JPH0655177A - Electrochemical treatment apparatus - Google Patents

Electrochemical treatment apparatus

Info

Publication number
JPH0655177A
JPH0655177A JP20871291A JP20871291A JPH0655177A JP H0655177 A JPH0655177 A JP H0655177A JP 20871291 A JP20871291 A JP 20871291A JP 20871291 A JP20871291 A JP 20871291A JP H0655177 A JPH0655177 A JP H0655177A
Authority
JP
Japan
Prior art keywords
water
treated
storage tank
electrolytic cell
electrochemical treatment
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
JP20871291A
Other languages
Japanese (ja)
Inventor
Nobutaka Goshima
伸隆 五嶋
Hiromi Nozaki
裕美 野崎
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.)
Konica Minolta Inc
Original Assignee
Konica Minolta Inc
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 Konica Minolta Inc filed Critical Konica Minolta Inc
Priority to JP20871291A priority Critical patent/JPH0655177A/en
Publication of JPH0655177A publication Critical patent/JPH0655177A/en
Pending legal-status Critical Current

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  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

PURPOSE:To achieve the reduction of cost to a large extent, to also save electric power and to always obtain purified water in an apparatus supplying water to be treated in a storage tank to a fixed bed type electrolytic cell to electrochemically treat the same, by arranging the electrolytic cell in the storage tank. CONSTITUTION:Water to be treated is supplied to a storage tank 8 through a supply pipe 11 to be electrochemically treated in an electrolytic cell main body 2 and the purified water 9 is taken out of a taking-out pipe 12 to be supplied, for example, as the cooling water of a heat exchanger. Since there is no circulating line between the electrolytic cell main body 2 and the storage tank 8 in this electrochemical treatment apparatus, the whole of the apparatus is miniaturized to reduce an establishment area and, since the water 9 to be treated in the storage tank 8 is always directly or indirectly in contact with the electrolytic cell, the purified water 9 to be treated is not contaminated by the propagation of bacteria in the storage tank 8.

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、熱交換器用冷却水や水
道水等の被処理水を電気化学的に処理する電気化学的処
理装置に関し、より詳細には三次元電極を使用して被処
理水の電気化学的処理を行うためのより小型化を可能に
した電気化学的処理装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an electrochemical treatment apparatus for electrochemically treating water to be treated such as cooling water for heat exchangers and tap water, and more particularly, it uses a three-dimensional electrode. The present invention relates to an electrochemical treatment device that can be downsized for performing an electrochemical treatment of treated water.

【0002】[0002]

【従来技術】従来から各種用途に多種類の水溶液や他の
物質を溶解していない単独の水が使用されている。これ
らの水溶液等は溶質が適度な養分を提供し、あるいは該
水溶液の液温が繁殖に好ましい比較的高温度であると、
細菌等の微生物が繁殖して該微生物は前記水溶液等の性
能劣化を起こしたり、又製品に悪影響を与えたり、処理
装置内に浮遊したり蓄積して処理装置の機能を損なうこ
とが多い。通常の水道水中の微生物数は20個/ミリリッ
トル以下であるが、この水道水を例えば熱交換器用冷却
水として使用すると前記微生物が飛躍的に繁殖して配管
の腐食や悪臭の発生が生ずる。これらの現象を防止する
ために従来は防黴剤や沈澱抑制剤等の各種薬剤を被処理
水中に投入したり各種フィルタを配管途中に設置したり
しているが、前記薬剤投入は前述の通り薬剤の残留によ
る被処理水への悪影響や薬剤使用のコスト面での問題点
が指摘されている。更に添加薬剤に対する抗菌が暫くす
ると発生し、次の薬剤を検討したり必要量以上に多量の
薬剤を供給する等の必要が生ずるという問題点を抱えて
いる。
2. Description of the Related Art Conventionally, various kinds of aqueous solutions and single water in which other substances are not dissolved have been used for various purposes. These aqueous solutions, etc., the solute provides an appropriate nutrient, or the liquid temperature of the aqueous solution is relatively high temperature preferable for breeding,
In many cases, microorganisms such as bacteria propagate and cause deterioration of the performance of the aqueous solution or the like, adversely affect the product, and floating or accumulating in the treatment device to impair the function of the treatment device. Usually, the number of microorganisms in tap water is 20 / ml or less, but when this tap water is used as cooling water for heat exchangers, the microorganisms remarkably propagate and corrosion of pipes and generation of malodor occur. In order to prevent these phenomena, conventionally, various chemicals such as antifungal agents and precipitation inhibitors have been put into the water to be treated and various filters have been installed in the middle of the piping. It has been pointed out that adverse effects on the water to be treated due to residual chemicals and problems in terms of the cost of using chemicals. Furthermore, there is a problem that antibacterial action against the added drug occurs after a while, and it becomes necessary to consider the next drug or supply a larger amount of drug than necessary.

【0003】殺菌剤や防黴剤等の薬剤投入による写真処
理液、プール水、製紙洗浄水、熱交換器冷却水、養魚場
水、薬剤希釈水及び浴場水等の滅菌処理では薬剤の残存
の問題が不可避で該残存薬剤により微生物がもたらす以
外の不都合が生ずることがあり、かつ使用する薬剤も危
険で高価なものであることが多く特に大量処理の必要が
あるプール水、製紙洗浄水及び浴場水等では経済的観点
からもしても、より簡便かつ安全で安価に微生物を含有
する被処理水の滅菌処理を可能にする方法の出現が望ま
れている。そして熱交換器用冷却水の電気化学的処理を
行う場合には炭素質三次元電極等を設置した電解槽を熱
交換器用冷却水の貯槽と別個に設置して両者を循環ライ
ンで連結し、貯槽内の冷却水を前記電解槽に循環させ冷
却水の滅菌を行うことが提案されている。そしてプール
水や製紙洗浄水等の比較的大量の水処理を必要とする被
処理水の場合にも該被処理水を貯槽(プールや洗浄水
槽)に貯留し、該貯留した被処理水を電解槽に循環して
処理を行うことが提案されている。しかしこの循環処理
では循環ラインを設置するため大きな空間と多大なコス
トを要するという欠点があり、更に循環ライン中での微
生物の繁殖が問題になることもある。
In the sterilization treatment of photographic processing liquid, pool water, papermaking washing water, heat exchanger cooling water, fish farm water, chemical dilution water, bath water, etc., by adding chemicals such as bactericides and fungicides, the chemicals remain. The problem is unavoidable and the residual chemicals may cause inconveniences other than those caused by microorganisms, and the chemicals used are often dangerous and expensive. With respect to water and the like, from an economical point of view, the emergence of a method that makes it possible to sterilize treated water containing microorganisms more simply, safely, and inexpensively is desired. When electrochemically treating the cooling water for the heat exchanger, an electrolytic cell equipped with a three-dimensional carbonaceous electrode is installed separately from the storage tank for the cooling water for the heat exchanger, and the two are connected by a circulation line. It has been proposed to circulate the cooling water in the electrolyzer to sterilize the cooling water. In the case of treated water that requires a relatively large amount of water treatment such as pool water and papermaking wash water, the treated water is stored in a storage tank (pool or wash water tank) and the stored treated water is electrolyzed. It has been proposed to circulate the solution in a tank for treatment. However, this circulation treatment has a drawback that it requires a large space and a great cost because a circulation line is installed, and further, there is a problem that the reproduction of microorganisms in the circulation line becomes a problem.

