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JPH0661541B2 - Method and apparatus for removing hydrogen peroxide - Google Patents
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JPH0661541B2 - Method and apparatus for removing hydrogen peroxide - Google Patents

Method and apparatus for removing hydrogen peroxide

Info

Publication number
JPH0661541B2
JPH0661541B2 JP16388785A JP16388785A JPH0661541B2 JP H0661541 B2 JPH0661541 B2 JP H0661541B2 JP 16388785 A JP16388785 A JP 16388785A JP 16388785 A JP16388785 A JP 16388785A JP H0661541 B2 JPH0661541 B2 JP H0661541B2
Authority
JP
Japan
Prior art keywords
hydrogen peroxide
activated carbon
granular activated
aqueous solution
packed bed
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 - Lifetime
Application number
JP16388785A
Other languages
Japanese (ja)
Other versions
JPS6227090A (en
Inventor
祐治 原口
敏樹 真鍋
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.)
Organo Corp
Original Assignee
Organo Corp
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 Organo Corp filed Critical Organo Corp
Priority to JP16388785A priority Critical patent/JPH0661541B2/en
Publication of JPS6227090A publication Critical patent/JPS6227090A/en
Publication of JPH0661541B2 publication Critical patent/JPH0661541B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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  • Water Treatment By Sorption (AREA)

Description

【発明の詳細な説明】 〈産業上の利用分野〉 本発明は、過酸化水素を比較的多量に含有する水溶液か
ら過酸化水素を除去し、これを放流可能とする過酸化水
素の除去方法およびその装置に関するものである。
DETAILED DESCRIPTION OF THE INVENTION <Industrial field of application> The present invention relates to a method for removing hydrogen peroxide, which removes hydrogen peroxide from an aqueous solution containing a relatively large amount of hydrogen peroxide, and makes it possible to discharge the hydrogen peroxide. It relates to the device.

〈従来技術〉 半導体を製造する電子工業では製品の洗浄に、各種イオ
ンはもとより、微粒子、生菌、TOCなどの不純物を極
限値まで除去した、いわゆる超純水が用いられる。この
ような超純水は濾過、イオン交換処理、逆浸透膜処理、
紫外線殺菌等あらゆる技術を駆使して製造されるが、当
該超純水の純度を維持するために、超純水を移送する配
管は定期的に洗浄される。当該配管洗浄は特に配管の滞
留部に沈着するスライムの除去や、接液部全般の殺菌の
ために行うもので、洗浄剤としては通常、0.15重量%〜
0.25重量%の過酸化水素の水溶液が用いられる。
<Prior Art> In the electronic industry that manufactures semiconductors, so-called ultrapure water in which impurities such as fine particles, viable bacteria, and TOC are removed to the limit value, as well as various ions, is used for cleaning products. Such ultrapure water is filtered, ion exchange treated, reverse osmosis membrane treated,
Although it is manufactured by making full use of various techniques such as ultraviolet sterilization, in order to maintain the purity of the ultrapure water, the pipe for transferring the ultrapure water is regularly cleaned. The pipe cleaning is particularly performed for removing slime deposited in the stagnant part of the pipe and for sterilizing the entire wetted part, and the cleaning agent is usually 0.15% by weight to
An aqueous solution of 0.25 wt% hydrogen peroxide is used.

したがって電子工業では当該洗浄に用いた過酸化水素の
水溶液が定期的に廃液として排出されることとなる。
Therefore, in the electronic industry, the aqueous solution of hydrogen peroxide used for the cleaning is regularly discharged as a waste liquid.

このような過酸化水素を含む水溶液はそのまま放流する
ことができないので、従来は当該廃液に亜硫酸ナトリウ
ムなどの還元剤を添加し、過酸化水素の酸力化を中和し
た後放流している。
Since such an aqueous solution containing hydrogen peroxide cannot be discharged as it is, conventionally, a reducing agent such as sodium sulfite is added to the waste liquid to neutralize the acidification of hydrogen peroxide and then discharged.

〈発明が解決しようとする問題点〉 しかしながら従来の還元剤を用いて上記中和を行う方法
は以下のような欠点を有している。
<Problems to be Solved by the Invention> However, the above-mentioned neutralizing method using a reducing agent has the following drawbacks.

