JPH06142646A - Method for washing activated charcoal - Google Patents

Method for washing activated charcoal

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Publication number
JPH06142646A
JPH06142646A JP30360992A JP30360992A JPH06142646A JP H06142646 A JPH06142646 A JP H06142646A JP 30360992 A JP30360992 A JP 30360992A JP 30360992 A JP30360992 A JP 30360992A JP H06142646 A JPH06142646 A JP H06142646A
Authority
JP
Japan
Prior art keywords
washing
activated carbon
column
piping
water
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP30360992A
Other languages
Japanese (ja)
Inventor
Motomu Koizumi
求 小泉
Katsunori Kuroki
勝憲 黒木
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.)
Kurita Water Industries Ltd
Original Assignee
Kurita Water Industries Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Kurita Water Industries Ltd filed Critical Kurita Water Industries Ltd
Priority to JP30360992A priority Critical patent/JPH06142646A/en
Publication of JPH06142646A publication Critical patent/JPH06142646A/en
Pending legal-status Critical Current

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  • Treatment Of Liquids With Adsorbents In General (AREA)
  • Water Treatment By Sorption (AREA)

Abstract

PURPOSE:To efficiently execute a washing/sterilizing treatment of an activated charcoal adsorption column subjected to slime contamination by feeding an alkali water solution to the adsorption column and washing it, and thereafter,washing it by feeding hot water, in the case of washing activated charcoal packed in an adsorption bed by feeding a washing liquid to the activated charcoal adsorption column. CONSTITUTION:In an activated charcoal adsorption column 1, an adsorption bed 1A filled with activated charcoal is formed. Also, in the activated charcoal adsorption column 1, an anion exchange resin column 2 is provided together, and by filling it with an anion exchange resin, an anion exchange resin bed 2A is formed. In such a state, raw water passes through the column 1, a piping 12 and the column 2 from a piping 11 and is treated, and also, treated water is discharged to the outside of a system from a piping 13. On the other hand, an alkali reproducing liquid passes through the column 2 and a piping 22 from a piping 21 and is supplied to the column 1, the activated charcoal adsorption bed 1A is subjected to alkali washing, and thereafter, discharged to the outside of the system from a piping 23. Moreover, hog water passes through a heat exchanger 3 and a piping 32 from a piping 31 and is supplied to the column 1, the activated charcoal adsorption bed 1A is subjected to hot water washing, and thereafter, it is supplied to a storage tank 4 from a piping 33.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は活性炭の洗浄方法に係
り、特に、活性炭のスライム汚染の洗浄、殺菌効果が高
く、例えば、半導体製造排水の回収システムにおける活
性炭吸着塔の洗浄に好適な活性炭の洗浄方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for cleaning activated carbon, and in particular, it has a high effect of cleaning slime contamination of activated carbon and has a high sterilization effect. Regarding the cleaning method.

【0002】[0002]

【従来の技術】半導体製造工場の電子部品の洗浄には、
多量の超純水が用いられるが、その洗浄排水は、若干の
不純物を含むもののその純度はなお相当に高いことか
ら、回収処理して再利用されている。従来、この半導体
製造排水の水回収システムは、一般に、活性炭吸着塔→
イオン交換樹脂塔→逆浸透膜分離装置→過酸化水素を併
用した紫外線酸化装置→活性炭吸着塔→アニオン交換樹
脂塔で構成される。
2. Description of the Related Art For cleaning electronic parts in a semiconductor manufacturing plant,
Although a large amount of ultrapure water is used, the cleaning wastewater contains some impurities, but its purity is still quite high. Therefore, it is recovered and reused. Conventionally, this water recovery system for semiconductor manufacturing wastewater is generally used in an activated carbon adsorption tower →
Ion-exchange resin tower → Reverse osmosis membrane separator → UV-oxidizer combined with hydrogen peroxide → Activated carbon adsorption tower → Anion-exchange resin tower.

