JPH10180256A - Electrolytic strongly acidic water, its production and endotoxin inactivator consisting of the strongly acidic water - Google Patents

Electrolytic strongly acidic water, its production and endotoxin inactivator consisting of the strongly acidic water

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Publication number
JPH10180256A
JPH10180256A JP34864996A JP34864996A JPH10180256A JP H10180256 A JPH10180256 A JP H10180256A JP 34864996 A JP34864996 A JP 34864996A JP 34864996 A JP34864996 A JP 34864996A JP H10180256 A JPH10180256 A JP H10180256A
Authority
JP
Japan
Prior art keywords
water
strongly acidic
endotoxin
electrolytic
acidic 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
JP34864996A
Other languages
Japanese (ja)
Inventor
Noriaki Tanaka
紀陽 田仲
Koichi Fujiwara
功一 藤原
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP34864996A priority Critical patent/JPH10180256A/en
Priority to PCT/JP1997/002462 priority patent/WO1998029347A1/en
Priority to AU34611/97A priority patent/AU3461197A/en
Publication of JPH10180256A publication Critical patent/JPH10180256A/en
Pending legal-status Critical Current

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Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104Devices therefor; Their operating or servicing
    • C02F1/4618Devices therefor; Their operating or servicing for producing "ionised" acidic or basic water
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/441Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by reverse osmosis
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/4602Treatment of water, waste water, or sewage by electrochemical methods for prevention or elimination of deposits
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104Devices therefor; Their operating or servicing
    • C02F1/4618Devices therefor; Their operating or servicing for producing "ionised" acidic or basic water
    • C02F2001/46185Devices therefor; Their operating or servicing for producing "ionised" acidic or basic water only anodic or acidic water, e.g. for oxidizing or sterilizing
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/04Disinfection

Landscapes

  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Electrochemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)
  • Apparatus For Disinfection Or Sterilisation (AREA)

Abstract

PROBLEM TO BE SOLVED: To eliminate scaling in an electrolytic water generator and to provide an electrolytic strongly acidic water with the endotoxin content decreased to a low concn. at which the water can be used in the medical field a short time after the production. SOLUTION: An electrolytic strongly acidic water contg. 15EU/l endotoxin one hour after the production is produced by electrolyzing a reverse-osmosis water. Concretely, the city water as raw material is introduced into an activated-carbon filter 1. The iron rust, etc., in the city water are removed by the filter 1, and further free chlorine and chloramine are adsorbed and removed. The water passed through the filter 1 is then introduced into a water softener 2, subjected ion exchange therein and softened. The softened water is introduced into a reverse-osmosis device 3 and refined, and the refined water is introduced into an electrolytic water generator 4 and electrolyzed.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、電解強酸性水及び
その製法、特に、製造直後から1時間経過後のエンドト
キシン濃度が15EU/リットル以下となる性質を有す
る電解強酸性水及びその製法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an electrolytic strongly acidic water and a method for producing the same, and more particularly to an electrolytic strongly acidic water having a property that an endotoxin concentration after one hour from immediately after production is 15 EU / liter or less, and a method for producing the same.

【0002】本発明は、更に、このような電解強酸性水
を含有するエンドトキシン不活化剤にも関する。
[0002] The present invention further relates to an endotoxin inactivating agent containing such strongly acidic electrolytic water.

【0003】[0003]

【従来の技術】従来から、一般の水道水を少量の塩化ナ
トリウムと共に電解水生成装置に供給して、電解強アル
カリ水とともに、電解強酸性水を生成することが行われ
ている。
2. Description of the Related Art Conventionally, general tap water has been supplied to an electrolyzed water generator together with a small amount of sodium chloride to generate electrolyzed strongly acidic water together with electrolyzed strongly alkaline water.

【0004】この電解水生成装置は、隔膜を隔てて陽極
と陰極を備えた電極槽に、少量の水酸化ナトリウムを添
加した水を添加し、一定の電流、電圧を印加して電気分
解するものであり、陽極室からは電解強酸性水が、陰極
室からは電解強アルカリ水がそれぞれ生成される。
[0004] This electrolyzed water generating apparatus is configured to add a small amount of sodium hydroxide-added water to an electrode tank having an anode and a cathode across a diaphragm and apply a constant current and voltage to perform electrolysis. In the anode compartment, strongly acidic electrolytic water is produced, and in the cathode compartment, strongly alkaline aqueous solution is produced.

【0005】こうして生成された電解強酸性水は、一般
にpHが2.7〜2.4程度、酸化還元電位が1100
〜1150mV程度、有効塩素濃度が10〜40ppm
程度のものであり、殺菌作用やエンドトキシン除去作用
を有するので、医療器具の殺菌をはじめ、各種の殺菌用
途に使用されつつある。
[0005] The electrolytic strongly acidic water thus produced generally has a pH of about 2.7 to 2.4 and an oxidation-reduction potential of 1100.
~ 1150mV, effective chlorine concentration is 10 ~ 40ppm
Since it has a bactericidal action and an endotoxin removing action, it is being used for various sterilization applications including sterilization of medical instruments.

【0006】ところが、従来の電解強酸性水の製法には
下記のような問題点がある。即ち、従来の水道水を使用
する電解強酸性水の製造法によれば、電解水生成装置の
陰極側において、電極にスケール(ナトリウム、カリウ
ム、カルシウム、マグネシウム等を主成分とする)が析
出するため、電気分解を著しく阻害したり、得られる電
解強酸性水の性状が不安定になるという問題点がある。
[0006] However, the conventional method for producing strongly electrolytic acidic water has the following problems. That is, according to the conventional method for producing electrolytic strongly acidic water using tap water, scale (mainly containing sodium, potassium, calcium, magnesium, etc.) is deposited on the electrode on the cathode side of the electrolytic water generator. Therefore, there is a problem that the electrolysis is significantly inhibited and the properties of the obtained strongly acidic electrolytic water become unstable.

【0007】この問題点を解決すべく、電極に付着した
スケールを除去するために、電解水の一定量の生成毎に
逆洗(例えば、陽極室で生成した電解強酸性水で、陰極
室の電極を洗浄すること)を行ったり、印加電圧極性を
反転させることが提案されている。
[0007] In order to solve this problem, in order to remove the scale attached to the electrode, backwashing is performed every time a certain amount of electrolyzed water is generated. Cleaning the electrode) or reversing the polarity of the applied voltage.

