過酸化水素の分解率は97%であっ
た。
The stirrer 6 rotates, and 1 in the neutralizer tank 3 is rotated.
% NaOH aqueous solution was injected into the pretreatment tank via the injection pump 8. The amount was added by receiving an electric signal from the pH meter 7 and performing sequence control so that the infusion pump operates until the reading of the pH meter reaches 7. Next, a fixed amount of hydrogen peroxide decomposing enzyme in the hydrogen peroxide decomposing agent tank 4 was sent to the pretreatment tank by the constant volume injection pump 9. As the hydrogen peroxide-degrading enzyme, Enchilon OL-50 manufactured by Rakuto Kasei Kogyo Co., Ltd. was used, and 7.5 g corresponding to 1/20 the mass of hydrogen peroxide in 100 liters of CMP wastewater was added. Hydrogen peroxide concentration after stirring for 10 minutes is 45 mg
/ Liter, and the decomposition rate of hydrogen peroxide was 97%.

【0018】過酸化水素が分解された前処理タンクの液
は送液ポンプで送液配管を経て図2の循環タンク17に
送液した。送液された液は、循環ポンプ16を経て高分
子多孔質膜14に入り、そこで濾過液と濃縮液に分離さ
れた。濃縮液は循環タンク17に戻され、濾過液は積算
流量計と流量センサー13を経て、イオン交換塔を通し
た。
The liquid of the pretreatment tank in which hydrogen peroxide was decomposed was sent to the circulation tank 17 of FIG. 2 through the liquid sending pipe by the liquid sending pump. The fed liquid entered the porous polymer membrane 14 through the circulation pump 16, and was separated into a filtrate and a concentrated liquid there. The concentrated liquid was returned to the circulation tank 17, and the filtrate was passed through the integrated flow meter and the flow sensor 13 and passed through the ion exchange tower.

【0019】高分子多孔質過膜14は旭化成工業株式会
社製の限外濾過膜、ACV−3050(ポリアクリルニ
トリル膜、膜面積3.1m2 、中空糸内径1.4mm)
を用いた。クロスフロー方式で、濾過温度30℃、操作
平均圧力は100KPa、膜流路内の流速は2m/秒と
し、1.1リットル/分、m2 の濾過速度で分離処理し
た。
The polymer porous overmembrane 14 is an ultrafiltration membrane manufactured by Asahi Kasei Corporation, ACV-3050 (polyacrylonitrile membrane, membrane area 3.1 m 2 , hollow fiber inner diameter 1.4 mm).
Was used. The filtration was carried out by a cross-flow method at a filtration temperature of 30 ° C., an operation average pressure of 100 KPa, a flow rate in the membrane channel of 2 m / sec, and a filtration rate of 1.1 liter / min and m 2 .

【0020】濾過水は無色透明、pH7.1 、EC3
μs/cmであり、洗浄水として使用した。6ヵ月稼働
後の膜の引張強さの保持率は90%であった。
The filtered water is colorless and transparent, pH 7.1, EC3
μs / cm, which was used as washing water. The retention of tensile strength of the film after operating for 6 months was 90%.

【0021】[0021]

【比較例1】実施例1で得たCMP廃水を、前処理なし
で高分子多孔質膜濾過装置で、実施例1で用いた限外濾
過膜ACV−3050を用いて分離処理した。濾過装置
の運転条件は実施例1と同一にした。濾過水はイオン交
換塔を通さなかった。濾過水の過酸化水素濃度は145
0mg/リットルであり、、pH4.0、EC180μ
s/cmで再使用、又は放流できる水質ではなかった。
また、6ヵ月稼働後の膜の引張強さの保持率は46%で
あった。
Comparative Example 1 The CMP wastewater obtained in Example 1 was separated without pretreatment in a polymer porous membrane filtration device using the ultrafiltration membrane ACV-3050 used in Example 1. The operating conditions of the filtration device were the same as in Example 1. The filtered water did not pass through the ion exchange tower. Hydrogen peroxide concentration of filtered water is 145
0 mg / liter, pH 4.0, EC 180μ
The water quality was not reusable or discharged at s / cm.
The retention rate of tensile strength of the film after operating for 6 months was 46%.

【0022】[0022]

【発明の効果】本発明によれば、酸系の過酸化水素を含
むCMP廃水を前処理装置で処理して高分子多孔質膜濾
過装置で濃縮するため、高分子多孔質膜の劣化が少く、
膜の寿命が長くなる。さらに、濾過水は洗浄水、工業用
水、冷却水、散水用水、及び農業用水としての水質基準
を満たすため、それらの用途に使用することができる。
According to the present invention, since the CMP wastewater containing acid-type hydrogen peroxide is treated by the pretreatment device and concentrated by the polymer porous membrane filtration device, deterioration of the polymer porous membrane is reduced. ,
Longer membrane life. Further, the filtered water meets the water quality standards for washing water, industrial water, cooling water, sprinkling water, and agricultural water, and thus can be used for these applications.