【0004】又飲料水は、貯水池等の水源に貯水された
水を浄水場で滅菌処理した後、各家庭や飲食店等に上水
道を通して供給される。飲料水の前記滅菌は塩素ガスに
よる処理が一般的であるが、該塩素処理によると飲料水
の滅菌は比較的良好に行われる反面、残留塩素の影響に
より処理された飲料水に異物質が混和したような違和感
が生じて天然の水の有するまろやかさが損なわれるとい
う欠点が生ずる。飲料水は人間の健康に直結するもの
で、それに含有される細菌の殺菌や黴の繁殖の防止つま
り微生物の死滅除去は不可欠であり、該殺菌や防黴の方
法としては前述の塩素による方法が主流である。しかし
都市部の水道滅菌はその原水となる河川水、湖水等が各
種有機物等で汚染され微生物の死滅に必要な量以上の塩
素を添加するため、有機ハロゲン化物、次亜塩素酸イオ
ン及び残留塩素等の有効塩素成分を生起していわゆるカ
ルキ臭が生じ、処理後の飲料水等の味が悪くなるという
欠点があり、このカルキ臭を除去するに該カルキ臭源で
ある次亜塩素酸イオン(有効塩素)を活性炭等に吸着さ
せ、かつ活性炭の構成分子である炭素を酸化することで
有効塩素を還元処理する方法が使用されていた。しかし
この方法では、活性炭の吸着能力の限界があり、しばら
く使用すると有効塩素分解が生じなくなるという寿命の
点で致命的な欠点があり、又活性炭の交換といった煩雑
な操作とコストが必要であるとともに、完全なカルキ臭
の除去が達成できないことがある。
The drinking water is supplied to each home, restaurant, etc. through water supply after sterilizing the water stored in a water source such as a reservoir. The above-mentioned sterilization of drinking water is generally treated with chlorine gas, but sterilization of drinking water is relatively good according to the chlorine treatment, while foreign substances are mixed in the treated drinking water due to the influence of residual chlorine. Such a discomfort occurs and the mellowness of natural water is impaired. Drinking water is directly related to human health, and sterilization of bacteria contained in it and prevention of reproduction of mold, that is, killing and removal of microorganisms are indispensable.As a method of sterilizing and preventing mold, the above-mentioned chlorine method is used. Mainstream. However, in tap water sterilization in urban areas, the raw water, such as river water and lake water, is contaminated with various organic substances and more chlorine is added than is necessary to kill microorganisms.Therefore, organic halides, hypochlorite ions and residual chlorine are added. There is a drawback that so-called chlorine odor is generated by generating effective chlorine components such as, and the taste of drinking water after treatment is deteriorated. To remove this chlorine odor, the hypochlorite ion which is the source of the chlorine odor ( A method has been used in which available chlorine is adsorbed on activated carbon and the like, and carbon that is a constituent molecule of activated carbon is oxidized to reduce available chlorine. However, in this method, there is a limit to the adsorption capacity of activated carbon, and there is a fatal defect in terms of the lifetime that effective chlorine decomposition does not occur after a while being used, and in addition, complicated operations such as replacement of activated carbon and cost are required. , It may not be possible to achieve complete removal of odor.

【0005】従って前述の通り人体に有害な有機塩素化
合物や飲料水の味を損ない易い次亜塩素酸イオン等を生
じさせ易い塩素処理に代わり得る人体に害がなくかつ天
然水に近い味を有する飲料水の処理方法が要請されてい
る。これらの現象を防止するために従来は防黴剤や沈澱
抑制剤等の各種薬剤を被処理水中に投入したり各種フィ
ルタを配管途中に設置したりしているが、前記薬剤投入
は前述の通り薬剤の残留による被処理水への悪影響や薬
剤使用のコスト面での問題点が指摘されている。更に添
加薬剤に対する抗菌が暫くすると発生し、次の薬剤を検
討する必要が生ずる。このような従来技術の欠点を解消
するために、本出願人は前記各被処理水を電気化学的に
処理することにより該被処理水の滅菌やカルキ臭の除去
を行う方法を提案した(特願平1−326846号、特願平2-
236723号)。この方法による電気化学的処理では薬剤等
の被処理水中への残存を生じさせることなく確実に被処
理水の改質を行うことができる。
Therefore, as described above, it has a taste similar to that of natural water, which does not harm the human body and can be replaced with chlorine treatment which easily produces hypochlorite ions and the like, which are liable to harm the human body and taste of drinking water. A method of treating drinking water is required. In order to prevent these phenomena, conventionally, various chemicals such as antifungal agents and precipitation inhibitors have been put into the water to be treated and various filters have been installed in the middle of the piping. It has been pointed out that adverse effects on the water to be treated due to residual chemicals and problems in terms of the cost of using chemicals. Furthermore, antibacterial action against the added drug occurs after a while, and it becomes necessary to consider the next drug. In order to solve the above-mentioned drawbacks of the prior art, the applicant has proposed a method of electrochemically treating each of the treated waters to sterilize the treated waters or remove the odor of chlorine. Japanese Patent Application No. 1-326846, Japanese Patent Application No. 2-
No. 236723). In the electrochemical treatment by this method, the water to be treated can be surely reformed without causing chemicals and the like to remain in the water to be treated.

【0006】この電気化学的処理により薬剤を使用する
ことなく飲料水等の滅菌を初めとする改質処理を行うこ
とができるが、これらの電気化学的処理は大量の飲料水
の処理を意図し、従って使用する電解槽も大型で該電解
槽の設置場所でしか飲料水等の改質処理を行うことがで
きず、電気化学的に処理された清浄な飲料水をポット等
に入れて保存しても該ポット中での微生物の繁殖が生じ
て飲料水の汚染が生ずることがある。特に水事情の悪い
海外では水道水中に各種雑菌が多く含まれかつ異臭を伴
うことがあり蛇口からの水道水をそのまま摂取すると味
覚を損なうだけでなく下痢や腹痛等を誘発することがあ
り、海外では消毒済の飲料水以外は飲まないことが常識
となっている。しかし飲料水の摂取を抑止するにも限度
があり、特に気温の高い地方では非常に高価な飲料水を
購入しなければならないという欠点がある。
[0006] By this electrochemical treatment, modification treatment such as sterilization of drinking water can be performed without using chemicals, but these electrochemical treatments are intended to treat a large amount of drinking water. Therefore, the electrolytic cell to be used is also large, and the reforming treatment of drinking water and the like can be performed only at the place where the electrolytic cell is installed, and the clean electrochemically treated drinking water is put in a pot or the like and stored. However, there is a case where microorganisms propagate in the pot and pollute drinking water. Especially in overseas where the water situation is poor, various miscellaneous bacteria are contained in tap water and may have an unpleasant odor, and ingesting tap water from the faucet as it is may not only impair the taste but also induce diarrhea and abdominal pain. It is common sense that only drink water that has been disinfected. However, there are limits to how much drinking water can be taken in, and there is the disadvantage that very expensive drinking water must be purchased, especially in areas with high temperatures.

【0007】[0007]

【発明の目的】本発明は、前述の従来技術の欠点を解消
し、貯槽に貯留された被処理水を電気化学的に処理でき
る比較的小型の処理装置を提供することを目的とする。
SUMMARY OF THE INVENTION It is an object of the present invention to solve the above-mentioned drawbacks of the prior art and to provide a relatively small-sized treatment apparatus capable of electrochemically treating the water to be treated stored in the storage tank.

【0008】[0008]

【問題点を解決するための手段】本発明は、貯槽内に貯
留した被処理水を固定床型電解槽に供給し該被処理水を
電気化学的に処理する装置において、前記電解槽を前記
貯槽内に設置したことを特徴とする電気化学的処理装置
である。なお本発明では電極表面上で実質的な酸化還元
反応のような電気化学反応を生起していないことがある
ので本発明方法に使用される槽は電気化学的処理装置と
いうべきであるが、一般呼称に従って電解槽と称する。
The present invention is an apparatus for supplying the water to be treated stored in a storage tank to a fixed bed type electrolytic cell to electrochemically treat the water to be treated, wherein It is an electrochemical treatment device characterized by being installed in a storage tank. In the present invention, since the electrochemical reaction such as the substantial redox reaction may not occur on the electrode surface, the tank used in the method of the present invention should be an electrochemical treatment apparatus, but It is called an electrolytic cell according to the name.