【0008】しかしながら、このような方法では、繰り
返される逆洗や頻回の極性の反転により、電解水生成装
置の電極を劣化させることになる。
However, in such a method, the electrodes of the electrolyzed water generator are deteriorated due to repeated backwashing and frequent polarity reversal.

【0009】特に、いくつかの外国において、電解水生
成装置を用いて電解強酸性水を製造する場合、日本国内
における一般水道水に比し、水質の純度や硬度において
必ずしも満足しがたい点があり、特に陰極側電極にC
a、Mg等の析出が多量に発生すると考えられ、より一
層頻回の洗浄や印加電圧極性の反転を余儀なくされ、電
極の劣化が早期に起こり、電極の取り替えを頻繁に行な
うこととなる。
[0009] Particularly, in some foreign countries, when producing electrolytically acidic water using an electrolytic water generator, the purity and hardness of water quality are not always satisfactory as compared with general tap water in Japan. Yes, especially on the cathode side electrode
It is considered that a large amount of precipitation of a, Mg, etc. is generated, so that more frequent cleaning and reversal of the polarity of the applied voltage are inevitable, and the deterioration of the electrode occurs early and the electrode is frequently replaced.

【0010】更に、本発明者の研究によれば、一般の水
道水を原水として使用して電解強酸性水を製造する場
合、得られる電解強酸性水は、殺菌作用の点では充分で
あるが、製造直後の時点で、数千EU/リットルもの予
想外に高い濃度のエンドトキシンが検出され、電解強酸
性水がエンドトキシン不活化作用を有しているにも拘わ
らず、エンドトキシン濃度の低下が極めて緩慢で、製造
直後から長時間にわたって、比較的高いエンドトキシン
濃度が維持されることが見出された。(ここで、「E
U」とは、エンドトキシンユニットを指す。「透析液エ
ンドトキシンがよくわかる本」、竹沢真吾編集、株式会
社東京医学社、1995年7月1日発行、第29〜31
頁参照。) エンドトキシンは、健常人の血中には通常15EU/リ
ットル程度の低濃度で存在しているが、外部からエンド
トキシンが体内に入ると、ヒトに対して、急性的に悪
寒、発熱、低血圧等の反応を示し、慢性的にはエンドト
キシン抗体の産生、インターロイキン1βや腫瘍壊死因
子(TNF)等のサイトカインを誘導し、更に他の外毒
素や(1→3)−β−D−グルカン等の菌体成分との相
乗作用により動物に対する致死作用を増強することが報
告されている。
Further, according to the study of the present inventor, when electrolytic strong acid water is produced by using general tap water as raw water, the obtained electrolytic strong acid water is sufficient in terms of bactericidal action. Immediately after production, an unexpectedly high endotoxin concentration of several thousand EU / liter was detected, and the endotoxin concentration decreased extremely slowly despite the fact that the electrolytically acidic water had an endotoxin inactivating effect. It was found that a relatively high endotoxin concentration was maintained for a long time immediately after production. (Here, "E
"U" refers to endotoxin unit. "A Book to Understand Dialysis Fluid Endotoxin", edited by Shingo Takezawa, Tokyo Medical Co., Ltd., issued July 1, 1995, No. 29-31.
See page. Endotoxin is normally present in the blood of healthy individuals at a low concentration of about 15 EU / liter, but when endotoxin enters the body from the outside, it will acutely cause chills, fever, hypotension, etc. to humans. Chronically produce endotoxin antibodies, induce cytokines such as interleukin-1β and tumor necrosis factor (TNF), and further induce other exotoxins and (1 → 3) -β-D-glucan. It has been reported that a synergistic effect with bacterial cell components enhances the lethal effect on animals.

【0011】従って、上記のように数千EU/リットル
もの高濃度のエンドトキシンを含む電解強酸性水を、殺
菌等の目的で医療分野に使用することは、安全性の面か
ら重大な問題を惹起する可能性がある。
Therefore, the use of electrolytically acidic water containing endotoxin as high as several thousand EU / liter in the medical field for the purpose of sterilization or the like causes a serious problem from the viewpoint of safety. there's a possibility that.

【0012】[0012]

【発明が解決しようとする課題】本発明は、電解水生成
装置におけるスケール発生の問題を著しく抑制すること
を目的とするものである。
SUMMARY OF THE INVENTION An object of the present invention is to remarkably suppress the problem of scale generation in an electrolyzed water generating apparatus.

【0013】また、本発明は、製造から短時間内でエン
ドトキシン濃度が、医療分野で使用する場合にも問題の
ない程度の低濃度まで低下する電解強酸性水を提供する
ことを目的とするものでもある。
Another object of the present invention is to provide an electrolytic strongly acidic water in which the endotoxin concentration is reduced within a short time after production to a low concentration that does not cause any problem even when used in the medical field. But also.

【0014】[0014]

【課題を解決するための手段】本発明者は、上記目的を
達成すべく鋭意研究を重ねた結果、電解強酸性水を製造
する際に、その原料となる原水として、逆浸透水を使用
すると、スケールの発生が著しく抑制され、しかも、得
られる電解強酸性水が、極めて低濃度のエンドトキシン
を含むだけであって、製造直後から1時間程度経過すれ
ば、そのエンドトキシン濃度が、医療分野で臨床応用す
る場合に問題のない程度の低濃度、特に健常人の体内に
通常存在する15EU/リットル以下の低濃度にまで低
下することを見出した。本発明は、この新知見に基づき
完成されたものである。
Means for Solving the Problems As a result of intensive studies to achieve the above object, the present inventor has found that when producing electrolytically strongly acidic water, reverse osmosis water is used as raw water as a raw material thereof. In addition, the generation of scale is remarkably suppressed, and the obtained electrolytically acidic water contains only a very low concentration of endotoxin. It has been found that the concentration is reduced to such a low concentration that there is no problem when applied, particularly to a low concentration of 15 EU / liter or less which is normally present in the body of a healthy person. The present invention has been completed based on this new finding.

【0015】即ち、本発明は、逆浸透水を電解して得ら
れる電解強酸性水であって、該電解強酸性水の製造直後
から1時間経過した時点で、15EU/リットル以下の
エンドトキシン濃度を有していることを特徴とする電解
強酸性水を提供するものである。
That is, the present invention relates to an electrolytic strongly acidic water obtained by electrolyzing reverse osmosis water, wherein an endotoxin concentration of 15 EU / liter or less is obtained one hour after the production of the electrolytic strongly acidic water. The present invention provides electrolytic strongly acidic water characterized by having.