まず過酸化水素と亜硫酸ナトリウムの反応時間が2〜3
時間と比較的長く、したがって反応槽もそれだけ大きく
なり、当該廃液量が多い場合は反応槽の設置面積を広く
必要とするし、またその処理液に過酸化水素が残留して
も、逆に亜硫酸ソーダが残留してもいずれの場合も放流
不適となり、酸やアルカリの中和反応と比較して放流に
おける認容範囲が極めて狭く、酸化還元の中和は技術的
にかなり難しく、これを自動化する場合制御が比較的複
雑となる。
First, the reaction time of hydrogen peroxide and sodium sulfite is 2-3
It takes a relatively long time, and therefore the reaction tank becomes large, and when the amount of the waste liquid is large, a large installation area is required for the reaction tank. In any case, even if soda remains, it becomes unsuitable for discharge, the acceptance range in discharge is extremely narrow compared to the acid or alkali neutralization reaction, and it is technically difficult to neutralize redox. Control becomes relatively complicated.

したがってこのような反応槽、自動制御機構および攪拌
機構を備えた処理装置の設備費は比較的高価となり、か
つ定常的に亜硫酸ナトリウム等の還元剤も必要とするの
で、ランニングコストも高い。
Therefore, the equipment cost of the processing apparatus equipped with such a reaction tank, automatic control mechanism, and stirring mechanism is relatively high, and a reducing agent such as sodium sulfite is constantly required, and the running cost is high.

本発明は従来の処理方法における、かかる欠点を除き、
設備面積をそれ程必要とせず、操作が簡単で、かつイニ
シャルコストおよびランニングコストが比較的安価な過
酸化水素の除去方法およびその装置を提供することを目
的とするものである。
The present invention eliminates such drawbacks in the conventional processing method,
An object of the present invention is to provide a method and apparatus for removing hydrogen peroxide, which does not require a large installation area, is easy to operate, and has relatively low initial cost and running cost.

〈問題点を解決する手段〉 本発明の第一発明は過酸化水素の除去方法に関するもの
で、過酸化水素を含む水溶液のpHを10以上に調整し
て粒状活性炭充填層に通液することを特徴とするもので
あり、また本発明の第二発明は、本発明の方法を実施す
る装置に関するもので、槽内に粒状活性炭充填層を上下
二層に充填するとともにそれぞれの充填層の下方に空間
部を形成し、少なくとも上部粒状活性炭充填層の下方に
形成した空間部に外部へ通じるガス抜き管を連通し、上
部粒状活性炭充填層の上方部に過酸化水素を含む水溶液
の流入管を、下部粒状活性炭充填層の下方の空間部に処
理液の流出管をそれぞれ連通したことを特徴とするもの
である。
<Means for Solving Problems> The first invention of the present invention relates to a method for removing hydrogen peroxide, which comprises adjusting the pH of an aqueous solution containing hydrogen peroxide to 10 or more and passing the solution through a granular activated carbon packed bed. The second invention of the present invention relates to an apparatus for carrying out the method of the present invention, in which a granular activated carbon packed bed is packed in upper and lower two layers in a tank and below each packed bed. A space part is formed, at least the space part formed below the upper granular activated carbon packed layer is connected to a gas vent pipe communicating to the outside, and an inflow pipe of an aqueous solution containing hydrogen peroxide is provided above the upper granular activated carbon packed layer. The present invention is characterized in that the processing liquid outflow pipes are connected to the spaces below the lower granular activated carbon packed bed.

〈作用〉 本発明は過酸化水素を含む水溶液を粒状活性炭の充填層
に通液して、粒状活性炭の有する還元力を用いて水溶液
中の過酸化水素を分解除去するものであるが、本発明者
等の実験によれば、当該処理効果は粒状活性炭層に接触
させる当該水溶液のpHによって大幅に変化し、pHを
10以上、好ましくはpHを10.5以上にしないと満足す
る処理効果が得られないことを知見した。
<Operation> The present invention is to pass an aqueous solution containing hydrogen peroxide through a packed bed of granular activated carbon and decompose and remove hydrogen peroxide in the aqueous solution using the reducing power of the granular activated carbon. According to the experiments by the researchers, the treatment effect largely varies depending on the pH of the aqueous solution brought into contact with the granular activated carbon layer, and the satisfactory treatment effect cannot be obtained unless the pH is 10 or more, preferably 10.5 or more. I found out that.

すなわち後述する実施例で示したごとく、充填層高60
0mmの粒状活性炭層に0.2重量%〜3.0重量%の過酸化水
素を含む水溶液をLV3m/H〜LV7m/Hで通液し
た結果では、いずれも当該水溶液のpHが9以下の場合
は、短時間で処理液に過酸化水素が漏出し、pHを10
に上昇させると処理液に僅かの過酸化水素を漏出する
が、長時間処理することができ、またpHを10.5まで上
昇させると処理液に過酸化水素は全く漏出せず、安定し
て長時間処理することができた。
That is, as shown in Examples described later, the packed bed height 60
As a result of passing an aqueous solution containing 0.2% by weight to 3.0% by weight of hydrogen peroxide through a 0 mm granular activated carbon layer at LV3 m / H to LV7 m / H, when the pH of the aqueous solution is 9 or less, it is considered that a short time is required. Hydrogen peroxide leaks into the processing solution at pH 10
A slight amount of hydrogen peroxide leaks into the processing solution when it is raised to 1, but it can be treated for a long time, and when the pH is raised to 10.5, hydrogen peroxide does not leak into the processing solution at all, and it is stable for a long time. I was able to handle it.