【0009】以下本発明を詳細に説明する。本発明は従
来のように、被処理水の電気化学的処理用電解槽を被処
理水の貯槽と別個に設置し被処理水を前記電解槽及び貯
槽間で循環させる形態に代えて、電解槽を貯槽内に設置
することにより循環に要するラインを不要としかつ貯槽
内での清浄な被処理水の汚染を防止することにより常に
清浄な被処理水を提供できる電気化学的処理装置を提供
することを特徴とする。本電解槽は特に被処理水の滅菌
や飲料水中のカルキ臭除去に有効であり、カルキ臭を有
する飲料水を例えば炭素電極を使用する三次元電極式電
解槽に供給し該電解槽に直流又は交流電圧を印加し前記
被処理水中の微生物の滅菌処理や飲料水中のカルキ臭成
分の分解を行うことができる。なお上記微生物には、細
菌(バクテリア)、菌、糸状菌(黴)、大腸菌、酵母、
変形菌、単細胞の藻類、原生動物、ウイルス等が含まれ
る。本発明装置では、固定床型電解槽を貯槽内に収容す
るため該貯槽は前記電解槽より十分に大きく貯槽内の被
処理水が貯槽内で対流等により循環して前記電解槽内を
流通し電気化学的に処理されなければならない。該被処
理水を固定床型三次元電極電解槽に供給すると、該被処
理水中の微生物は液流動によって前記電解槽の陽極や陰
極あるいは後述する誘電体等に接触しそれらの表面で高
電位のエネルギー供給を受け強力な酸化還元反応が微生
物細胞内で生じ、その活動が弱まったり微生物自身が死
滅して滅菌が行われると考えられる。
The present invention will be described in detail below. The present invention is different from the conventional one in which the electrolytic cell for electrochemical treatment of the water to be treated is installed separately from the reservoir of the water to be treated, and the water to be treated is circulated between the electrolytic vessel and the tank, instead of the electrolytic vessel. To provide an electrochemical treatment device which can always provide clean treated water by preventing the line required for circulation from being installed in the storage tank and preventing contamination of clean treated water in the storage tank. Is characterized by. This electrolytic cell is particularly effective for sterilizing the water to be treated and removing the chlorine odor in drinking water, and supplies drinking water having a chlorine odor to a three-dimensional electrode type electrolytic cell using a carbon electrode for direct current or By applying an AC voltage, it is possible to sterilize the microorganisms in the water to be treated and decompose the chlorine odor component in the drinking water. The above microorganisms include bacteria, fungi, fungi (mold), E. coli, yeast,
Includes morphobacterium, unicellular algae, protozoa, virus and the like. In the device of the present invention, since the fixed bed type electrolytic cell is housed in the storage tank, the storage tank is sufficiently larger than the electrolytic tank, and the water to be treated in the storage tank circulates in the storage tank by convection or the like and flows in the electrolytic tank. Must be electrochemically processed. When the water to be treated is supplied to a fixed bed type three-dimensional electrode electrolyzer, the microorganisms in the water to be treated come into contact with the anode or cathode of the electrolyzer or a dielectric substance described later due to the liquid flow and have a high potential on their surface. It is considered that a strong redox reaction occurs in the microbial cells by receiving energy supply, the activity is weakened, and the microbial cells themselves are killed to perform sterilization.

【0010】本発明の電気化学的処理装置の貯槽は、比
較的大型の熱交換器用冷却水用貯留タンクやプール及び
浴場の他に,ポット等の小型の飲料水の貯留器を含み、
前記貯槽は前記電解槽内の被処理水に好ましくは全体が
浸漬するように設置するが、該被処理水と前記三次元電
極の接触が十分に行われるのであれば部分的な浸漬のみ
でもよい。ポット内に電解槽を設置する場合には該ポッ
トの被処理水の容量に適したサイズの電解槽をなるべく
ポットの下部に設置する。本発明の電気化学的処理装置
の電極は一般に固定床型三次元電極好ましくは多孔質三
次元炭素電極と給電用電極を含み、これらの他に補助電
極を設置してもよい。三次元電極の材質は炭素系材料の
他に、白金族金属酸化物被覆チタン材(寸法安定性電
極)、白金被覆チタン材、ニッケル、フェライト等を使
用することができる。前記炭素系材料は、前記被処理水
が透過可能な多孔質炭素材料、例えば粉状、粒状、フェ
ルト状、織布状、多孔質ブロック状等の形状を有する活
性炭、グラファイト、炭素繊維等の炭素系材料、あるい
は該炭素系材料に貴金属のコーティングを施した材料か
ら選択することができる。このように三次元電極を構成
する材料は特に限定されず、従来使用されている任意の
電極材料の使用できるが、炭素系材料を使用することが
最も望ましい。該炭素系材料は導体抵抗が小さく過電圧
が高いという三次元電極の要件を満足する材料であり、
更に該炭素系材料は毒性が全くなくかつイオンやその水
酸化物を形成しないため飲料水等の体内に摂取される被
処理水の処理用として望ましい。又表面積が莫大であり
電解質や微生物あるいは有効塩素成分が接触する機会が
非常に大きくなるとともに吸着能力も作用して処理効率
が大幅に上昇する。更に炭素系材料は安価であり、他の
金属材料極と異なり電解を停止しても腐食が生じないた
め、経済的にも操作性の面からも有利である。なお炭素
系材料を分極させて使用する場合の該炭素系材料(誘電
体)はその誘電率が高いほど分極度が高いので有効に陽
陰極が生成し、被処理水の処理を効率良く行うことがで
きる。
The storage tank of the electrochemical treatment apparatus of the present invention includes a relatively large cooling water storage tank for a heat exchanger, a pool and a bath, and a small drinking water storage such as a pot.
The storage tank is preferably installed so as to be entirely immersed in the water to be treated in the electrolytic tank, but only partial immersion may be performed if the water to be treated and the three-dimensional electrode are sufficiently contacted with each other. . When an electrolytic cell is installed in the pot, an electrolytic cell having a size suitable for the capacity of the water to be treated in the pot is installed in the lower part of the pot as much as possible. The electrodes of the electrochemical treatment apparatus of the present invention generally include a fixed bed type three-dimensional electrode, preferably a porous three-dimensional carbon electrode and a feeding electrode, and an auxiliary electrode may be installed in addition to these. As the material of the three-dimensional electrode, a platinum group metal oxide coated titanium material (dimensional stability electrode), a platinum coated titanium material, nickel, ferrite and the like can be used in addition to the carbon-based material. The carbon-based material is a porous carbon material that is permeable to the water to be treated, such as activated carbon having a shape such as powder, granules, felt, woven cloth, or porous block, carbon such as graphite or carbon fiber. It can be selected from a group-based material or a material obtained by coating the carbon-based material with a noble metal. Thus, the material forming the three-dimensional electrode is not particularly limited, and any conventionally used electrode material can be used, but it is most preferable to use a carbon-based material. The carbon-based material is a material that satisfies the requirement of the three-dimensional electrode that the conductor resistance is small and the overvoltage is high,
Further, since the carbonaceous material has no toxicity and does not form ions or hydroxides thereof, it is desirable for treatment of water to be treated such as drinking water to be ingested into the body. Further, since the surface area is enormous, the chances of contact with electrolytes, microorganisms or effective chlorine components become very large, and the adsorption capacity also acts to greatly increase the treatment efficiency. Further, the carbonaceous material is inexpensive, and unlike other metal material electrodes, corrosion does not occur even if the electrolysis is stopped, which is advantageous from the economical and operability viewpoint. When a carbon-based material is polarized and used, the higher the dielectric constant of the carbon-based material (dielectric), the higher the degree of polarization. Therefore, a positive and negative electrode is effectively generated, and the treated water is treated efficiently. You can