【0016】また、本発明は、逆浸透水を電解すること
を特徴とする上記電解強酸性水、即ち、該電解強酸性水
の製造直後から1時間経過した時点で、15EU/リッ
トル以下のエンドトキシン濃度を有している電解強酸性
水の製造法を提供するものでもある。
Further, the present invention is characterized in that reverse osmosis water is electrolyzed, that is, 1 hour after the production of the above electrolytic strongly acidic water, that is, 15 EU / liter or less of endotoxin. Another object of the present invention is to provide a method for producing electrolytically strongly acidic water having a concentration.

【0017】更に、こうして得られた電解強酸性水は、
そのエンドトキシン不活化作用が極めて優れていること
が見出された。従って、本発明は、逆浸透水を電解して
得られる電解強酸性水であって、該電解強酸性水の製造
直後から1時間経過した時点で、15EU/リットル以
下のエンドトキシン濃度を有している電解強酸性水を含
有することを特徴とするエンドトキシン不活化剤を提供
するものでもある。
Further, the thus obtained electrolytically acidic water is
The endotoxin inactivating effect was found to be extremely excellent. Therefore, the present invention provides an electrolytic strongly acidic water obtained by electrolyzing reverse osmosis water, which has an endotoxin concentration of 15 EU / liter or less at the time of one hour immediately after the production of the electrolytic strongly acidic water. Another object of the present invention is to provide an endotoxin inactivating agent characterized by containing an electrolytic strongly acidic water.

【0018】[0018]

【発明の実施の形態】本明細書において、エンドトキシ
ン濃度は、合成基質法(比色法)のカイネティック法
(「透析液エンドトキシンがよくわかる本」、竹沢真吾
編集、株式会社東京医学社、1995年7月1日発行、
第38〜39頁参照)により測定したものである。
BEST MODE FOR CARRYING OUT THE INVENTION In the present specification, the endotoxin concentration is determined by a kinetic method of a synthetic substrate method (colorimetric method) (“A book that understands endotoxin in dialysate”, edited by Shingo Takezawa, Tokyo Medical Co., Ltd., 1995). Issued on July 1,
38 to 39).

【0019】この方法は、エンドトキシンとライセート
中のC因子系反応によって最終的に活性化された凝固酵
素が、コアグロゲンをコアグリンに変換する際のコアグ
ロゲンの水解部位のアミノ酸配列と類似の配列を持つ合
成ペプチドに、発色基p−ニトロアニリン(pNA)を
結合させた発色合成基質を用い、凝固酵素のアミダーゼ
活性によって遊離するpNAの吸光度を測定する方法で
あって、カイネティック法である。該カイネティック法
は、pNAの遊離の吸光度変化率(mAbs/min)
が、エンドトキシン濃度に比例すること(比色反応速度
法、rate assay)、又は反応液の吸光度変化が予め設定
したしきい値に達するのに要した時間(Ta)の対数がエン
ドトキシン濃度の対数に反比例すること(比色反応時間
法、ΔOD−time assay)に基づく定量法である。
According to this method, a coagulation enzyme finally activated by a factor C-based reaction in endotoxin and lysate has a sequence similar to the amino acid sequence of the hydrolysis site of coagulogen when converting coagulogen to coagulin. A kinetic method in which the absorbance of pNA released by the coagulation enzyme amidase activity is measured using a chromogenic synthetic substrate in which a chromogenic group p-nitroaniline (pNA) is bound to a peptide. The kinetic method is based on the rate of change in absorbance of the released pNA (mAbs / min).
Is proportional to the endotoxin concentration (colorimetric kinetic method, rate assay), or the logarithm of the time (Ta) required for the absorbance change of the reaction solution to reach a preset threshold value is the logarithm of the endotoxin concentration. It is a quantitative method based on inverse proportion (colorimetric reaction time method, ΔOD-time assay).

【0020】恒温槽と解析プログラム内蔵のマイクロプ
レートリーダー(ウェルリーダーSK601:生化学工
業)を用い、通常96穴マイクロプレートの各ウェルに
検体と比色法リムルス試薬を各0.05mlとり、ふた
をして30分間反応させる。吸光度の増加が2波長(測
定波長405nm,対照波長492nm)で経時的に計
測され、反応終了と同時に解析プログラムが作動し、同
時に測定した標準エンドトキシンの検量線から検体中の
濃度が自動算出される。
Using a thermostat and a microplate reader (well reader SK601: Seikagaku Kogyo) with a built-in analysis program, 0.05 ml of the sample and the colorimetric Limulus reagent are usually taken in each well of a 96-well microplate, and the lid is placed. And react for 30 minutes. The increase in absorbance is measured over time at two wavelengths (measurement wavelength: 405 nm, control wavelength: 492 nm), the analysis program is activated at the same time as the reaction is completed, and the concentration in the sample is automatically calculated from the standard endotoxin calibration curve measured at the same time. .

【0021】電解水の測定は、ダイレクトには測定せず
に、エンドトキシンフリーの蒸留水で10倍以上に希釈
し、測定を実施した。これは、電解水の成分が測定系に
影響を及ぼすのを避けるためである。尚、10倍以上と
いう希釈倍数は、添加回収試験により決定したものであ
る。
The measurement of the electrolyzed water was carried out by diluting the electrolyzed water 10 times or more with endotoxin-free distilled water without directly measuring it. This is to prevent the component of the electrolyzed water from affecting the measurement system. The dilution factor of 10 times or more was determined by an addition recovery test.

【0022】本発明の電解強酸性水は、原水として逆浸
透水を使用し、これを電気分解することにより製造され
るものである。
The electrolytic strongly acidic water of the present invention is produced by using reverse osmosis water as raw water and electrolyzing it.

【0023】原水として使用する逆浸透水は、通常の逆
浸透装置を用いた逆浸透法(reverseosmosis;RO)に
より得られるものであり、その製造条件としては従来か
ら慣用されている方法で採用されている条件がいずれも
使用できる。
The reverse osmosis water used as raw water is obtained by a reverse osmosis (RO) method using an ordinary reverse osmosis apparatus, and its production conditions are adopted by a conventionally used method. Any of these conditions can be used.