当該水溶液のpHを上昇させるといかなる理由で処理効
果が上昇するのか今のところ明確ではないが、前述の通
液状態を観察すると以下のような現象が生じている。
It is not clear at present why the treatment effect is enhanced by increasing the pH of the aqueous solution, but the following phenomenon occurs when observing the above-mentioned liquid passing state.

すなわち過酸化水素を含む水溶液が粒状活性炭層に接触
すると、直ちに分解反応が生じ酸素が発生するが、水溶
液のpHが9以下では粒状活性炭の充填層の内部でも酸
素が発生し、それが気泡となって充填層内に閉じ込めら
れるが、水溶液のpHが10以上となると当該気泡が充
填層内に閉じ込められることがない。
That is, when an aqueous solution containing hydrogen peroxide comes into contact with the granular activated carbon layer, a decomposition reaction immediately occurs and oxygen is generated. However, when the pH of the aqueous solution is 9 or less, oxygen is also generated inside the granular activated carbon packed layer, which causes bubbles. However, when the pH of the aqueous solution becomes 10 or more, the bubbles are not trapped in the packed bed.

水溶液のpHが9以下における処理液の過酸化水素の漏
出は、前記気泡によって充填層内を水溶液がショートパ
ス(チャンネリング現象)することが起因していると考
えられる。
It is considered that the leakage of hydrogen peroxide in the treatment liquid when the pH of the aqueous solution is 9 or less is due to the short path (channeling phenomenon) of the aqueous solution in the packed bed due to the bubbles.

また水溶液のpHを10以上に上昇させると充填層内に
気泡が生じないことから、接触pHの上昇により明らか
に過酸化水素の分解速度が速くなり、そのため水溶液中
の過酸化水素のほとんどが粒状活性炭充填層の比較的上
層部で分解するものと考えられる。
Also, when the pH of the aqueous solution is raised to 10 or more, no bubbles are generated in the packed bed, so the decomposition rate of hydrogen peroxide obviously increases due to the increase of the contact pH, so that most of the hydrogen peroxide in the aqueous solution is granular. It is considered that it decomposes in the relatively upper part of the activated carbon packed bed.

いずれにしても過酸化水素を含む水溶液のpHを10以
上に調整することは本発明の所期の目的を達するために
必須の要件である。
In any case, adjusting the pH of the aqueous solution containing hydrogen peroxide to 10 or more is an essential requirement for achieving the intended purpose of the present invention.

なお粒状活性炭に過酸化水素を含む水溶液を接触させて
過酸化水素を分解除去する際に、粒状活性炭の炭素成分
と過酸化水素の反応により、微量の一酸化炭素が発生す
るが、当該水溶液のpHをアルカリ性にすることによ
り、当該一酸化炭素を処理液中に溶解させて固定するこ
とができ、有害ガスである一酸化炭素の発生による環境
汚染を防止できるという効果も奏する。
When the aqueous solution containing hydrogen peroxide is brought into contact with the granular activated carbon to decompose and remove the hydrogen peroxide, a small amount of carbon monoxide is generated due to the reaction between the carbon component of the granular activated carbon and hydrogen peroxide. By making the pH alkaline, the carbon monoxide can be dissolved and fixed in the treatment liquid, and there is an effect that environmental pollution due to the generation of carbon monoxide, which is a harmful gas, can be prevented.

次に本発明の方法を実施する装置について以下に説明す
る。
Next, an apparatus for carrying out the method of the present invention will be described below.

前述したごとく、粒状活性炭層に過酸化水素を含む水溶
液を接触させると過酸化水素が分解し酸素が発生するの
で、当該酸素が粒状活性炭の充填層中に閉じ込められる
ことによるチャンネリング現象が生じないようにする必
要があるが、本発明においては前述したように接触pH
を上昇させることによりこれを回避するとともに、装置
的にも発生した酸素を効果的に排出できるような構造と
したものである。
As described above, when the aqueous solution containing hydrogen peroxide is brought into contact with the granular activated carbon layer, hydrogen peroxide is decomposed and oxygen is generated, so that the channeling phenomenon due to the oxygen being confined in the packed layer of granular activated carbon does not occur. However, in the present invention, the contact pH is set as described above.
This is to avoid this by raising, and to have a structure in which the generated oxygen can be effectively discharged also in terms of the device.