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

【図1】本発明のCMP廃水処理装置の前処理装置概略
フロー図である。
FIG. 1 is a schematic flow chart of a pretreatment device of a CMP wastewater treatment device of the present invention.

【図2】本発明のCMP廃水処理装置の高分子多孔質膜
濃縮装置概略フロー図である。
FIG. 2 is a schematic flow diagram of a polymer porous membrane concentrating device of the CMP wastewater treatment device of the present invention.

【符号の説明】[Explanation of symbols]

1 CMP装置 2 前処理タンク 3 中和剤タンク 4 過酸化水素分解剤タンク 5 液面レベル計 6 攪拌機 7 pH計 8 中和剤注入ポンプ 9 定量注入ポンプ 10 送液ポンプ 11 送液配管 12 液面レベル計 13 積算濾液流量計と流量センサー 14 高分子多孔質膜 15 イオン交換塔 16 循環ポンプ 17 循環タンク 18 濃縮液タンク 1 CMP device 2 Pretreatment tank 3 Neutralizer tank 4 Hydrogen peroxide decomposer tank 5 Liquid level meter 6 Stirrer 7 pH meter 8 Neutralizer injection pump 9 Constant injection pump 10 Liquid feed pump 11 Liquid feed pipe 12 Liquid level Level meter 13 Integrated filtrate flow meter and flow sensor 14 Polymeric porous membrane 15 Ion exchange tower 16 Circulation pump 17 Circulation tank 18 Concentrated liquid tank

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 ケミカルメカニカルポリッシング廃水を
高分子多孔質膜濾過装置を用いて処理するに際し、該廃
水中の過酸化水素を前処理装置であらかじめ分解し、該
濾過装置に供給することを特徴とするケミカルメカニカ
ルポリッシング廃水処理方法。
1. When treating a chemical mechanical polishing wastewater using a polymer porous membrane filtration device, hydrogen peroxide in the wastewater is decomposed in advance by a pretreatment device and supplied to the filtration device. Chemical mechanical polishing wastewater treatment method.
【請求項2】 ケミカルメカニカルポリッシング廃水中
の過酸化水素を前処理装置であらかじめ分解するに際
し、該廃水のpHを中性にした後に過酸化水素分解酵素
を注入することを特徴とする請求項1記載のケミカルメ
カニカルポリッシング廃水処理方法。
2. When pre-decomposing hydrogen peroxide in a chemical mechanical polishing wastewater by a pretreatment device, the pH of the wastewater is neutralized, and then a hydrogen peroxide-decomposing enzyme is injected. The chemical mechanical polishing wastewater treatment method described.
JP28024895A 1995-10-27 1995-10-27 Treatment of waste water from chemical/mechanical polishing Withdrawn JPH09117763A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP28024895A JPH09117763A (en) 1995-10-27 1995-10-27 Treatment of waste water from chemical/mechanical polishing

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP28024895A JPH09117763A (en) 1995-10-27 1995-10-27 Treatment of waste water from chemical/mechanical polishing

Publications (1)

Publication Number Publication Date
JPH09117763A true JPH09117763A (en) 1997-05-06

Family

ID=17622370

Family Applications (1)

Application Number Title Priority Date Filing Date
JP28024895A Withdrawn JPH09117763A (en) 1995-10-27 1995-10-27 Treatment of waste water from chemical/mechanical polishing

Country Status (1)

Country Link
JP (1) JPH09117763A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2000002819A1 (en) * 1998-07-10 2000-01-20 United States Filter Corporation Ion exchange removal of metal ions from wastewater
JP2008000750A (en) * 2007-08-16 2008-01-10 Japan Organo Co Ltd Apparatus for treating waste water from cmp process
US7488423B2 (en) 2005-08-02 2009-02-10 Siemens Water Technologies Holding Corp. System and method of slurry treatment
JP2010119956A (en) * 2008-11-19 2010-06-03 Kurita Water Ind Ltd Method of treating anti-corrosive-containing water for azole-based copper
JP2015009214A (en) * 2013-06-28 2015-01-19 パナソニックIpマネジメント株式会社 Hydrogen peroxide-containing effluent treatment apparatus and treatment method

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2000002819A1 (en) * 1998-07-10 2000-01-20 United States Filter Corporation Ion exchange removal of metal ions from wastewater
US6818129B2 (en) 1998-07-10 2004-11-16 Usfilter Corporation Ion exchange removal of metal ions from wastewater
US7488423B2 (en) 2005-08-02 2009-02-10 Siemens Water Technologies Holding Corp. System and method of slurry treatment
JP2008000750A (en) * 2007-08-16 2008-01-10 Japan Organo Co Ltd Apparatus for treating waste water from cmp process
JP2010119956A (en) * 2008-11-19 2010-06-03 Kurita Water Ind Ltd Method of treating anti-corrosive-containing water for azole-based copper
JP2015009214A (en) * 2013-06-28 2015-01-19 パナソニックIpマネジメント株式会社 Hydrogen peroxide-containing effluent treatment apparatus and treatment method

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