【0003】このような回収システムにおいて、前段の
活性炭吸着塔と、紫外線酸化装置の後段の活性炭吸着塔
では、スライムの発生が著しく、活性炭吸着塔の差圧の
上昇、菌体リークの増大といった問題が起きている。
In such a recovery system, slime is remarkably generated in the activated carbon adsorption tower in the former stage and the activated carbon adsorption tower in the latter stage of the ultraviolet oxidizer, which causes a problem that the differential pressure in the activated carbon adsorption tower rises and the cell leak increases. Is happening.

【0004】従来、この対策として、活性炭吸着塔に殺
菌剤を添加したり、温水洗浄を行なうなどの方法が採用
されている。
Conventionally, as measures against this, methods such as adding a sterilizing agent to the activated carbon adsorption tower and washing with warm water have been adopted.

【0005】[0005]

【発明が解決しようとする課題】しかしながら、殺菌剤
の添加では十分な効果が得られず、また、温水による洗
浄では、80〜90℃の高温水を用いないと十分な殺菌
効果が得られない上に、スライムの剥離効果が小さいと
いう欠点がある。
However, the addition of a bactericidal agent does not provide a sufficient effect, and the washing with hot water cannot obtain a sufficient bactericidal effect unless hot water of 80 to 90 ° C. is used. In addition, there is a disadvantage that the slime removing effect is small.

【0006】また、アルカリ洗浄も試みられているが、
アルカリ洗浄ではスライムの剥離効果はあるが、洗浄後
の水質の立上り性が悪いという欠点がある。
Alkaline cleaning has also been tried,
Alkali cleaning has the effect of removing slime, but it has the drawback that the rising quality of water after cleaning is poor.

【0007】このようなことから、活性炭吸着塔に発生
したスライムを効率的に剥離除去すると共に、十分な殺
菌効果を得ることができる洗浄・殺菌方法が望まれてい
る。
For these reasons, there is a demand for a cleaning / sterilizing method capable of efficiently removing the slime generated in the activated carbon adsorption tower and removing the slime, and obtaining a sufficient sterilizing effect.

【0008】なお、従来、超純水製造装置の末端逆浸透
膜分離装置の洗浄方法としては、過酸化水素水溶液で洗
浄後、アルカリ性純水、加熱純水、アルコールなどで洗
浄する方法は知られているが(特開昭62−25480
5号公報)、活性炭吸着塔については有効な洗浄・殺菌
方法が提供されていないのが実情である。
Conventionally, as a method of cleaning the terminal reverse osmosis membrane separation device of the ultrapure water production system, a method of cleaning with an aqueous solution of hydrogen peroxide and then with alkaline pure water, heated pure water, alcohol or the like is known. (Japanese Patent Application Laid-Open No. 62-25480
No. 5, gazette), no effective cleaning / sterilizing method is provided for the activated carbon adsorption tower.

【0009】本発明は上記従来の実情に鑑みてなされた
ものであって、スライム汚染された活性炭吸着塔を効率
的に洗浄・殺菌処理することができる活性炭の洗浄方法
を提供することを目的とする。
The present invention has been made in view of the above conventional circumstances, and an object of the present invention is to provide a method for cleaning activated carbon capable of efficiently cleaning and sterilizing a slime-contaminated activated carbon adsorption tower. To do.

【0010】[0010]

【課題を解決するための手段】請求項1の活性炭の洗浄
方法は、活性炭が充填されて吸着床を形成している活性
炭吸着塔に洗浄液を通液して活性炭を洗浄する方法にお
いて、前記吸着塔にアルカリ水溶液を通液してアルカリ
洗浄し、次いで温水を通水して洗浄することを特徴とす
る。
The method for cleaning activated carbon according to claim 1 is a method for cleaning activated carbon by passing a cleaning liquid through an activated carbon adsorption tower which is filled with activated carbon to form an adsorption bed. It is characterized in that an alkaline aqueous solution is passed through the tower for alkali washing, and then hot water is passed for washing.