第1図は本発明装置の実施態様の一例のフローを示す説
明図であり、上方が開放した槽1内に、液は通過するが
粒状活性炭は通過させないスクリーン2Aおよび2B、
たとえば目板にサラン布を張ったものを上下二段に設置
し、それぞれのスクリーン2Aおよび2Bの上部に粒状
活性炭を充填して、上部粒状活性炭層3および下部粒状
活性炭層4を形成する。なお下部粒状活性炭層4を形成
する場合は、スクリーン2Aの下方に位置する槽1の側
胴マンホール(図示せず)から粒状活性炭を充填する。
また両粒状活性炭層3および4の下方部にはそれぞれ空
間部S1およびS2を形成する。
FIG. 1 is an explanatory diagram showing a flow of an example of an embodiment of the device of the present invention, in which a screen 2A and 2B through which liquid passes but granular granular activated carbon does not pass, in a tank 1 whose upper side is open,
For example, a sheet of cloth covered with Saran cloth is installed in two upper and lower stages, and granular activated carbon is filled in the upper portions of the screens 2A and 2B to form an upper granular activated carbon layer 3 and a lower granular activated carbon layer 4. When forming the lower granular activated carbon layer 4, the granular activated carbon is filled from the side trunk manhole (not shown) of the tank 1 located below the screen 2A.
Spaces S 1 and S 2 are formed below the granular activated carbon layers 3 and 4, respectively.

上部粒状活性炭層3の上方部にディストリビュータ5を
設置し、当該ディストリビュータ5に過酸化水素を含む
水溶液である原液の流入管6の一端を連通し、さらに下
部粒状活性炭層4の下方に形成した空間部S2に処理液
の流出管7を連通するとともに、当該処理液の流出管7
に逆洗水流入管8を連通する。
A space formed by disposing a distributor 5 above the upper granular activated carbon layer 3 and connecting one end of an inflow pipe 6 of a stock solution, which is an aqueous solution containing hydrogen peroxide, to the distributor 5 and further below the lower granular activated carbon layer 4. The processing liquid outflow pipe 7 is connected to the portion S 2 and the processing liquid outflow pipe 7 is connected.
The backwash water inflow pipe 8 is communicated with.

またそれぞれの空間部S1およびS2に、上部粒状活性炭
層3の上方に形成される水面より上方まで立上げたガス
抜き管9を連通するとともに、当該ガス抜き管9に下部
粒状活性炭層4の逆洗排水を排出するための逆洗排水流
出管10Bを連通する。
Further, a gas vent pipe 9 that is raised above the water surface formed above the upper granular activated carbon layer 3 is communicated with each space S 1 and S 2 , and the lower granular activated carbon layer 4 is connected to the gas vent pipe 9. The backwash drainage outflow pipe 10B for discharging the backwash drainage is communicated.

一方前記原液の流入管6に上部粒状活性炭層3の逆洗排
水を排出するための逆洗排水流出管10Aとカ性ソーダ
溶液流入管11の一端を連通し、当該カ性ソーダ溶液流
入管11の他端を注入ポンプ12を介してカ性ソーダ溶
液槽13に連通する。なお原液の流入管6とカ性ソーダ
溶液流入管11の接合点下流側に混合器14を付設する
とともに、当該混合器14の下流側にpH電極15を付
設し、当該pH電極15と注入ポンプ12とをpH指示
調節計16を介して計装的に接続する。なお17はブロ
ー管であり、18〜24はそれぞれ弁を示す。
On the other hand, a backwash drainage outflow pipe 10A for discharging backwash drainage of the upper granular activated carbon layer 3 and one end of the caustic soda solution inflow pipe 11 are connected to the stock solution inflow pipe 6, and the caustic soda solution inflow pipe 11 is connected. The other end of the solution is communicated with the caustic soda solution tank 13 via the injection pump 12. In addition, a mixer 14 is attached downstream of the junction of the stock solution inflow pipe 6 and the caustic soda solution inflow pipe 11, and a pH electrode 15 is attached downstream of the mixer 14, and the pH electrode 15 and the injection pump are attached. 12 is instrumentally connected via a pH indicator controller 16. Reference numeral 17 is a blow pipe, and 18 to 24 are valves.

次に本装置の操作を以下に説明する。Next, the operation of this device will be described below.