【0011】前記誘電体として活性炭、グラファイト、
炭素繊維等の炭素系材料を使用しかつ陽極から酸素ガス
を発生させながら被処理水を処理する場合には、前記誘
電体が酸素ガスにより酸化され炭酸ガスとして溶解する
ことがある。これを防止するためには前記誘電体の陽分
極する側にチタン等の基材上に酸化イリジウム、酸化ル
テニウム等の白金族金属酸化物を被覆し通常不溶性金属
電極として使用される多孔質材料あるいはフェライト被
覆層を接触状態で設置し、酸素発生が主として該多孔質
材料等の上で生ずるようにすればよい。このような材料
から成る例えば円板状の1個又は複数個の誘電体(三次
元電極)を直流又は交流電場内に置き、両端に設置した
平板状又はエキスパンドメッシュ状やパーフォレーティ
ッドプレート状等の多孔板体から成る給電用電極間に直
流電圧あるいは交流電圧を印加して前記誘電体を分極さ
せ該誘電体の一端及び他端にそれぞれ陽極及び陰極を形
成させて成る三次元電極を収容した複極式固定床型電解
槽とすることが可能である。この他に給電用電極と同一
電位の単一の陽極及び陰極を設置する単極式固定床電解
槽も使用することができる。被処理水の電気化学的処理
に際しては該被処理水がこの三次元電極に可能な限り接
触することが必要であり、かつ貯槽内の被処理水がまん
べんなく前記三次元電極に接触することが望ましい。本
発明装置では前記電解槽が貯槽内に設置され被処理水が
常に前記三次元電極に接触し前者の要望は十分に満たし
ているが、後者の要望は必ずしも満たされない。従って
貯槽内に攪拌用のプロペラ等を設置して該貯槽内の被処
理水を対流等により循環させ電解槽内を流通させること
が好ましい。
As the dielectric, activated carbon, graphite,
When a carbon-based material such as carbon fiber is used and the water to be treated is treated while generating oxygen gas from the anode, the dielectric may be oxidized by oxygen gas and dissolved as carbon dioxide gas. In order to prevent this, a porous material ordinarily used as an insoluble metal electrode by coating a platinum group metal oxide such as iridium oxide or ruthenium oxide on a substrate such as titanium on the side of the dielectric which is positively polarized or The ferrite coating layer may be placed in contact with each other so that oxygen generation mainly occurs on the porous material or the like. For example, one or a plurality of disk-shaped dielectrics (three-dimensional electrodes) made of such a material are placed in a DC or AC electric field, and a flat plate, an expanded mesh, a perforated plate, or the like installed at both ends. A DC voltage or an AC voltage is applied between the power feeding electrodes made of a porous plate to polarize the dielectric and form a positive electrode and a negative electrode at one end and the other end of the dielectric, respectively. It is possible to use a polar fixed-bed electrolytic cell. In addition to this, it is also possible to use a monopolar fixed bed electrolytic cell in which a single anode and cathode having the same potential as the power supply electrode are installed. In the electrochemical treatment of the water to be treated, it is necessary that the water to be treated is in contact with the three-dimensional electrode as much as possible, and it is desirable that the water to be treated in the storage tank is evenly in contact with the three-dimensional electrode. . In the device of the present invention, the electrolytic bath is installed in the storage tank, and the water to be treated is always in contact with the three-dimensional electrode, so that the former demand is sufficiently satisfied, but the latter demand is not always satisfied. Therefore, it is preferable to install a stirring propeller or the like in the storage tank and circulate the water to be treated in the storage tank by convection or the like to circulate in the electrolytic tank.

【0012】又本発明の電解槽では、被処理水中に含有
されることのあるカルシウムイオンやマグネシウムイオ
ンの除去も行うことができる。カルシウムイオンやマグ
ネシウムイオンを含む被処理水を電解槽に供給すると、
カルシウムやマグネシウムの水酸化物等が三次元電極上
特に三次元陰極上に析出しこれを剥離操作等により該陰
極上から除去することにより被処理水中のカルシウムイ
オン等が除去される。逆に陰極上に析出する前記水酸化
物等を除去せずに電気化学的処理を継続すると前記陰極
の目詰まりが生じて被処理水の流通を阻害しかつ電極性
能を低下させる。これらを防止するには、前記三次元電
極の極性を反転させて析出したカルシウムの水酸化物等
を被処理水の水素イオン濃度が高い陽極面上で再溶解さ
せて電極表面から除去し、これにより陰極の目詰まりに
よる被処理水の流通阻害等を生じさせることなく、前記
被処理水の電気化学的処理を行うことができ、特に殺菌
を目的とする通電を停止することなく電極表面からカル
シウムやマグネシウムの水酸化物、酸化物あるいは炭酸
塩を除去することが可能であるため非常に有効である。
前記電解槽内を隔膜で区画して陽極室と陰極室を形成し
ても、隔膜を使用せずにそのまま通電を行うこともでき
るが、隔膜を使用せずかつ電極の極間距離あるいは誘電
体と電極、又は誘電体相互の間隔を狭くする場合には短
絡防止のため電気絶縁性のスペーサとして例えば有機高
分子材料で作製した網状スペーサ等を両極間あるいは前
記誘電体間等に挿入することができる。又隔膜を使用す
る場合には流通する被処理水の移動を妨害しないように
多孔質例えばその開口率が10%以上95%以下好ましくは
20%以上80%以下の隔膜を使用することが望ましく、該
隔膜は少なくとも前記被処理水が透過できる程度の孔径
の微細孔を有していなければならない。
The electrolytic cell of the present invention can also remove calcium ions and magnesium ions which may be contained in the water to be treated. When water to be treated containing calcium ions and magnesium ions is supplied to the electrolytic cell,
Calcium or magnesium hydroxide or the like is deposited on the three-dimensional electrode, especially on the three-dimensional cathode, and is removed from the cathode by a peeling operation or the like to remove calcium ions in the water to be treated. On the contrary, if the electrochemical treatment is continued without removing the hydroxide or the like deposited on the cathode, the cathode is clogged, which impedes the flow of the water to be treated and deteriorates the electrode performance. In order to prevent these, the polarity of the three-dimensional electrode is reversed and the precipitated calcium hydroxide or the like is redissolved on the anode surface having a high hydrogen ion concentration of the water to be treated and removed from the electrode surface. Without causing flow inhibition of the water to be treated due to clogging of the cathode, it is possible to perform the electrochemical treatment of the water to be treated, calcium from the electrode surface without stopping the energization especially for the purpose of sterilization It is very effective because it can remove hydroxides, oxides or carbonates of magnesium and magnesium.
Even if the inside of the electrolytic cell is partitioned by a diaphragm to form an anode chamber and a cathode chamber, it is possible to carry on electricity as it is without using the diaphragm, but without using the diaphragm and the distance between electrodes or the dielectric. When the space between the electrode and the electrode or the dielectric is narrowed, an electrically insulating spacer such as a mesh spacer made of an organic polymer material may be inserted between the electrodes or between the dielectrics to prevent a short circuit. it can. When a diaphragm is used, it is preferably porous such that its opening ratio is 10% or more and 95% or less so as not to interfere with the movement of the water to be treated flowing through it.
It is desirable to use a diaphragm of 20% or more and 80% or less, and the diaphragm must have fine pores having a pore size at least permeable to the water to be treated.