【0011】請求項2の活性炭の洗浄方法は、請求項1
において、活性炭吸着塔にアニオン交換樹脂塔が併設さ
れており、前記アルカリ水溶液として、該アニオン交換
樹脂塔の再生排液を用いることを特徴とする。
The method for cleaning activated carbon according to claim 2 is the method according to claim 1.
In the above, the activated carbon adsorption tower is provided with an anion exchange resin tower, and the recycled waste liquid of the anion exchange resin tower is used as the alkaline aqueous solution.

【0012】以下、図面を参照して本発明を詳細に説明
する。
The present invention will be described in detail below with reference to the drawings.

【0013】図1は本発明の活性炭の洗浄方法の一実施
例方法を説明する系統図である。
FIG. 1 is a system diagram for explaining an embodiment of a method for cleaning activated carbon according to the present invention.

【0014】図中、1は活性炭が充填されて吸着床1A
を形成している活性炭吸着塔であり、2はアニオン交換
樹脂が充填されてアニオン交換樹脂床2Aを形成してい
るアニオン交換樹脂塔である。
In the figure, 1 is an adsorption bed 1A filled with activated carbon.
Is an activated carbon adsorption tower, and 2 is an anion exchange resin tower filled with an anion exchange resin to form an anion exchange resin bed 2A.

【0015】11,12,13は通水配管であり、原水
(半導体製造排水等の被処理水)は、配管11より活性
炭吸着塔1、配管12、アニオン交換樹脂塔2を経て処
理され、処理水は配管13より系外へ排出される。
Reference numerals 11, 12, and 13 are water passage pipes, and raw water (water to be treated such as semiconductor manufacturing wastewater) is treated from the pipe 11 through an activated carbon adsorption tower 1, a pipe 12 and an anion exchange resin tower 2 and treated. Water is discharged from the system through the pipe 13.

【0016】21,22,23は再生配管であり、水酸
化ナトリウム(NaOH)水溶液等のアルカリ再生液
が、配管21よりアニオン交換樹脂塔2に供給され、こ
の再生排液は次いで配管22より活性炭吸着塔1に供給
され、活性炭吸着床1Aのアルカリ洗浄を行なった後、
アルカリ洗浄排水は配管23より系外へ排出される。
Reference numerals 21, 22 and 23 are regeneration pipes, and an alkali regeneration liquid such as an aqueous solution of sodium hydroxide (NaOH) is supplied to the anion exchange resin tower 2 through a pipe 21, and this regeneration waste liquid is then activated through a pipe 22. After being supplied to the adsorption tower 1 and washing the activated carbon adsorption bed 1A with an alkali,
The alkaline cleaning waste water is discharged from the system through the pipe 23.

【0017】31,32,33は温水洗浄配管であり、
配管31より導入され熱交換器33で加温された温水
(温純水)は、配管32より活性炭吸着塔1に導入さ
れ、活性炭吸着床1Aを温水洗浄し、洗浄排水は配管3
3より排出されて、貯槽4に回収される。
Reference numerals 31, 32, and 33 are hot water washing pipes,
The warm water (warm pure water) introduced through the pipe 31 and heated by the heat exchanger 33 is introduced through the pipe 32 into the activated carbon adsorption tower 1, and the activated carbon adsorption bed 1A is washed with warm water, and the cleaning drainage is the pipe 3.
It is discharged from 3 and collected in the storage tank 4.

【0018】即ち、本実施例は、アニオン交換樹脂塔が
併設された活性炭吸着塔に本発明を適用した例であり、
活性炭吸着塔のアルカリ洗浄のアルカリ水溶液として、
アニオン交換樹脂塔の再生のために用いたアルカリ再生
液の再生排液を利用するものである。
That is, the present embodiment is an example in which the present invention is applied to an activated carbon adsorption tower provided with an anion exchange resin tower,
As an alkaline aqueous solution for alkaline cleaning of an activated carbon adsorption tower,
The regeneration waste liquid of the alkali regeneration liquid used for regeneration of the anion exchange resin tower is used.