【0024】特に、本発明では、原水として、透析用に
使用されている逆浸透水を使用するのが好ましい。透析
液希釈水用の逆浸透水を製造するには、例えば、予備処
理として、水道水を、プレフィルター、活性炭濾過装
置、イオン交換装置、レジンフィルター等の少なくとも
1つを通過させ、次いで、逆浸透装置に導入することに
より行なうのが好ましい。特に、水道水に、プレフィル
ター、活性炭濾過装置、イオン交換装置及びレジンフィ
ルターからなる予備処理を行った上で生成させた逆浸透
水を原水として使用するのがより好ましい。
In particular, in the present invention, it is preferable to use reverse osmosis water used for dialysis as raw water. To produce reverse osmosis water for dialysate dilution water, for example, as a pretreatment, tap water is passed through at least one of a prefilter, an activated carbon filtration device, an ion exchange device, a resin filter, and the like. It is preferred to do so by introducing it into an infiltration device. In particular, it is more preferable to use, as raw water, reverse osmosis water generated after performing pretreatment of a tap water with a prefilter, an activated carbon filtration device, an ion exchange device, and a resin filter.

【0025】上記プレフィルターは、水道水中の鉄錆や
砂等の粗いごみを除去するために使用される孔径10〜
25μm程度のフィルターである。また、活性炭濾過装
置は、水道水中の遊離塩素やクロラミンを除去低減する
ための装置である。イオン交換装置は、膜のスケール防
止のために水道水中の硬度成分(カルシウム、マグネシ
ウム等)や一部の重金属成分を除去低減するための装置
である。レジンフィルターは、活性炭濾過装置から流失
した活性炭やイオン交換装置からの樹脂、及びプレフィ
ルターを通過した微粒子の除去のため使用される孔径が
通常5μm程度の一般フィルターである。
The prefilter has a pore diameter of 10 to be used for removing coarse dust such as iron rust and sand in tap water.
It is a filter of about 25 μm. The activated carbon filtration device is a device for removing and reducing free chlorine and chloramine in tap water. The ion exchange device is a device for removing and reducing hardness components (such as calcium and magnesium) and some heavy metal components in tap water in order to prevent scale of the membrane. The resin filter is a general filter having a pore size of usually about 5 μm used for removing activated carbon that has flowed off from the activated carbon filtration device, resin from the ion exchange device, and fine particles that have passed through the prefilter.

【0026】本発明では、上記逆浸透水に少量の塩化ナ
トリウムを添加した後、電気分解して電解強酸性水を製
造する。電気分解の際の条件は、慣用されている方法で
採用されている条件がいずれも使用できる。例えば、上
記逆浸透水に塩化ナトリウムを少量添加した液を、隔膜
により陽極室と陰極室とに仕切られた電解槽において電
気分解すればよい。
In the present invention, a small amount of sodium chloride is added to the above-mentioned reverse osmosis water, followed by electrolysis to produce electrolytically acidic water. As the conditions for the electrolysis, any of the conditions adopted by a commonly used method can be used. For example, a solution obtained by adding a small amount of sodium chloride to the above reverse osmosis water may be electrolyzed in an electrolytic cell partitioned by a diaphragm into an anode chamber and a cathode chamber.

【0027】現在多くのメーカーから、各種の電解水生
成装置が販売されており、本発明でもこれら市販の電解
水生成装置を使用して電気分解を行えばよい。
At present, various types of electrolyzed water generators are sold by many manufacturers, and in the present invention, electrolysis may be performed using these commercially available electrolyzed water generators.

【0028】典型的な電解水生成装置について記載する
と、その電極は、チタン棒に白金をコーティング又は焼
き付けしたものが一般的であり、隔膜は中性膜のポリエ
ステル等が使用されている。電力は、電解水の生成量に
応じて、家庭用100Vのものから動力用200Vを必
要とするものなど各種のものがあり、また、電流の条件
は、電極間の距離や塩化ナトリウム添加量等によって適
宜決定される。
To describe a typical electrolyzed water generating apparatus, the electrode is generally a titanium rod coated or baked with platinum, and a neutral membrane polyester or the like is used for the diaphragm. Depending on the amount of electrolyzed water generated, there are various types of power, such as 100 V for home use and 200 V for motive power. The current conditions include the distance between electrodes and the amount of sodium chloride added. Is determined as appropriate.

【0029】こうして得られる電解強酸性水は、必要に
応じて、電解強酸性水タンクに貯蔵しても良い。
The electrolyzed strongly acidic water thus obtained may be stored in an electrolyzed strongly acidic water tank, if necessary.

【0030】上記した本発明電解強酸性水の製造の態様
の概略を示すフローを記載した図1及び図2を参照し
て、本発明の電解強酸性水の製造方法を説明する。
With reference to FIGS. 1 and 2, which illustrate the outline of the above-described embodiment of the production of the strongly acidic electrolytic water of the present invention, the method of producing the strongly acidic electrolytic water of the present invention will be described.

【0031】図1において、まず、原料としての水道水
は、活性炭濾過装置1に導かれる。該活性炭濾過装置1
は、水道水中の鉄錆等を除去し、更に遊離塩素やクロラ
ミンを吸着除去する。活性炭濾過装置1を通過した水
は、次いで、軟水装置2に導かれ、そこでイオン交換さ
れて軟水化される。次いで、この軟水化された水を、逆
浸透装置3に導入して逆浸透法により精製する。得られ
た逆浸透水を、電解水生成装置4に導入して、電気分解
することによって、本発明の電解強酸性水を得る。
In FIG. 1, first, tap water as a raw material is led to an activated carbon filtration device 1. The activated carbon filter 1
Removes iron rust and the like in tap water and further adsorbs and removes free chlorine and chloramine. The water that has passed through the activated carbon filtration device 1 is then led to a water softening device 2 where it is ion-exchanged and softened. Next, the softened water is introduced into the reverse osmosis device 3 and purified by the reverse osmosis method. The obtained reverse osmosis water is introduced into the electrolyzed water generator 4 and electrolyzed to obtain the electrolyzed strongly acidic water of the present invention.

【0032】こうして得られた電解強酸性水は、そのま
ま配管8から取り出して使用しても良いし、また、必要
に応じて、電解強酸性水タンク5に貯液しても良い。該
電解強酸性水タンク5から、電解強酸性水が使用され、
電解強酸性水タンク5のレベルが一定以下に下がれば、
制御装置7により、電解水生成装置4と逆浸透装置3が
同時に稼働し、常に必要な強酸性水を生成する。
The thus obtained strongly acidic electrolyzed water may be taken out of the pipe 8 and used as it is, or may be stored in the strongly acidic electrolyzed water tank 5 as needed. From the electrolytic strong acid water tank 5, electrolytic strong acid water is used,
If the level of the electrolytic strongly acidic water tank 5 drops below a certain level,
By the control device 7, the electrolyzed water generation device 4 and the reverse osmosis device 3 operate simultaneously, and always generate the required strongly acidic water.