【0013】又電極電位は陽極電位を+1.2 V(vs.SHE)
より卑で+0.2 V(vs.SHE)より貴である値とし、陰極電
位を−1.0 V(vs.SHE)より貴である値とすることが望ま
しい。この電位範囲では両極における通常の電解反応に
より生ずる酸素ガス及び水素ガスの発生が殆ど認められ
ず、前記微生物の滅菌に寄与することのない発生ガスに
配慮することなく、更にそれら発生ガスによる処理液と
の酸化還元反応により処理液成分が変化することなく、
又電解電力を被処理水滅菌以外の無駄でかつ殺菌処理を
阻害する電解ガス発生に使用することなく、前記被処理
水の滅菌処理を行うことができる。なお、本発明に使用
する電解槽では漏洩電流が電解槽から被処理水を通して
他の部材に流れ込み、好ましくない電気化学反応を誘起
したり、部材壁面を電気化学的に腐食させ壁面構成材料
を溶出させることがあるため、電解槽内の陽陰極が相対
しない電極背面部及び/又は前記電解槽の出入口配管内
に、前記被処理水より導電性が高くかつ電解反応を生じ
させることのできる部材をその一端を接地可能なように
設置して前記漏洩電流を遮断することができる。
The electrode potential is the anode potential +1.2 V (vs.SHE)
It is desirable that the value be more base and more noble than +0.2 V (vs.SHE) and that the cathode potential be noble than -1.0 V (vs.SHE). In this potential range, almost no generation of oxygen gas and hydrogen gas generated by the usual electrolytic reaction in both electrodes was observed, and the treated liquid by the generated gas was not considered without considering the generated gas that does not contribute to the sterilization of the microorganism. The components of the treatment liquid do not change due to the redox reaction with
Further, the sterilization treatment of the water to be treated can be performed without using the electrolysis electric power to generate electrolytic gas which is a waste except the sterilization of the treatment water and inhibits the sterilization treatment. In the electrolytic cell used in the present invention, a leakage current flows from the electrolytic cell through the water to be treated into other members to induce an undesired electrochemical reaction or the member wall surface is electrochemically corroded to elute the wall surface constituent material. Therefore, a member having higher conductivity than the water to be treated and capable of causing an electrolytic reaction is provided in the back surface of the electrode where the positive and negative electrodes in the electrolytic cell do not face each other and / or in the inlet / outlet pipe of the electrolytic cell. The leak current can be cut off by installing one end thereof so that it can be grounded.

【0014】次に添付図面に基づいて本発明に使用でき
る電解槽及び該電解槽を使用する本発明に係わる電気化
学的処理装置の好ましい例を説明するが、本発明はこれ
らに限定されるものではない。図1は、本発明の電気化
学的処理装置の電解槽として使用可能な複極型固定床式
電解槽の一例を示す概略縦断面図である。上下にフラン
ジ1を有する円筒形の電解槽本体2の内部上端近傍及び
下端近傍にはそれぞれメッシュ状の給電用陽極3と給電
用陰極4が設けられている。電解槽本体2は、長期間の
使用又は再度の使用にも耐え得る電気絶縁材料で形成す
ることが好ましく、特に合成樹脂であるポリエピクロル
ヒドリン、ポリビニルメタクリレート、ポリエチレン、
ポリプロピレン、ポリ塩化ビニル、ポリ塩化エチレン、
フェノール−ホルムアルデヒド樹脂等が好ましく使用で
きる。正の直流電圧を与える前記給電用陽極3は、例え
ば炭素系材料(例えば活性炭、炭、コークス、石炭
等)、グラファイト材 (例えば炭素繊維、カーボンク
ロス、グラファイト等)、炭素複合材(例えば炭素に金
属を粉状で混ぜ焼結したもの等)、活性炭素繊維不織布
(例えばKE−1000フェルト、東洋紡株式会社)、又は
これに白金、白金、パラジウムやニッケルを担持させた
材料、更に寸法安定性電極 (白金族酸化物被覆チタン
材) 、白金被覆チタン材、ニッケル材、ステンレス材、
鉄材等から形成される。又給電用陽極3に対向し負の直
流電圧を与える給電用陰極4は、例えば白金、ステンレ
ス、チタン、ニッケル、ハステロイ、グラファイト、炭
素材、軟鋼あるいは白金族金属をコーティングした金属
材料等から形成されている。
Next, preferred examples of the electrolytic cell which can be used in the present invention and the electrochemical treatment apparatus according to the present invention which uses the electrolytic cell will be described with reference to the accompanying drawings, but the present invention is not limited thereto. is not. FIG. 1 is a schematic vertical cross-sectional view showing an example of a bipolar electrode fixed bed type electrolytic cell that can be used as an electrolytic cell of the electrochemical treatment apparatus of the present invention. A mesh-shaped power feeding anode 3 and power feeding cathode 4 are provided in the vicinity of the upper end and the lower end of the inside of a cylindrical electrolytic cell body 2 having a flange 1 at the top and bottom, respectively. The electrolytic cell body 2 is preferably formed of an electrically insulating material that can withstand long-term use or re-use, and in particular, synthetic resin polyepichlorohydrin, polyvinyl methacrylate, polyethylene,
Polypropylene, polyvinyl chloride, polyethylene chloride,
Phenol-formaldehyde resin and the like can be preferably used. The power supply anode 3 that gives a positive DC voltage is, for example, a carbon-based material (for example, activated carbon, charcoal, coke, coal, etc.), a graphite material (for example, carbon fiber, carbon cloth, graphite, etc.), a carbon composite material (for example, for carbon). Metal powder mixed and sintered), activated carbon fiber non-woven fabric (for example, KE-1000 felt, Toyobo Co., Ltd.), or a material in which platinum, platinum, palladium or nickel is supported, and a dimensionally stable electrode. (Platinum group oxide coated titanium material), platinum coated titanium material, nickel material, stainless steel material,
It is made of iron or the like. The power-supplying cathode 4, which faces the power-supplying anode 3 and applies a negative DC voltage, is formed of, for example, platinum, stainless steel, titanium, nickel, hastelloy, graphite, carbon material, mild steel or a metal material coated with a platinum group metal. ing.