【0019】従って、活性炭吸着塔1の洗浄に当って
は、まず、アニオン交換樹脂塔2の再生処理を行ない、
再生排液を配管22より下向流にて活性炭吸着塔1に供
給してアルカリ洗浄を行なう。アルカリ洗浄終了後、温
水を配管32より上向流にて活性炭吸着塔1に供給して
温水洗浄を行なう。
Therefore, in washing the activated carbon adsorption tower 1, first, the anion exchange resin tower 2 is regenerated.
The regeneration waste liquid is supplied from the pipe 22 to the activated carbon adsorption tower 1 in a downward flow to perform alkali cleaning. After completion of the alkali washing, hot water is supplied to the activated carbon adsorption tower 1 through the pipe 32 in an upward flow to wash the hot water.

【0020】このような方法において、活性炭吸着塔に
供給するアルカリ洗浄液(本実施例ではアニオン交換樹
脂塔の再生排液)の通水量、通水時間等には特に制限は
なく、アニオン交換樹脂塔の再生条件に準じて適宜設定
すればよい。一般には、活性炭吸着塔のアルカリ洗浄液
のpHは10以上であることが好ましい。なお、アニオ
ン交換樹脂塔の再生排液は通常の場合pH10以上であ
る。
In such a method, there is no particular limitation on the amount of water passed through the alkali cleaning liquid (in this embodiment, the regenerated waste liquid of the anion exchange resin tower) supplied to the activated carbon adsorption tower, the water passage time, and the like. It may be set as appropriate according to the reproduction conditions of. Generally, it is preferable that the pH of the alkaline cleaning liquid in the activated carbon adsorption tower is 10 or more. The pH of the recycled waste liquid from the anion exchange resin tower is usually 10 or higher.

【0021】また、活性炭吸着塔のアルカリ洗浄液の通
水方向にも特に制限はなく、上向流、下向流を問わない
が、望ましくは下向流とするのが良い。なお、アニオン
交換樹脂塔の再生液の通水方向も下向流が望ましい。
Further, the water flow direction of the alkali cleaning liquid in the activated carbon adsorption tower is not particularly limited, either upward flow or downward flow is preferable, but downward flow is preferable. In addition, it is desirable that the regenerant in the anion exchange resin tower also flows downward in the water flow direction.

【0022】活性炭吸着塔のアルカリ洗浄後の温水洗浄
の温水としては、水温50〜60℃のものを用いること
ができる。水温はこの温度より高くても良いが、加温コ
ストの面から50〜60℃とするのが好ましい。活性炭
吸着塔が、半導体製造排水再生用の活性炭吸着塔である
場合には、この温水としては、特に加温純水を用いる。
As hot water for washing with hot water after washing the activated carbon adsorption tower with alkali, water having a water temperature of 50 to 60 ° C. can be used. The water temperature may be higher than this temperature, but it is preferably 50 to 60 ° C. from the viewpoint of heating cost. When the activated carbon adsorption tower is an activated carbon adsorption tower for recycling semiconductor manufacturing wastewater, heated pure water is particularly used as the hot water.

【0023】また、この温水洗浄の通水条件はLV=5
〜20m/hr、特に5〜10m/hr、通水量10〜
30BVとするのが好ましい。この温水洗浄の通水方向
は、上記アルカリ洗浄の通水方向に対して並流通水であ
っても向流通水であってもいずれでも良い。
The water flow condition for this hot water washing is LV = 5.
-20 m / hr, especially 5-10 m / hr, water flow rate 10
It is preferably 30 BV. The water flow direction of this warm water washing may be either parallel flow water or counter flow water with respect to the water flow direction of the alkali washing.

【0024】なお、図示の実施例は、本発明の一実施例
であって、本発明はその要旨を超えない限り、何ら図示
の方法に限定されるものではない。
The illustrated embodiment is an embodiment of the present invention, and the present invention is not limited to the illustrated method insofar as it does not exceed the gist of the invention.