運転の当初に粒状活性炭を充填して各層3および4を形
成するが、当該粒状活性炭に微粉炭が混入している場合
は、弁23、弁20、弁19を開口して逆洗水流入管8
から逆洗水を流入し、各層3および4を適度に膨張さ
せ、微粉炭を含む逆洗排水を逆洗排水流出管10Aおよ
び10Bから流出させる。なお当該逆洗工程は、以下に
説明する通液工程を続行するにしたがい各層3、4に懸
濁物質が詰まり、その圧力損失が上昇した際にも適宜に
行う。このような逆洗が終了した後各弁を閉じ、弁24
を開口して槽1内の水をブロー管17から排出する。
At the beginning of the operation, the granular activated carbon is filled to form the layers 3 and 4, but when pulverized coal is mixed in the granular activated carbon, the valve 23, the valve 20 and the valve 19 are opened and the backwash water inflow pipe 8 is opened.
The backwash water is introduced from the above, the respective layers 3 and 4 are appropriately expanded, and the backwash drainage containing the pulverized coal is caused to flow out from the backwash drainage outflow pipes 10A and 10B. The backwashing step is appropriately performed even when the suspended substance is clogged in each of the layers 3 and 4 as the liquid passing step described below is continued and the pressure loss thereof increases. After such backwashing is completed, each valve is closed and the valve 24
To discharge the water in the tank 1 from the blow pipe 17.

次いで弁18、弁21、弁22を開口し、その他の弁は
閉じ、原液の流入管6から原液を流入し、処理液の流出
管7から処理液を得る通液を行う。
Next, the valves 18, 21, and 22 are opened, the other valves are closed, and the stock solution is introduced from the stock solution inflow pipe 6 and the process solution is obtained from the process solution outflow pipe 7.

なお当該通液時に注入ポンプ12を駆動して原液にカ性
ソーダ溶液を混合し、原液のpHを10以上、好ましく
は10.5〜11.0に調整する。
When the liquid is passed, the injection pump 12 is driven to mix the caustic soda solution with the stock solution to adjust the pH of the stock solution to 10 or more, preferably 10.5-11.0.

この調整はpH電極15によって測定されるpHが、あ
らかじめ定めた所定の範囲になるように、pH指示調節
計16により計装的に注入ポンプ12のカ性ソーダ溶液
注入量を調節することにより行う。
This adjustment is performed by instrumentally adjusting the caustic soda solution injection amount of the injection pump 12 by the pH indicator controller 16 so that the pH measured by the pH electrode 15 falls within a predetermined range determined in advance. .

ディストリビュータ5により均等に分配した原液を上部
粒状活性炭層3の上面に落下させ、当該層3、スクリー
ン2A、下部粒状活性炭層4、スクリーン2Bを順次通
過させ、空間部S2で集液し、処理液を処理液の流出管
7から流出する。なお槽1内の水を排出した後に前述の
通液を行うと通液の続行により、上部粒状活性炭層3の
上部、下部粒状活性炭層4の上部および空間部S2の底
部に比較的薄い液面が形成される。
The undiluted solution evenly distributed by the distributor 5 is dropped onto the upper surface of the upper granular activated carbon layer 3, and sequentially passed through the layer 3, the screen 2A, the lower granular activated carbon layer 4, and the screen 2B, and the liquid is collected in the space S 2 and treated. The liquid flows out from the processing liquid outflow pipe 7. If the above-mentioned liquid flow is performed after the water in the tank 1 is discharged, the liquid flow continues, so that a relatively thin liquid is applied to the upper part of the upper granular activated carbon layer 3, the upper part of the lower granular activated carbon layer 4 and the bottom of the space S 2. A surface is formed.

このような通液により原液中に存在する過酸化水素は粒
状活性炭層に接触することにより分解するが、当該分解
により発生する酸素の大部分は上部粒状活性炭層3の上
面から大気に放出される。また上部粒状活性炭層3によ
って分解されずに残留する小量の過酸化水素は下部粒状
活性炭層4に接触する際に直ちに分解され、当該分解に
よって発生した酸素は空間部S1に連通したガス抜き管
9から大気に放出される。さらに空間部S2においてた
とえ酸素が発生したとしても空間部S2に連通したガス
抜き管9から同様にして大気に放出される。
The hydrogen peroxide present in the stock solution by such passage is decomposed by coming into contact with the granular activated carbon layer, but most of the oxygen generated by the decomposition is released from the upper surface of the upper granular activated carbon layer 3 to the atmosphere. . Further, a small amount of hydrogen peroxide remaining without being decomposed by the upper granular activated carbon layer 3 is immediately decomposed when coming into contact with the lower granular activated carbon layer 4, and the oxygen generated by the decomposition is degassed to communicate with the space S 1. Emitted from the pipe 9 to the atmosphere. Is released to the atmosphere in the same manner from the gas vent pipe 9 communicating with the space S 2 even if oxygen is generated further in the space portion S 2.