【0033】図1のように、逆浸透装置3と電解水生成
装置4とを直結すると、逆浸透水タンクなどを設置する
ことによる滞留によって生じる汚染や外部からの汚染を
極力排除することができる。
As shown in FIG. 1, when the reverse osmosis device 3 and the electrolyzed water generating device 4 are directly connected to each other, contamination caused by stagnation caused by installing a reverse osmosis water tank and the like and external contamination can be eliminated as much as possible. .

【0034】しかし、場合によっては、図2のごとく、
逆浸透水タンク9を、逆浸透装置3と電解水生成装置4
との間に設置しても良い。その場合、該タンク9に、電
解強酸性水を配管6を経由して送液し、シャワリングな
どの方法で該タンク9を殺菌洗浄することも可能であ
る。
However, in some cases, as shown in FIG.
The reverse osmosis water tank 9 includes the reverse osmosis device 3 and the electrolyzed water generation device 4.
And may be installed between them. In this case, it is also possible to send electrolytic strongly acidic water to the tank 9 via the pipe 6 and sterilize and wash the tank 9 by a method such as showering.

【0035】本発明方法により得られる電解強酸性水
は、通常、pH2.7以下、酸化還元電位(ORP)1
100mV以上、有効塩素濃度10〜40ppm程度で
あり、特にpH2.7〜2.4程度、ORP1100〜
1150mV程度、有効塩素濃度15〜30ppm程度
であるのが好ましい。
The electrolyzed strongly acidic water obtained by the method of the present invention usually has a pH of 2.7 or less and an oxidation-reduction potential (ORP) of 1 or less.
100 mV or more, effective chlorine concentration is about 10 to 40 ppm, especially about pH 2.7 to 2.4, ORP1100
Preferably, it is about 1150 mV and the effective chlorine concentration is about 15 to 30 ppm.

【0036】本発明に従い、逆浸透水を原水として使用
すると、従来のように水道水を原水として使用する場合
に比し、電解水生成装置においてスケールの発生が極め
て少なく、従来行われていた逆洗や印加電圧極性の反転
が少なくて済み、そのため電解水生成装置の電極の劣化
が防止され、安定して一定の性質を有する電解強酸性水
が得られる。
According to the present invention, when reverse osmosis water is used as raw water, the generation of scale in the electrolyzed water generator is extremely small compared to the case where tap water is used as raw water as in the past, and the reverse water conventionally used is used. The washing and the reversal of the polarity of the applied voltage are small, so that the electrode of the electrolyzed water generator is prevented from being deteriorated, and the electrolyzed strongly acidic water having stable and constant properties can be obtained.

【0037】しかも、逆浸透水を原水として使用して電
気分解により得られる電解強酸性水は、使用する原水で
ある逆浸透水が、通常はエンドトキシンを少量しか含有
していないこともあって、製造直後の本発明電解強酸性
水中のエンドトキシン量は極めて少なく、たとえ、製造
直後の本発明電解強酸性水中のエンドトキシン濃度が、
健常人の体内に通常存在する15EU/リットルを若干
越える濃度を有していたとしても、本発明電解強酸性水
の製造直後から1時間を経過した時点では、15EU/
リットル以下の濃度となる性質を有する。
In addition, the strongly acidic electrolytic water obtained by electrolysis using reverse osmosis water as raw water has a problem that the reverse osmosis water used as raw water usually contains only a small amount of endotoxin. The amount of endotoxin in the electrolytic strongly acidic water of the present invention immediately after production is extremely small, for example, the endotoxin concentration in the electrolytic strongly acidic water of the present invention immediately after production is
Even if it has a concentration slightly higher than 15 EU / liter which is normally present in the body of a healthy person, at the point of time one hour immediately after the production of the electrolytic strong acid water of the present invention, 15 EU / liter
It has the property that the concentration becomes less than liter.

【0038】なお、原水として、エンドトキシン濃度の
低い逆浸透水を用いると、本発明電解強酸性水は、製造
直後から約30分経過という早い時点でも、例えば、1
0EU/リットル又は5EU/リットル以下程度の極め
て低いエンドトキシン濃度を有することになる。
When reverse osmosis water having a low endotoxin concentration is used as raw water, the electrolyzed strongly acidic water of the present invention can be produced, for example, at a time as short as about 30 minutes immediately after the production, for example, at 1 point.
It will have very low endotoxin concentrations of the order of 0 EU / liter or less, such as 5 EU / liter or less.

【0039】従って、本発明の電解強酸性水は、これを
臨床の分野で殺菌等の目的で使用する場合に、体内に入
ったとしてもそのエンドトキシン濃度が通常の健常人の
体内で見出される濃度程度の極めて低いものであるか
ら、安全性が極めて高いものである。
Therefore, when the strongly acidic electrolytic water of the present invention is used for the purpose of sterilization or the like in the clinical field, even if it enters the body, its endotoxin concentration can be found in the body of a normal healthy person. Since the degree is extremely low, the safety is extremely high.

【0040】更に、驚くべきことに、本発明者の研究に
よれば、原水として逆浸透水を用いて製造された本発明
の電解強酸性水は、殺菌作用を持つばかりではなく、通
常の水道水を原水として製造された電解強酸性水に比
し、極めて良好なエンドトキシン不活化作用を有してい
ることが明らかとなった。
Furthermore, surprisingly, according to the research of the present inventor, the electrolytically acidic water of the present invention produced using reverse osmosis water as raw water has not only a bactericidal action but also a normal tap water. It has been revealed that it has an extremely good endotoxin inactivating effect as compared with electrolytically acidic water produced using water as raw water.