【0025】例えば、図示の如く、アニオン交換樹脂塔
の再生排液を利用する場合において、必ずしも活性炭吸
着塔の後段にアニオン交換樹脂塔が設けられているもの
に限られず、両塔の間に他の装置が組み入れられていて
も良い。また、その設置形態も任意である。
For example, as shown in the figure, in the case of utilizing the regenerated effluent of the anion exchange resin tower, the anion exchange resin tower is not necessarily provided in the latter stage of the activated carbon adsorption tower, and another one may be provided between the two towers. The device may be incorporated. Further, its installation form is also arbitrary.

【0026】もちろん、本発明はアニオン交換樹脂塔が
系内に設けられていない活性炭吸着塔に適用することも
でき、その場合には、アルカリ洗浄にpH10以上のN
aOH水溶液等を用いれば良い。
Of course, the present invention can also be applied to an activated carbon adsorption column in which an anion exchange resin column is not provided in the system. In that case, N of pH 10 or more is used for alkali washing.
An aOH aqueous solution or the like may be used.

【0027】[0027]

【作用】アルカリ洗浄と温水洗浄とを併用することによ
る相乗効果でスライム汚染された活性炭の洗浄・殺菌を
著しく効率的に行なうことができる。また、温水とし
て、比較的低温のものを用いることができる上に、洗浄
後の処理水の水質の立上り性も良い。
The synergistic effect of the combined use of alkali washing and warm water washing makes it possible to wash and sterilize activated carbon contaminated with slime remarkably efficiently. Further, as the hot water, one having a relatively low temperature can be used, and the water quality of the treated water after washing is also excellent in rising property.

【0028】請求項2の方法によれば、アニオン交換樹
脂塔の再生排液を有効利用することができる。
According to the method of claim 2, the recycled waste liquid of the anion exchange resin tower can be effectively used.

【0029】[0029]

【実施例】以下に具体的な実施例及び比較例を挙げて、
本発明をより具体的に説明する。
[Examples] Specific examples and comparative examples are given below,
The present invention will be described more specifically.

【0030】なお、いずれの例においても、下記仕様の
活性炭吸着塔及びアニオン交換樹脂塔が併設された系に
おいて、イソプロピルアルコール:2mg−TOC/
l,NaHCO3 :10mg/lを純水に溶解した原水
を10リットル/hrの条件で約10日間下向流にて通
水し、差圧が0.2kgf/cm2 となった活性炭吸着
塔について洗浄を行なった。
In any of the examples, isopropyl alcohol: 2 mg-TOC / in a system in which an activated carbon adsorption tower of the following specifications and an anion exchange resin tower were installed side by side.
l, NaHCO 3: The raw water to 10 mg / l was dissolved in pure water was passed through at about 10 days downflow under the condition 10 liters / hr, the activated carbon adsorption tower pressure difference became 0.2 kgf / cm 2 Was washed.

【0031】活性炭吸着塔 活性炭:クラレコールKW(10/32メッシュ)
((株)クラレ製) 活性炭充填量:1リットル カラム:直径5cm×高さ80cmアニオン交換樹脂塔 アニオン交換樹脂:ダイヤイオンSA10A(三菱化成
(株)製) アニオン交換樹脂充填量:0.5リットル カラム:直径5cm×高さ80cm 実施例1 アニオン交換樹脂塔については、3日に1回の頻度にて
4%NaOH水溶液(50g−NaOH/l)を用いて
30分間再生を行なった。
Activated carbon adsorption tower Activated carbon: Kuraray Coal KW (10/32 mesh)
(Manufactured by Kuraray Co., Ltd.) Activated carbon filling amount: 1 liter Column: Diameter 5 cm x height 80 cm Anion exchange resin tower Anion exchange resin: Diaion SA10A (manufactured by Mitsubishi Kasei Co., Ltd.) Anion exchange resin filling amount: 0.5 liter Column: diameter 5 cm × height 80 cm Example 1 The anion exchange resin column was regenerated for 30 minutes using a 4% NaOH aqueous solution (50 g-NaOH / l) once every three days.