【0015】前記両給電用電極3、4間には複数個の、
図示の例では3個の固定床5つまり三次元電極が積層さ
れ、かつ該固定床5間及び該固定床5と前記両給電用電
極3、4間に4枚のドーナツ状の隔膜あるいはスペーサ
ー6が挟持されている。各固定床5の前記給電用陰極4
に向かう面にはフェライト被覆層7が被覆され、該固定
床5は電解槽本体2の内壁に密着し固定床5の内部を通
過せず、固定床5と電解槽本体2の側壁との間を流れる
被処理水等の漏洩流がなるべく少なくなるように配置さ
れている。隔膜を使用する場合には該隔膜として織布、
素焼板、粒子焼結ブラスチック、多孔板、イオン交換膜
等が用いられ、スペーサーとして電気絶縁性材料で製作
された織布、多孔板、網、棒状材等が使用される。この
ような構成から成る電解槽2に被処理水を図1に矢印で
示すように下方から供給しながら通電を行うと、前記各
固定床5が図示の如く下面が正に上面が負に分極して固
定床5内及び固定床5間に電位が生じ、該電解槽内を流
通する被処理水はこの電位により正又は負に分極された
固定床5に接触して該被処理水の改質処理が行われる。
この電気化学的処理により酸素ガスが発生する場合でも
フェライト被覆層7の酸素過電圧が固定床5である炭素
質系材料の酸素過電圧より低いため、酸素ガスがフェラ
イト被覆層7からほぼ選択的に起こって酸素ガスによる
前記固定床5の溶出が最小限に抑制され、該固定床5を
交換することなくつまり煩雑な操作である電解槽の分解
及び組み立てを行うことなく長期間に亘って被処理水の
処理や電解液の電解を行うことが可能になる。
A plurality of electrodes are provided between the power feeding electrodes 3 and 4.
In the illustrated example, three fixed beds 5, that is, three-dimensional electrodes are laminated, and four doughnut-shaped diaphragms or spacers 6 are provided between the fixed beds 5 and between the fixed bed 5 and the power feeding electrodes 3 and 4. Are pinched. The feeding cathode 4 of each fixed bed 5
The surface facing toward is covered with a ferrite coating layer 7, the fixed bed 5 is in close contact with the inner wall of the electrolytic cell body 2 and does not pass through the inside of the fixed bed 5, and between the fixed bed 5 and the side wall of the electrolytic cell body 2. It is arranged so that the leakage flow of the water to be treated and the like flowing through it is reduced as much as possible. When using a diaphragm, a woven fabric as the diaphragm,
A bisque plate, a particle-sintered plastic, a perforated plate, an ion exchange membrane, etc. are used, and a woven fabric, a perforated plate, a net, a rod-shaped member made of an electrically insulating material is used as a spacer. When the water to be treated is supplied to the electrolytic cell 2 having such a structure from below as shown by the arrow in FIG. 1, the fixed bed 5 is polarized so that the lower surface is positive and the upper surface is negative as shown. As a result, an electric potential is generated in the fixed bed 5 and between the fixed beds 5, and the water to be treated flowing in the electrolytic cell comes into contact with the fixed bed 5 which is polarized positively or negatively by the electric potential to modify the water to be treated. Quality processing is performed.
Even when oxygen gas is generated by this electrochemical treatment, the oxygen overvoltage of the ferrite coating layer 7 is lower than the oxygen overvoltage of the carbonaceous material of the fixed bed 5, so that the oxygen gas is generated almost selectively from the ferrite coating layer 7. Elution of the fixed bed 5 due to oxygen gas is suppressed to a minimum, and the treated water can be treated for a long time without replacing the fixed bed 5, that is, without disassembling and assembling the electrolytic cell, which is a complicated operation. And the electrolysis of the electrolytic solution can be performed.

【0016】図2は、図1の電解槽(フェライト被覆層
は省略)を被処理水の貯槽に設置した状態を示す概略縦
断面図であり、図1と同一部材には同一符号を付して説
明を省略する。上面が開口可能な箱型の貯槽8には被処
理水9が収容され、該貯槽8の底面には4個の支持杆10
が立設されている。該支持杆10の上端には前記電解槽本
体2の下部フランジ1が載置され該電解槽本体2を貯槽
8内に保持している。該貯槽8の上面開口部には、先端
が前記支持杆10の近傍に達する被処理水供給管11と基端
が前記被処理水9に接触する被処理水取出管12を有する
蓋体13が嵌合され、未処理の被処理水を前記被処理水供
給管11を通して前記貯槽8に供給し、電解槽本体2で電
気化学的に処理され清浄化された被処理水を被処理水取
出管12から取り出して所定用途、例えば熱交換器の冷却
用水として供給するようにしている。この電気化学的処
理装置では電解槽本体と貯槽間に循環ラインがないた
め、装置全体を小型化して設置面積を小さくできるとと
ともに、貯槽内の被処理水が電解槽と直接又は間接に常
に接触しているため、清浄化された被処理水が貯槽内で
微生物の繁殖等により汚染されることがなく、被処理水
取出管からは常に清浄な被処理水が取り出される。
FIG. 2 is a schematic vertical sectional view showing a state in which the electrolytic cell of FIG. 1 (the ferrite coating layer is omitted) is installed in the storage tank of the water to be treated. The same members as those in FIG. 1 are designated by the same reference numerals. And the description is omitted. Water to be treated 9 is contained in a box-shaped storage tank 8 whose top surface can be opened, and four support rods 10 are provided on the bottom surface of the storage tank 8.
Is erected. The lower flange 1 of the electrolytic cell body 2 is placed on the upper end of the supporting rod 10 to hold the electrolytic cell body 2 in the storage tank 8. A lid 13 having a treated water supply pipe 11 whose tip reaches the vicinity of the support rod 10 and a treated water take-out pipe 12 whose base end contacts the treated water 9 is provided at the upper opening of the storage tank 8. The untreated untreated water that has been fitted is supplied to the storage tank 8 through the untreated water supply pipe 11, and the untreated water that has been electrochemically treated and purified in the electrolytic cell body 2 is the untreated water take-out pipe. It is taken out from 12 and supplied for a predetermined purpose, for example, as cooling water for a heat exchanger. In this electrochemical treatment device, since there is no circulation line between the electrolytic cell body and the storage tank, the entire equipment can be downsized and the installation area can be reduced, and the water to be treated in the storage tank is always in direct or indirect contact with the electrolytic cell. Therefore, the purified water to be treated is not contaminated by the propagation of microorganisms in the storage tank, and clean water to be treated is always taken out from the treated water extraction pipe.

【0017】図3は、図1の電解槽(フェライト被覆層
は省略)を飲料水用ポット内に設置した状態を示す概略
縦断面図であり、図1と同一部材には同一符号を付して
説明を省略する。合成樹脂等から成る円筒状ポット本体
14左壁面には上下1対のL字状の連結部材15が固定さ
れ、該連結部材15の水平部はボルト16により前記電解槽
本体2の上下のフランジ1に締着され、電解槽本体2が
ポット本体14の左壁面近傍に保持されている。ポット本
体14の右側壁面上端にはヒンジ17を介してカバー18が連
結され、該カバー18の他端はポット本体14の左側壁面上
端に形成された嘴状注出口19に近接している。該ポット
本体14の左側壁面の外側には補助壁面20が設置され、該
左側壁面と補助壁面20に形成された空間に電解槽本体2
駆動用電源21が収容され、該電源21は前記給電用陽極3
及び給電用陰極4に接続されている。22は底板のやや上
方に設置された攪拌翼である。このポット本体14に水道
水を入れ、電源21により前記固定床5を分極させかつ攪
拌翼22を回転させておくとポット本体14内の水道水が常
に直接又は間接に帯電して固定床5に接触し電気化学的
に処理されるため、ポット本体14内に水道水を長期間保
存しても該水道水の汚染が殆ど生ずることがなく、前記
注出口19から常に清浄な飲料水を供給することができ
る。
FIG. 3 is a schematic vertical sectional view showing a state in which the electrolytic cell of FIG. 1 (the ferrite coating layer is omitted) is installed in a pot for drinking water. The same members as those in FIG. 1 are designated by the same reference numerals. And the description is omitted. Cylindrical pot body made of synthetic resin
14 A pair of upper and lower L-shaped connecting members 15 are fixed to the left wall surface, and the horizontal portions of the connecting members 15 are fastened to the upper and lower flanges 1 of the electrolytic cell body 2 by bolts 16, so that the electrolytic cell body 2 Are held near the left wall surface of the pot body 14. A cover 18 is connected to the upper end of the right wall surface of the pot body 14 via a hinge 17, and the other end of the cover 18 is close to a beak-shaped spout 19 formed on the upper end of the left wall surface of the pot body 14. An auxiliary wall surface 20 is installed outside the left wall surface of the pot body 14, and the electrolytic cell body 2 is placed in the space formed between the left wall surface and the auxiliary wall surface 20.
A driving power source 21 is housed, and the power source 21 is the power feeding anode 3
And the power supply cathode 4. 22 is a stirring blade installed a little above the bottom plate. When tap water is put in the pot body 14, the fixed bed 5 is polarized by the power source 21 and the stirring blades 22 are rotated, the tap water in the pot body 14 is always charged directly or indirectly to the fixed bed 5. Since they come into contact and are electrochemically treated, even if tap water is stored in the pot body 14 for a long period of time, the tap water is hardly contaminated, and clean drinking water is always supplied from the spout 19. be able to.