【0041】即ち、水道水を原水として使用して電解強
酸性水を製造すると、得られる電解強酸性水中には、製
造直後に数千EU/リットル程度の予想外に高い濃度の
エンドトキシンが含まれており、該電解強酸性水がエン
ドトキシン不活化作用を有するにも拘わらず、当初の高
いエンドトキシン濃度が極めて緩慢にしか減少しない。
これに対して、本願発明に従って、逆浸透水を原水とし
て使用して得られた電解強酸性水は、製造直後のエンド
トキシン濃度が低く、しかも、これに数千EU/リット
ル程度のエンドトキシンを添加した場合、その数千EU
/リットルのエンドトキシン濃度が急速に減少すること
が明らかとなった。
That is, when the electrolytic strongly acidic water is produced using tap water as raw water, the obtained electrolytically strong acidic water contains an unexpectedly high concentration of endotoxin of about several thousand EU / liter immediately after production. In spite of the fact that the electrolytic strongly acidic water has an endotoxin inactivating effect, the initially high endotoxin concentration decreases only very slowly.
On the other hand, according to the present invention, the electrolyzed strongly acidic water obtained by using reverse osmosis water as raw water has a low endotoxin concentration immediately after production, and endotoxin of about several thousand EU / liter is added thereto. In that case, the thousands of EU
It was found that the concentration of endotoxin per liter rapidly decreased.

【0042】即ち、本発明の電解強酸性水は、水道水を
原水として得られる電解強酸性水に比し、より強力なエ
ンドトキシン不活化作用を有する。
That is, the electrolyzed strongly acidic water of the present invention has a stronger endotoxin inactivating effect than the electrolyzed strongly acidic water obtained using tap water as raw water.

【0043】従って、本発明の電解強酸性水は、エンド
トキシン不活化剤として有用であり、例えば、医療用と
して、術創や壊死、褥創等の創部処置等や、血液透析装
置の透析液配管系の洗浄に有利に使用できる。
Accordingly, the strongly acidic electrolytic water of the present invention is useful as an endotoxin inactivating agent. For example, for medical treatment, wound treatment for surgical wounds, necrosis, pressure sores, etc., and dialysis solution piping for hemodialysis equipment It can be used advantageously for cleaning systems.

【0044】本発明の電解強酸性水をエンドトキシン不
活化剤として使用する場合、エンドトキシンを不活化な
いし除去する箇所に、本発明の電解強酸性水を接触させ
ればよい。接触時間は、当該箇所のエンドトキシン濃度
が高いほど長時間接触させればよい。従って、一般に
は、エンドトキシンを不活化する必要のある箇所のエン
ドトキシン濃度と本発明電解強酸性水によるエンドトキ
シン不活化速度との関係を予め調べておいて、所望の結
果が得られるように、接触時間等の条件を適宜決定すれ
ばよい。例えば、数千EU/リットル程度のエンドトキ
シンは、本発明の電解強酸性水中では、約2時間で約1
/10から1/30の濃度に低下するので、これを目安
に使用量や接触時間を適宜決定すればよい。
When the strongly acidic electrolytic solution of the present invention is used as an endotoxin inactivating agent, the strongly acidic electrolytic solution of the present invention may be brought into contact with a portion where the endotoxin is inactivated or removed. As for the contact time, the higher the endotoxin concentration at the site, the longer the contact. Therefore, in general, the relationship between the endotoxin concentration at the site where the endotoxin needs to be inactivated and the rate of endotoxin inactivation by the strongly acidic water of the present invention is examined in advance, and the contact time is adjusted so that a desired result can be obtained. And the like may be appropriately determined. For example, endotoxin of about several thousand EU / liter is about 1 hour in about 2 hours in the strongly acidic water of the present invention.
Since the concentration decreases from / 10 to 1/30, the amount to be used and the contact time may be appropriately determined based on this.

【0045】本発明のエンドトキシ不活化剤を使用する
際の温度条件は特に限定されないが、通常は10〜50
℃程度が好ましく、20〜40℃程度がより好ましい。
The temperature conditions when using the endotoxin inactivating agent of the present invention are not particularly limited.
C. is preferable, and about 20 to 40 C. is more preferable.

【0046】[0046]

【実施例】以下、実施例を掲げて、本発明をより一層詳
しく説明する。
EXAMPLES Hereinafter, the present invention will be described in more detail with reference to Examples.

【0047】なお、以下の実施例及び比較例並びに試験
例において、エンドトキシン濃度の測定は、前記した
「透析液エンドトキシンがよくわかる本」、竹沢真吾編
集、株式会社東京医学社、1995年7月1日発行、第
38〜39頁に記載の合成基質法のエンドスペシー法
(カイネティック法)でマイクロプレートリーダーにて
室温(22〜25℃)で測定した。電解強酸性水中のエ
ンドトキシン濃度については、電解強酸性水を採取と同
時に10倍に希釈し、反応を停止させることにより、採
取時点でのエンドトキシンの値(ET値)を室温(22
〜25℃)で測定した。
In the following Examples, Comparative Examples, and Test Examples, the endotoxin concentration was measured by the above-mentioned "Dialysis Fluid Endotoxin is well understood", edited by Shingo Takezawa, Tokyo Medical Co., Ltd., July 1, 1995. The measurement was carried out at room temperature (22 to 25 ° C.) using a microplate reader by the endospecies method (kinetic method) of the synthetic substrate method described on pages 38 to 39, published on the day of publication. Regarding the endotoxin concentration in the electrolytic strongly acidic water, the value of the endotoxin at the time of collection (ET value) was reduced to room temperature (22
2525 ° C.).

【0048】尚、測定に関して、測定限界値は2EU/
リットルであり、測定信頼値を5EU/リットルとし
た。
As for the measurement, the measurement limit value is 2 EU /
Liter, and the measurement reliability value was 5 EU / liter.

【0049】実施例1 (a)逆浸透水の製造 水処理装置(三菱レイヨン・エンジニアリング社製)を
使用し、該装置から生成された逆浸透水を、逆浸透水タ
ンク500リットルに貯水し、その逆浸透水のET値を
測定した。この方法を、日時を変更して、合計4回行な
った。
Example 1 (a) Production of Reverse Osmosis Water Using a water treatment device ( manufactured by Mitsubishi Rayon Engineering Co., Ltd.), reverse osmosis water generated from the device was stored in a 500 liter reverse osmosis water tank. The ET value of the reverse osmosis water was measured. This method was performed a total of four times, changing the date and time.

【0050】こうして、エンドトキシン濃度が7、2
3、91及び124EU/リットルの4種類の逆浸透水
を得た。
Thus, the endotoxin concentration was 7, 2
Four types of reverse osmosis water of 3, 91 and 124 EU / liter were obtained.