【0032】活性炭吸着塔の洗浄にあたっては、まず、
活性炭吸着塔に、このアニオン交換樹脂塔の再生排液の
1回分を下向流にて通水してアルカリ洗浄を行なった。
その後、60℃の温水(加温純水)をLV=10m/h
rで15分間上向流にて通水して洗浄した。
In cleaning the activated carbon adsorption tower, first,
A single portion of the regenerated waste liquid of the anion exchange resin tower was passed through the activated carbon adsorption tower in a downward flow to carry out alkali washing.
Then, warm water (heated pure water) at 60 ° C. was applied to LV = 10 m / h.
It was washed by flowing water at r for 15 minutes in an upward flow.

【0033】この洗浄後、活性炭吸着塔の差圧の回復
率、原水の通水を再開してから10時間後の活性炭吸着
塔出口水の生菌数を調べ、結果を表1に示した。
After this washing, the recovery rate of the differential pressure of the activated carbon adsorption tower and the viable cell count of the activated carbon adsorption tower outlet water 10 hours after restarting the passage of raw water were examined, and the results are shown in Table 1.

【0034】比較例1 実施例1において、活性炭吸着塔のアルカリ洗浄を行な
わず、純水(23℃)をLV=25m/hrで15分間
上向流で通水して逆洗のみを行ない、同様に差圧回復率
及び生菌数を調べ、結果を表1に示した。
Comparative Example 1 In Example 1, the alkali washing of the activated carbon adsorption tower was not carried out, but pure water (23 ° C.) was passed upward at LV = 25 m / hr for 15 minutes to carry out only back washing. Similarly, the differential pressure recovery rate and the viable cell count were examined, and the results are shown in Table 1.

【0035】比較例2 実施例1において、活性炭吸着塔のアルカリ洗浄を行な
わず、60℃の温水をLV=10m/hrで15分間上
向流で通水したこと以外は同様にして、差圧回復率及び
生菌数を調べ、結果を表1に示した。
Comparative Example 2 The pressure difference was the same as in Example 1 except that the activated carbon adsorption tower was not washed with alkali and hot water at 60 ° C. was passed in an upward flow at LV = 10 m / hr for 15 minutes. The recovery rate and the viable cell count were examined, and the results are shown in Table 1.

【0036】比較例3 実施例1において、アルカリ洗浄後、純水(23℃)を
LV=10m/hrで15分間下向流にて通水して洗浄
したこと以外は同様に行なって、差圧回復率及び生菌数
を調べ、結果を表1に示した。
Comparative Example 3 The same procedure as in Example 1 was carried out except that, after the alkali cleaning, pure water (23 ° C.) was passed by a downward flow of LV = 10 m / hr for 15 minutes to perform cleaning. The pressure recovery rate and the viable cell count were examined, and the results are shown in Table 1.

【0037】表1より、本発明の方法によれば、活性炭
吸着塔の洗浄・殺菌を効率的に行なって、差圧を十分に
回復させるとともに、生菌数を著しく低減できることが
明らかである。
From Table 1, it is clear that according to the method of the present invention, the activated carbon adsorption tower can be efficiently washed and sterilized to sufficiently recover the differential pressure and to significantly reduce the viable cell count.

【0038】これに対して、アルカリ洗浄を行なわず、
冷水洗浄のみの比較例1では差圧回復率、生菌数ともに
良好な結果が得られない。また、温水洗浄のみの比較例
2では、生菌数はある程度低減するが差圧回復率は良く
ない。更に、アルカリ洗浄を行なってもその後、冷水で
洗浄する比較例3では、差圧はある程度回復するが生菌
数が多い。
On the other hand, without alkali cleaning,
In Comparative Example 1 in which only cold water washing is performed, good results cannot be obtained in terms of differential pressure recovery rate and viable cell count. In Comparative Example 2 in which only washing with warm water is performed, the viable cell count is reduced to some extent, but the differential pressure recovery rate is not good. Furthermore, in Comparative Example 3 in which the alkaline cleaning is performed and then the cleaning is performed with cold water, the differential pressure recovers to some extent, but the number of viable bacteria is large.