このように本発明の装置は粒状活性炭を充填する槽を上
部開放型とし、かつ粒状活性炭充填層を上下二段に充填
し、上部粒状活性炭層3と下部粒状活性炭層4の間に空
間部S1を設け、当該空間部S1に外部へ通じるガス抜き
管9を連通したので、発生する酸素を容易に槽外へ放出
することができ、粒状活性炭の充填層に気泡を発生させ
ることがなく、チャンネリング現象に起因する過酸化水
素の漏出を効果的に防止することができる。
As described above, in the apparatus of the present invention, the tank for filling the granular activated carbon is of the upper open type, and the granular activated carbon packed layers are filled in two stages, the space S between the upper granular activated carbon layer 3 and the lower granular activated carbon layer 4. Since 1 is provided and the gas vent pipe 9 communicating with the outside is connected to the space S 1 , the generated oxygen can be easily released to the outside of the tank, and no bubbles are generated in the packed bed of granular activated carbon. It is possible to effectively prevent the leakage of hydrogen peroxide due to the channeling phenomenon.

なお槽1を密閉型とし、重力式通液によらず圧力式通液
とすることも可能であるが、その場合は、槽1の上部に
ガス抜き弁などを設置し、上部粒状活性炭層3から発生
する酸素を大気に放出するような構造とする必要があ
る。
Note that the tank 1 may be a closed type, and pressure type liquid flow may be used instead of gravity type liquid flow. In that case, a gas vent valve or the like is installed in the upper part of the tank 1 and the upper granular activated carbon layer 3 It is necessary to have a structure that releases oxygen generated from the atmosphere to the atmosphere.

本発明装置におけるそれぞれの粒状活性炭層3、4の充
填層高は、400mm〜600mmが適当で、あまり厚く充
填すると充填層内に気泡が発生しやすくなるので好まし
くない。また通液流速は原液の過酸化水素の含有量が多
い程、低流速にする必要があるが、過酸化水素含有量が
たとえば0.2重量%の時はLV7m/H前後、および過
酸化水素含有量がたとえば3重量%の時はLV3m/H
前後が適当である。
The height of the packed bed of each of the granular activated carbon layers 3 and 4 in the apparatus of the present invention is suitably 400 mm to 600 mm, and it is not preferable that the packed bed is too thick because bubbles tend to occur in the packed bed. The flow rate should be lower as the content of hydrogen peroxide in the stock solution is higher. However, when the hydrogen peroxide content is 0.2% by weight, the flow rate should be around LV 7 m / H and the hydrogen peroxide content. Is 3% by weight, LV3m / H
The front and back are appropriate.

〈効果〉 以上説明したごとく、本発明方法は粒状活性炭層に原液
を通過させるのみで過酸化水素を除去できるので、従来
法のような大きな反応槽を必要とせず、装置の設置面積
を小さくすることができ、かつ操作が簡単であるから自
動操作も容易であり、装置の設備費を従来のものより安
価とすることができ、さらに亜硫酸ナトリウムなどの還
元剤を用いないので、ランニングコストも大幅に低減で
きる。さらに粒状活性炭槽に過酸化水素を含む水溶液を
接触させて粒状活性炭の有する還元剤で過酸化水素を分
解除去する際に、原液のpHを10以上に調整すること
により、粒状活性炭層の層内に気泡が発生するのを防止
し、原液のチャンネリング現象による処理液への過酸化
水素の漏出を効果的に防止することができる。
<Effect> As described above, since the method of the present invention can remove hydrogen peroxide by simply passing the stock solution through the granular activated carbon layer, a large reaction tank as in the conventional method is not required, and the installation area of the apparatus can be reduced. It can be operated easily and is easy to operate automatically, and the equipment cost of the device can be made lower than the conventional one. Furthermore, since a reducing agent such as sodium sulfite is not used, the running cost is also large. Can be reduced to Further, when the aqueous solution containing hydrogen peroxide is brought into contact with the granular activated carbon tank to decompose and remove the hydrogen peroxide with the reducing agent of the granular activated carbon, the pH of the stock solution is adjusted to 10 or more, so that the granular activated carbon layer It is possible to prevent air bubbles from being generated and effectively prevent leakage of hydrogen peroxide into the treatment liquid due to the channeling phenomenon of the raw liquid.