【0051】(b)電解強酸性水の製造 上記において貯水した4種の逆浸透水の各500リット
ルを、一般に市販されている電解水生成装置に導入し、
4種の電解強酸性水を得た。
(B) Production of Electrolyzed Strongly Acidic Water Each 500 liters of the four types of reverse osmosis water stored above are introduced into a generally commercially available electrolyzed water generator,
Four kinds of electrolytic strongly acidic water were obtained.

【0052】こうして得られた4種の本発明電解強酸性
水のpH、酸化還元電位(ORP)及び有効塩素濃度
は、下記表1の通りであった。
The pH, oxidation-reduction potential (ORP) and effective chlorine concentration of the thus obtained four kinds of strongly acidic water of the present invention are as shown in Table 1 below.

【0053】[0053]

【表1】 [Table 1]

【0054】試験例1 上記実施例1において製造した4種の本発明電解強酸性
水の製造直後のエンドトキシン濃度、製造直後から30
分、1時間及び2時間経過後のエンドトキシン濃度を測
定した。
Test Example 1 The endotoxin concentrations immediately after the production of the four kinds of strongly acidic electrolyzed water of the present invention produced in the above-mentioned Example 1, and the endotoxin concentrations immediately after the production were 30%.
The endotoxin concentration was measured after 1 minute and 1 hour.

【0055】結果を下記表2に示す。The results are shown in Table 2 below.

【0056】[0056]

【表2】 [Table 2]

【0057】表2から明らかなように、本発明の電解強
酸性水は、製造直後のエンドトキシン濃度がかなり低
く、いずれも製造直後から30分を経過した時点でエン
ドトキシン濃度が測定信頼値の5EU/リットル以下の
極めて低い濃度となることが判る。
As is evident from Table 2, the electrolyzed strongly acidic water of the present invention has a very low endotoxin concentration immediately after its production, and the endotoxin concentration is 5 EU / measured at 30 minutes after production. It can be seen that the concentration is very low, less than one liter.

【0058】比較例1 原水として、逆浸透水に代えて、水道水を使用する以外
は実施例1(b)と同様にして、電解強酸性水を得た。
COMPARATIVE EXAMPLE 1 Electrolytic strongly acidic water was obtained in the same manner as in Example 1 (b) except that tap water was used as raw water instead of reverse osmosis water.

【0059】得られた電解強酸性水の物性は、pH2.
5、酸化還元電位1130mV及び有効塩素濃度25p
pmであった。
The properties of the obtained strongly acidic electrolytic water were adjusted to pH 2.
5. Redox potential 1130mV and effective chlorine concentration 25p
pm.

【0060】試験例2 (a)上記比較例1において原水として使用した水道水
について、採取直後、採取から30分間、1時間及び2
時間経過後のエンドトキシン濃度を測定した。
Test Example 2 (a) For tap water used as raw water in Comparative Example 1, immediately after collection, 30 minutes after collection, 1 hour and 2 hours
After the lapse of time, the endotoxin concentration was measured.

【0061】また、比較例1において得られた電解強酸
性水についても、製造直後、製造直後から30分間、1
時間及び2時間経過後のエンドトキシン濃度を測定し
た。
The electrolytically acidic water obtained in Comparative Example 1 was also used immediately after production, for 30 minutes immediately after production.
Time and the endotoxin concentration after 2 hours were measured.

【0062】(b)上記実施例1において逆浸透水を原
水として製造した本発明の電解強酸性水(製造直後から
10分以内のもの)に、エンドトキシンを含有する逆浸
透水を、該電解強酸性水中のエンドトキシン濃度が、8
157EU/リットル又は8005EU/リットルの濃
度となるように添加した。添加直後および添加から30
分間、1時間及び2時間経過後のエンドトキシン濃度を
測定した。
(B) Reverse osmosis water containing endotoxin was added to the strongly acidic water of the present invention (within 10 minutes from immediately after the production) produced in Example 1 using the reverse osmosis water as raw water, Endotoxin concentration in sexual water is 8
It was added to a concentration of 157 EU / liter or 8005 EU / liter. Immediately after addition and 30 after addition
After 1 minute, 1 hour and 2 hours, the endotoxin concentration was measured.

【0063】結果を下記表3に示す。The results are shown in Table 3 below.

【0064】[0064]

【表3】 [Table 3]

【0065】また、上記表3の結果から、原水における
エンドトキシン濃度又は添加エンドトキシン量を基準と
して、水道水原水採取直後、電解強酸性水製造直後又は
エンドトキシン添加直後及びそれから30分間、1時間
及び2時間経過後のエンドトキシン濃度を百分率に換算
した結果(エンドトキシン残存率)をグラフにして、図
3に示す。なお、表3中の記号A〜Dは、図3中のカー
ブA〜Dに、それぞれ対応する。
From the results in Table 3 above, based on the endotoxin concentration in the raw water or the amount of added endotoxin, immediately after collecting tap water raw water, immediately after producing electrolytically acidic water or immediately after adding endotoxin, and 30 minutes, 1 hour and 2 hours thereafter FIG. 3 is a graph showing the results (endotoxin residual rate) obtained by converting the endotoxin concentration after passage into percentage. The symbols A to D in Table 3 correspond to the curves A to D in FIG. 3, respectively.

【0066】表3及び図3から明らかなように、水道水
を原水として製造した電解強酸性水は、製造直後のエン
ドトキシン濃度が高く、その後のエンドトキシン濃度減
少もその速度が緩慢であって、原水中の濃度を100%
とした場合、製造直後に原水中の濃度の約60%程度に
相当する濃度となるが、製造直後から2時間経過して
も、なお原水中の濃度の約40%程度に相当する高い濃
度が維持されている。
As is clear from Table 3 and FIG. 3, the electrolyzed strongly acidic water produced using tap water as raw water has a high endotoxin concentration immediately after production, and the rate of decrease in endotoxin concentration thereafter is slow. 100% concentration in water
In this case, immediately after the production, the concentration becomes about 60% of the concentration in the raw water. However, even after 2 hours from the production, the high concentration equivalent to about 40% of the concentration in the raw water still remains. Has been maintained.

【0067】これに対して、本発明に従い得られた電解
強酸性水に、上記水道水原水中に存在するのと同程度の
エンドトキシンを添加した場合、添加直後に添加濃度の
45〜50%程度に相当する濃度に減少し、その後は急
速に減少し、添加から2時間経過後は、添加エンドトキ
シン濃度のわずか3%程度まで減少する。
On the other hand, when the same level of endotoxin as that present in the tap water raw water is added to the electrolytic strongly acidic water obtained according to the present invention, the endotoxin concentration becomes about 45 to 50% of the added concentration immediately after the addition. It decreases to the corresponding concentration, and then rapidly decreases, and after 2 hours from the addition, decreases to only about 3% of the added endotoxin concentration.