【0018】[0018]

【実施例】次に本発明の電気化学的処理装置による被処
理水処理の実施例を記載するが、本発明はこれらの実施
例に限定されるものではない。
EXAMPLES Next, examples of treatment of water to be treated by the electrochemical treatment apparatus of the present invention will be described, but the present invention is not limited to these examples.

【実施例1】透明な硬質ポリ塩化ビニル樹脂製の高さ 1
00mm、内径50mmのフランジ付円筒形である図1に示
した電解槽を、微生物を3200個/ミリリットル含有する
熱交換器用冷却水を3.5 トン収容した縦80cm、横60c
m、深さ100 cmの箱型の熱交換器用冷却水の貯槽内に
設置した。該電解槽内には、給電用陰極側に厚さ1.0m
mの寸法安定性電極を接触状態で設置したポーラスカー
ボンから成る直径200mm、厚さ10mmの固定床5個
を、外径200 mm、内径180 mm及び厚さ1mmのポリ
エチレン樹脂製のドーナツ状スペーサー6枚で挟み込
み、上下両端の隔膜にそれぞれ白金をその表面にメッキ
したチタン製である直径195 mm厚さ 1.0mmのメッシ
ュ状給電用陽極及び給電用陰極を接触させて設置した。
前記貯槽内の冷却水を攪拌翼で上方向に液流が生ずるよ
うに攪拌し、該冷却水が電解槽本体内を流通するように
した。この状態で貯槽内の冷却水中の微生物数の経時変
化を測定したところ表1に示す通りであった。又電力消
費量を表1に示した。表1から微生物数は24時間経過時
には零になり、以後殆ど零のまま維持されることが判
る。
Example 1 Height made of transparent hard polyvinyl chloride resin 1
The cylindrical electrolytic cell shown in Fig. 1 with a diameter of 00 mm and an inner diameter of 50 mm and having a capacity of 3 tons of cooling water for a heat exchanger containing 3200 microorganisms / ml was placed in a column of 80 cm in length and 60 c in width.
It was installed in a box-shaped cooling water storage tank for heat exchanger having a depth of 100 m and a depth of 100 cm. Inside the electrolytic cell, the thickness of the power supply cathode side is 1.0 m.
Dimensionally stable electrodes of 5 m, made of porous carbon and having a fixed diameter of 200 mm and a thickness of 10 mm, were fixed to five, and a doughnut-shaped spacer 6 made of polyethylene resin with an outer diameter of 200 mm, an inner diameter of 180 mm and a thickness of 1 mm was used. It was sandwiched between sheets, and a mesh-shaped power feeding anode and a power feeding cathode each having a diameter of 195 mm and a thickness of 1.0 mm, which were made of titanium and whose surfaces were plated with platinum, were placed in contact with each other.
The cooling water in the storage tank was stirred by a stirring blade so that a liquid flow was generated in the upward direction, and the cooling water was allowed to flow in the electrolytic cell body. In this state, the time-dependent change in the number of microorganisms in the cooling water in the storage tank was measured. The power consumption is shown in Table 1. It can be seen from Table 1 that the number of microorganisms becomes zero after 24 hours, and thereafter remains almost zero.

【0019】[0019]

【比較例1】実施例1の電解槽本体を実施例1の貯槽か
ら外部に取り出し、該電解槽本体及び貯槽を循環ライン
を通して接続し、貯槽内の冷却水を電解槽本体に供給し
て電気化学的に処理し、かつ貯槽に循環し、これを繰り
返した。貯槽内の冷却水中の微生物数の経時変化を測定
したところ表1に示す通りであった。又本比較例の電気
化学的処理及び循環の電力消費の全量を表1に示した。
表1から実施例1及び比較例1の両者では貯槽内の冷却
水中の微生物の経時変化には殆ど差異がないのに対し、
電力消費量は冷却水の循環用の分だけ比較例1の方が大
きく、経済的でないことが判る。
Comparative Example 1 The electrolytic cell body of Example 1 was taken out of the storage tank of Example 1, the electrolytic cell body and the storage tank were connected through a circulation line, and the cooling water in the storage tank was supplied to the electrolytic cell body to generate electricity. It was treated chemically and circulated to a reservoir, which was repeated. The change in the number of microorganisms in the cooling water in the storage tank with time was measured, and the results are shown in Table 1. In addition, Table 1 shows the total amount of electric power consumption in the electrochemical treatment and circulation of this comparative example.
From Table 1, both Example 1 and Comparative Example 1 show almost no difference in the change with time of microorganisms in the cooling water in the storage tank.
It can be seen that the power consumption is larger in Comparative Example 1 as much as the cooling water is circulated, which is not economical.

【0020】[0020]

【表1】 [Table 1]

【0021】[0021]

【実施例2】透明な硬質ポリ塩化ビニル樹脂製の高さ60
mm、内径40mmのフランジ付円筒形である図1に示し
た電解槽を内径100 mm、深さ150 mmのポット内に図
3に示すように設置した。、微生物を1600個/ミリリッ
トル含有する模擬水0.95リットルを前記ポット内に収容
した。前記電解槽内には、給電用陰極側に厚さ1.0 mm
の寸法安定性電極を接触状態で設置したポーラスカーボ
ンから成る直径39mm、厚さ10mmの固定床5個を、外
径40mm、内径35mm及び厚さ1.0 mmのポリエチレン
樹脂製のドーナツ状スペーサー6枚で挟み込み、上下両
端の隔膜にそれぞれ白金をその表面にメッキしたチタン
製である直径38mm厚さ1.0 mmのメッシュ状給電用陽
極及び給電用陰極を接触させて設置した。このポット内
の両給電用電極間に30Vの電圧を印可し、この状態でポ
ット本体内の被処理水中の微生物数の経時変化を測定し
たところ表2に示す通りであった。
[Example 2] Height 60 made of transparent hard polyvinyl chloride resin
The cylindrical electrolytic cell shown in FIG. 1 having a diameter of 40 mm and an inner diameter of 40 mm was set in a pot having an inner diameter of 100 mm and a depth of 150 mm as shown in FIG. 0.95 liters of simulated water containing 1600 microorganisms / ml was stored in the pot. Inside the electrolytic cell, the thickness of the cathode for feeding is 1.0 mm.
Dimensional stability 5 fixed beds of 39 mm diameter and 10 mm thickness made of porous carbon with electrodes placed in contact with 6 donut spacers made of polyethylene resin with an outer diameter of 40 mm, an inner diameter of 35 mm and a thickness of 1.0 mm. A mesh-shaped power feeding anode and a power feeding cathode each having a diameter of 38 mm and a thickness of 1.0 mm, which were made of titanium and whose surfaces were plated with platinum, were placed in contact with each other. A voltage of 30 V was applied between both power supply electrodes in the pot, and the time-dependent change in the number of microorganisms in the water to be treated in the pot body was measured in this state.