また本発明の装置は、槽内に粒状活性炭充填層を上下二
層に充填するとともに、それぞれの充填層の下方に空間
部を形成し、少なくとも上部粒状活性炭層の下方に形成
した空間部に、外部へ通じるガス抜き管を連通した構造
としたので、上部粒状活性炭層の処理液中に残留する過
酸化水素が、下部粒状活性炭に接触することにより分解
し、たとえ小量の過酸化水素が発生しても、前記ガス抜
き管から当該酸素を容易に槽外へ放出することができ、
上下二層の粒状活性炭層に気泡を発生させることがな
く、チャンネリング現象に起因する処理液の過酸化水素
の漏出をより効果的に防止することができる。
Further, the device of the present invention, while filling the upper and lower two layers of granular activated carbon packed bed in the tank, to form a space below each packed bed, at least in the space formed below the upper granular activated carbon layer, Since the structure is such that the gas vent pipe communicating with the outside is connected, hydrogen peroxide remaining in the treatment liquid of the upper granular activated carbon layer decomposes when it contacts the lower granular activated carbon, and even a small amount of hydrogen peroxide is generated. Even so, it is possible to easily release the oxygen from the gas vent pipe to the outside of the tank,
It is possible to more effectively prevent the leakage of hydrogen peroxide of the treatment liquid due to the channeling phenomenon without generating bubbles in the upper and lower granular activated carbon layers.

以下に本発明の効果を明確とするために実施例を説明す
る。
Examples will be described below to clarify the effects of the present invention.

〔実施例〕〔Example〕

試験カラムに粒状活性炭、ダイヤホープ(登録商標)0
08を600mmの高さに充填し、過酸化水素含有量0.2
重量%、1.0重量%、3.0重量%の原液について、当該原
液のpHをそれぞれ5.5、7.0、9.0、10.0、10.5に調整
して通液試験を行った。なお通液流速は過酸化水素含有
量0.2重量%の原液についてはLV7m/h、過酸化水
素含有量1.0重量%の原液についてはLV5m/H、過
酸化水素含有量3重量%の原液についてはLV3m/H
とした。
Granular activated carbon, DiaHope (registered trademark) 0 in the test column
08 is filled to a height of 600 mm and the hydrogen peroxide content is 0.2
For the stock solutions of wt%, 1.0 wt% and 3.0 wt%, the pH of the stock solutions was adjusted to 5.5, 7.0, 9.0, 10.0 and 10.5, respectively, and a liquid passing test was conducted. The flow rate is LV7m / h for the stock solution with a hydrogen peroxide content of 0.2% by weight, LV5m / H for the stock solution with a hydrogen peroxide content of 1.0% by weight, and LV3m for the stock solution with a hydrogen peroxide content of 3% by weight. / H
And

過酸化水素含有量0.2重量%の通液結果を第2図に、過
酸化水素含有量1.0重量%の通液結果を第3図に、過酸
化水素含有量3.0重量%の通液結果を第4図にそれぞれ
示した。
Figure 2 shows the results of passing hydrogen peroxide content of 0.2% by weight, Figure 3 shows the results of passing hydrogen peroxide content of 1.0% by weight, and Figure 3 shows the results of passing hydrogen peroxide content of 3.0% by weight. Each is shown in FIG.

第2図〜第4図に見られるごとく、原液のpHが9.0以
下では短時間で過酸化水素が漏出した。また通液の状態
を観察すると、pH9.0以下の場合はいずれも充填層内
に気泡が発生していることが認められた。
As shown in FIGS. 2 to 4, when the pH of the stock solution was 9.0 or less, hydrogen peroxide leaked out in a short time. Further, when the state of liquid passage was observed, it was confirmed that air bubbles were generated in the packed bed in all cases where the pH was 9.0 or less.

また原液のpHが10の場合は、処理液に僅かに過酸化
水素が漏出するものの長時間処理することができ、また
pHが10.5の場合は、処理液に過酸化水素が全く漏出せ
ずに安定して長時間処理することができた。
When the pH of the stock solution is 10, the hydrogen peroxide slightly leaks to the treatment liquid, but it can be treated for a long time. When the pH is 10.5, hydrogen peroxide does not leak to the treatment liquid at all. It was possible to process stably for a long time.