【0039】[0039]

【表1】 [Table 1]

【0040】[0040]

【発明の効果】以上詳述した通り、本発明の方法によれ
ば、活性炭吸着塔に充填された活性炭を容易かつ効率的
に洗浄・殺菌することができ、 活性炭吸着塔の差圧を高度に回復させると共に、差
圧の上昇速度を低減することができる。 活性炭吸着塔流出水中の生菌数を著しく低減するこ
とができる。 活性炭吸着塔の洗浄頻度を低減することができる。 温水として高温水を使用する必要がなく、比較的低
温の温水で殺菌が可能である。 洗浄後の処理水の水質立上り性も良好である。 等の優れた効果が達成される。
As described in detail above, according to the method of the present invention, the activated carbon packed in the activated carbon adsorption tower can be easily and efficiently washed and sterilized, and the differential pressure of the activated carbon adsorption tower can be enhanced. It is possible to recover and reduce the rising speed of the differential pressure. The number of viable bacteria in the effluent of the activated carbon adsorption tower can be significantly reduced. The cleaning frequency of the activated carbon adsorption tower can be reduced. It is not necessary to use high temperature water as warm water, and sterilization can be performed with relatively low temperature warm water. The water quality of treated water after washing is also good. An excellent effect such as is achieved.

【0041】請求項2の方法によれば、活性炭吸着塔に
併設されたアニオン交換樹脂塔の再生排液を利用するこ
とができ、また、アニオン交換樹脂塔の再生と共に、活
性炭吸着塔のアルカリ洗浄も実施できる。
According to the method of claim 2, it is possible to utilize the regenerated effluent of the anion exchange resin tower provided adjacent to the activated carbon adsorption tower, and to regenerate the anion exchange resin tower and to wash the activated carbon adsorption tower with alkali. Can also be implemented.

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

【図1】本発明の活性炭の洗浄方法の一実施例方法を説
明する系統図である。
FIG. 1 is a system diagram for explaining a method of an embodiment of the activated carbon cleaning method of the present invention.

【符号の説明】[Explanation of symbols]

1 活性炭吸着塔 1A 活性炭吸着床 2 アニオン交換樹脂塔 2A アニオン交換樹脂床 3 熱交換器 1 Activated carbon adsorption tower 1A Activated carbon adsorption bed 2 Anion exchange resin tower 2A Anion exchange resin bed 3 Heat exchanger

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 活性炭が充填されて吸着床を形成してい
る活性炭吸着塔に洗浄液を通液して活性炭を洗浄する方
法において、 前記吸着塔にアルカリ水溶液を通液してアルカリ洗浄
し、次いで温水を通水して洗浄することを特徴とする活
性炭の洗浄方法。
1. A method for washing a activated carbon by passing a washing liquid through an activated carbon adsorption tower which is filled with activated carbon to form an adsorption bed, wherein an alkaline aqueous solution is passed through the adsorption tower for alkali washing, A method for washing activated carbon, which comprises washing with warm water.
【請求項2】 請求項1において、活性炭吸着塔にアニ
オン交換樹脂塔が併設されており、前記アルカリ水溶液
として、該アニオン交換樹脂塔の再生排液を用いること
を特徴とする活性炭の洗浄方法。
2. The method for cleaning activated carbon according to claim 1, wherein an anion exchange resin tower is provided in addition to the activated carbon adsorption tower, and the recycled waste water of the anion exchange resin tower is used as the alkaline aqueous solution.
JP30360992A 1992-11-13 1992-11-13 Method for washing activated charcoal Pending JPH06142646A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP30360992A JPH06142646A (en) 1992-11-13 1992-11-13 Method for washing activated charcoal

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP30360992A JPH06142646A (en) 1992-11-13 1992-11-13 Method for washing activated charcoal

Publications (1)

Publication Number Publication Date
JPH06142646A true JPH06142646A (en) 1994-05-24

Family

ID=17923058

Family Applications (1)

Application Number Title Priority Date Filing Date
JP30360992A Pending JPH06142646A (en) 1992-11-13 1992-11-13 Method for washing activated charcoal

Country Status (1)

Country Link
JP (1) JPH06142646A (en)

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