【0022】[0022]

【比較例2】実施例2と同一の電解槽をポット本体とは
別に設置し、実施例2と同一の微生物数の被処理水を電
気化学的に処理したところ、5時間経過後に微生物数が
零になったので、該被処理水を電解槽本体を設置してい
ない実施例2のポット本体内に注入し、そのまま放置し
て該被処理水中の微生物数の経時変化(電気化学的処理
の開始時を零とした)を測定したところ表2に示す通り
であった。表2から電気化学的処理により微生物数を零
とした被処理水もそのままポットに入れておくと微生物
が混入して汚染するのに対し、電解槽を収容したポット
に被処理水を入れておくと常に微生物の存在しない被処
理水が供給できることが判る。
[Comparative Example 2] The same electrolytic cell as in Example 2 was installed separately from the pot body, and the treated water having the same number of microorganisms as in Example 2 was electrochemically treated. Since it became zero, the water to be treated was poured into the pot body of Example 2 in which the electrolytic cell body was not installed, and was left as it was to change the number of microorganisms in the water to be treated with time (electrochemical treatment). It was as shown in Table 2 when the starting time was set to zero). From Table 2, it is contaminated by microorganisms if the water to be treated with the number of microorganisms made to be zero by electrochemical treatment is also put in the pot as it is, whereas the water to be treated is put in the pot containing the electrolytic cell. It can be seen that it is possible to always supply water to be treated that is free of microorganisms.

【0023】[0023]

【表2】 [Table 2]

【0024】[0024]

【発明の効果】本発明は、貯槽内に貯留した被処理水を
固定床型電解槽に供給し該被処理水を電気化学的に処理
する装置において、前記電解槽を前記貯槽内に設置した
ことを特徴とする電気化学的処理装置(請求項1)であ
る。本発明は熱交換器用貯槽、製紙洗浄水貯槽、プール
及び浴場等(請求項2)の比較的大量に必要とする被処
理水の製造に好ましく使用することができる。熱交換器
用冷却水の貯槽を電解槽本体と連結し、前記冷却水電解
槽本体に循環する従来の装置と比較して本発明の電気化
学的処理装置では、循環ラインを不要としているため設
置面積が小さくなりかつ循環ラインの設備費が節減でき
るため、大幅なコストダウンを達成することができる。
更に本発明装置では循環ポンプの電力量も節減でき、少
量の電力量で従来以上の処理効果を達成することができ
る。又本発明装置を飲料水のポットに適用すると(請求
項3)、ポット本体内の飲料水が常に直接又は間接に電
解槽の電極に接触するため、微生物等が混入しても確実
に滅菌し、ポットのサイズを大きくすることなく常に清
浄な飲料水を提供することができる。
According to the present invention, in the apparatus for supplying the water to be treated stored in the storage tank to the fixed bed type electrolysis tank to electrochemically treat the water to be treated, the electrolysis tank is installed in the storage tank. An electrochemical treatment apparatus (claim 1) characterized by the above. INDUSTRIAL APPLICABILITY The present invention can be preferably used for producing a relatively large amount of water to be treated such as a heat exchanger storage tank, a papermaking cleaning water storage tank, a pool and a bathhouse (Claim 2). In the electrochemical treatment apparatus of the present invention, a circulation line is not required in comparison with a conventional apparatus in which a storage tank for heat exchanger cooling water is connected to an electrolytic cell body and circulates in the cooling water electrolysis cell body, so that the installation area is small. Since it is smaller and the facility cost of the circulation line can be reduced, a significant cost reduction can be achieved.
Further, in the device of the present invention, the amount of electric power of the circulation pump can be saved, and a processing effect higher than conventional can be achieved with a small amount of electric power. When the device of the present invention is applied to a pot of drinking water (Claim 3), the drinking water in the pot body always comes into direct or indirect contact with the electrode of the electrolytic cell, so that sterilization is assured even if microorganisms or the like are mixed. Therefore, it is possible to always provide clean drinking water without increasing the size of the pot.

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

【図1】本発明の電気化学的処理装置に使用する複極式
固定床型電解槽の一例を示す概略縦断面図。
FIG. 1 is a schematic vertical sectional view showing an example of a bipolar electrode fixed bed type electrolytic cell used in an electrochemical treatment apparatus of the present invention.

【図2】図1の電解槽を被処理水貯留槽内に設置した本
発明に係わる電気化学的処理装置の一例を示す概略縦断
面図。
FIG. 2 is a schematic vertical cross-sectional view showing an example of the electrochemical treatment apparatus according to the present invention in which the electrolytic cell of FIG. 1 is installed in a treated water storage tank.

【図3】図1の電解槽を給水ポット内に設置した本発明
に係わる電気化学的処理装置の一例を示す概略縦断面
図。
FIG. 3 is a schematic vertical sectional view showing an example of the electrochemical treatment apparatus according to the present invention in which the electrolytic cell of FIG. 1 is installed in a water supply pot.

【符号の説明】 1・・・フランジ 2・・・電解槽本体 3・・・給電
用陽極 4・・・給電用陰極 5・・・固定床 6・・・スペーサー 7・・・フェライト被覆層 8・
・・貯槽 9・・・被処理水 10・・・支持杆 11・・
・被処理水供給管 12・・・被処理水取出管 13・・・
蓋体 14・・・ポット本体 15・・・連結部材 16・・・ボルト 17・・・ヒンジ 18・・・カバー 19
・・・嘴状注出口 20・・・補助壁面 21・・・電源
[Explanation of Codes] 1 ... Flange 2 ... Electrolyzer main body 3 ... Power feeding anode 4 ... Power feeding cathode 5 ... Fixed bed 6 ... Spacer 7 ... Ferrite coating layer 8・
..Reservoir 9 ... Water to be treated 10 ... Support rod 11 ...
・ Treatment water supply pipe 12 ・ ・ ・ Treatment water extraction pipe 13 ・ ・ ・
Lid 14 ... Pot body 15 ... Connecting member 16 ... Bolt 17 ... Hinge 18 ... Cover 19
... Beck spout 20 ... Auxiliary wall 21 ... Power supply

─────────────────────────────────────────────────────
─────────────────────────────────────────────────── ───

【手続補正書】[Procedure amendment]

【提出日】平成5年8月19日[Submission date] August 19, 1993

【手続補正1】[Procedure Amendment 1]

【補正対象書類名】図面[Document name to be corrected] Drawing

【補正対象項目名】全図[Correction target item name] All drawings

【補正方法】変更[Correction method] Change

【補正内容】[Correction content]

【図1】 [Figure 1]

【図2】 [Fig. 2]

【図3】 [Figure 3]

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 貯槽内に貯留した被処理水を固定床型電
解槽に供給し該被処理水を電気化学的に処理する装置に
おいて、前記電解槽を前記貯槽内に設置したことを特徴
とする電気化学的処理装置。
1. An apparatus for supplying water to be treated stored in a storage tank to a fixed bed type electrolytic cell to electrochemically treat the water to be treated, wherein the electrolytic cell is installed in the storage tank. Electrochemical processing equipment.
【請求項2】 貯槽が熱交換器用貯槽、製紙洗浄水貯
槽、プール及び浴場の少なくとも1種である請求項1に
記載の電気化学的処理装置。
2. The electrochemical treatment apparatus according to claim 1, wherein the storage tank is at least one of a heat exchanger storage tank, a papermaking wash water storage tank, a pool, and a bathhouse.
【請求項3】 貯槽が飲料水用ポットである請求項1に
記載の電気化学的処理装置。
3. The electrochemical treatment device according to claim 1, wherein the storage tank is a pot for drinking water.
JP20871291A 1991-07-26 1991-07-26 Electrochemical treatment apparatus Pending JPH0655177A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP20871291A JPH0655177A (en) 1991-07-26 1991-07-26 Electrochemical treatment apparatus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP20871291A JPH0655177A (en) 1991-07-26 1991-07-26 Electrochemical treatment apparatus

Publications (1)

Publication Number Publication Date
JPH0655177A true JPH0655177A (en) 1994-03-01

Family

ID=16560837

Family Applications (1)

Application Number Title Priority Date Filing Date
JP20871291A Pending JPH0655177A (en) 1991-07-26 1991-07-26 Electrochemical treatment apparatus

Country Status (1)

Country Link
JP (1) JPH0655177A (en)

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