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

第1図は本発明装置の実施態様の一例のフローを示す説
明図であり、第2図、第3図、第4図はそれぞれ実施例
における通液結果を示すグラフで、縦軸に処理液の過酸
化水素(H22)の濃度を示し、横軸に処理時間を示
す。 1…槽、2…スクリーン 3…上部粒状活性炭層 4…下部粒状活性炭層 5…ディストリビュータ 6…原液の流入管、7…処理液の流出管 8…逆洗水流入管、9…ガス抜き管 10…逆洗排水排出管 11…カ性ソーダ溶液流入管 12…注入ポンプ、13…カ性ソーダ溶液槽 14…混合器、15…pH電極 16…pH指示調節計、17…ブロー管 18〜24…弁、S…空間部
FIG. 1 is an explanatory view showing the flow of an example of an embodiment of the device of the present invention, and FIGS. 2, 3, and 4 are graphs showing the results of liquid passage in each example, with the treatment liquid on the vertical axis. Concentration of hydrogen peroxide (H 2 O 2 ) is shown, and the horizontal axis shows the treatment time. DESCRIPTION OF SYMBOLS 1 ... Tank, 2 ... Screen 3 ... Upper granular activated carbon layer 4 ... Lower granular activated carbon layer 5 ... Distributor 6 ... Stock solution inflow pipe, 7 ... Treatment liquid outflow pipe 8 ... Backwash water inflow pipe, 9 ... Gas vent pipe 10 ... Backwash drainage discharge pipe 11 ... Caustic soda solution inflow pipe 12 ... Injection pump, 13 ... Caustic soda solution tank 14 ... Mixer, 15 ... pH electrode 16 ... pH indicator controller, 17 ... Blow pipe 18-24 ... Valve , S ... Space section

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】過酸化水素を含む水溶液から過酸化水素を
除去するにあたり、当該水溶液のpHを10以上に調整
して粒状活性炭充填層に通液することを特徴とする過酸
化水素の除去方法。
1. A method for removing hydrogen peroxide, which comprises removing the hydrogen peroxide from an aqueous solution containing hydrogen peroxide by adjusting the pH of the aqueous solution to 10 or more and passing it through a granular activated carbon packed bed. .
【請求項2】過酸化水素を含む水溶液のpHを10以上
に調整して粒状活性炭充填層に通液する装置であって、
槽内に粒状活性炭充填槽を上下二層に充填するとともに
それぞれの充填層の下方に空間部を形成し、少なくとも
上部粒状活性炭充填層の下方に形成した空間部に外部へ
通じるガス抜き管を連通し、上部粒状活性炭充填層の上
方部に過酸化水素を含む水溶液の流入管を、下部粒状活
性炭充填層の下方の空間部に処理液の流出管をそれぞれ
連通したことを特徴とする過酸化水素の除去装置。
2. An apparatus for adjusting the pH of an aqueous solution containing hydrogen peroxide to 10 or more and passing it through a granular activated carbon packed bed,
The tank is filled with granular activated carbon filling tanks in upper and lower layers, and a space is formed below each packed bed, and a gas vent pipe communicating with the outside is connected to at least the space formed below the upper granular activated carbon packed bed. The upper part of the upper granular activated carbon packed bed is connected to an inflow pipe of an aqueous solution containing hydrogen peroxide, and the space part below the lower granular activated carbon packed bed is connected to an outflow pipe of the treatment liquid. Removal device.
JP16388785A 1985-07-26 1985-07-26 Method and apparatus for removing hydrogen peroxide Expired - Lifetime JPH0661541B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP16388785A JPH0661541B2 (en) 1985-07-26 1985-07-26 Method and apparatus for removing hydrogen peroxide

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP16388785A JPH0661541B2 (en) 1985-07-26 1985-07-26 Method and apparatus for removing hydrogen peroxide

Publications (2)

Publication Number Publication Date
JPS6227090A JPS6227090A (en) 1987-02-05
JPH0661541B2 true JPH0661541B2 (en) 1994-08-17

Family

ID=15782685

Family Applications (1)

Application Number Title Priority Date Filing Date
JP16388785A Expired - Lifetime JPH0661541B2 (en) 1985-07-26 1985-07-26 Method and apparatus for removing hydrogen peroxide

Country Status (1)

Country Link
JP (1) JPH0661541B2 (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3894788B2 (en) * 2001-12-21 2007-03-22 オルガノ株式会社 Wastewater treatment equipment containing hydrogen peroxide
JP4860008B1 (en) * 2011-06-02 2012-01-25 株式会社アサカ理研 Hydrogen peroxide decomposition apparatus and hydrogen peroxide decomposition method
JP6035109B2 (en) * 2012-10-24 2016-11-30 三菱レイヨンアクア・ソリューションズ株式会社 To-be-treated water treatment apparatus and to-be-treated water treatment method
JP2024070084A (en) * 2022-11-10 2024-05-22 日本メクトロン株式会社 Hydrogen peroxide decomposition system, hydrogen peroxide decomposition device, and method for decomposing hydrogen peroxide

Also Published As

Publication number Publication date
JPS6227090A (en) 1987-02-05

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