【0068】従って、本発明の電解強酸性水のエンドト
キシン不活化効果が極めて強いことが判る。
Therefore, it can be seen that the endotoxin inactivating effect of the electrolytic strongly acidic water of the present invention is extremely strong.

【0069】[0069]

【発明の効果】上記から明らかなように、本発明の電解
強酸性水は、製造直後でも低いエンドトキシン濃度を有
し、製造直後から1時間も経過すると、健常人の体内に
通常存在するエンドトキシン濃度である15EU/リッ
トル以下という極めて低いエンドトキシン濃度を有して
いる。
As is evident from the above, the electrolyzed strongly acidic water of the present invention has a low endotoxin concentration even immediately after production, and one hour after the production, the endotoxin concentration normally present in the body of a healthy person is obtained. Has an extremely low endotoxin concentration of 15 EU / liter or less.

【0070】従って、本発明電解強酸性水を、臨床分野
で殺菌等の目的で使用する場合に、安全性が極めて高
い。
Therefore, when the electrolytic strongly acidic water of the present invention is used for sterilization or the like in the clinical field, the safety is extremely high.

【0071】また、本発明の電解強酸性水は、水道水を
原水として得られた電解強酸性水に比し、エンドトキシ
ン不活化効果が高い。従って、本発明の電解強酸性水
は、エンドトキシン不活化剤として有用性が一段と高い
ものである。
The strongly acidic electrolyzed water of the present invention has a higher endotoxin inactivating effect than the strongly acidic electrolyzed water obtained using tap water as raw water. Therefore, the electrolyzed strongly acidic water of the present invention is much more useful as an endotoxin inactivating agent.

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

【図1】本発明の電解強酸性水製造の一態様を示すフロ
ー図である。
FIG. 1 is a flowchart showing one embodiment of the production of an electrolytic strongly acidic water of the present invention.

【図2】本発明の電解強酸性水製造の他の態様を示すフ
ロー図である。
FIG. 2 is a flowchart showing another embodiment of the production of an electrolytic strongly acidic water of the present invention.

【図3】試験例2で測定したエンドトキシン濃度の経時
的変化の値(表3)を、百分率に換算した結果(エンド
トキシン残存率)を示すグラフである。
FIG. 3 is a graph showing the results (endotoxin residual ratio) of converting the values of the endotoxin concentration over time (Table 3) measured in Test Example 2 into percentages.

【符号の説明】[Explanation of symbols]

1 活性炭濾過装置 2 軟水装置 3 逆浸透装置 4 電解水生成装置 5 電解強酸性水タンク 6 配管 7 制御装置 9 逆浸透水タンク DESCRIPTION OF SYMBOLS 1 Activated carbon filtration apparatus 2 Soft water apparatus 3 Reverse osmosis apparatus 4 Electrolyzed water generation apparatus 5 Electrolytic strongly acidic water tank 6 Piping 7 Control apparatus 9 Reverse osmosis water tank

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 逆浸透水を電解して得られる電解強酸性
水であって、該電解強酸性水の製造直後から1時間経過
した時点で、15EU/リットル以下のエンドトキシン
濃度を有していることを特徴とする電解強酸性水。
1. An electrolyzed strongly acidic water obtained by electrolyzing reverse osmosis water, which has an endotoxin concentration of 15 EU / liter or less at the time of one hour immediately after the production of the electrolyzed strongly acidic water. Electrolytic strongly acidic water characterized by the following.
【請求項2】 逆浸透水を電解することを特徴とする請
求項1に記載の電解強酸性水の製造法。
2. The method according to claim 1, wherein the reverse osmosis water is electrolyzed.
【請求項3】 逆浸透水を電解して得られる電解強酸性
水であって、該電解強酸性水の製造直後から1時間経過
した時点で、15EU/リットル以下のエンドトキシン
濃度を有している電解強酸性水を含有することを特徴と
するエンドトキシン不活化剤。
3. An electrolyzed strongly acidic water obtained by electrolyzing reverse osmosis water, which has an endotoxin concentration of 15 EU / liter or less when one hour has passed immediately after the production of the electrolyzed strongly acidic water. An endotoxin inactivating agent comprising electrolytically strongly acidic water.
JP34864996A 1996-12-26 1996-12-26 Electrolytic strongly acidic water, its production and endotoxin inactivator consisting of the strongly acidic water Pending JPH10180256A (en)

Priority Applications (3)

Application Number Priority Date Filing Date Title
JP34864996A JPH10180256A (en) 1996-12-26 1996-12-26 Electrolytic strongly acidic water, its production and endotoxin inactivator consisting of the strongly acidic water
PCT/JP1997/002462 WO1998029347A1 (en) 1996-12-26 1997-07-15 Strongly acidic electrolyzed water, process for preparing the same, and endotoxin inactivator comprising said strongly acidic electrolyzed water
AU34611/97A AU3461197A (en) 1996-12-26 1997-07-15 Strongly acidic electrolyzed water, process for preparing the same, and endotoxin inactivator comprising said strongly acidic electrolyzed water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP34864996A JPH10180256A (en) 1996-12-26 1996-12-26 Electrolytic strongly acidic water, its production and endotoxin inactivator consisting of the strongly acidic water

Publications (1)

Publication Number Publication Date
JPH10180256A true JPH10180256A (en) 1998-07-07

Family

ID=18398430

Family Applications (1)

Application Number Title Priority Date Filing Date
JP34864996A Pending JPH10180256A (en) 1996-12-26 1996-12-26 Electrolytic strongly acidic water, its production and endotoxin inactivator consisting of the strongly acidic water

Country Status (3)

Country Link
JP (1) JPH10180256A (en)
AU (1) AU3461197A (en)
WO (1) WO1998029347A1 (en)

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JP2004505770A (en) * 2000-08-11 2004-02-26 エイチツーオー・テクノロジーズ・リミテッド Water treatment system under the sink
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Publication number Priority date Publication date Assignee Title
JP2004505770A (en) * 2000-08-11 2004-02-26 エイチツーオー・テクノロジーズ・リミテッド Water treatment system under the sink
JP2007307502A (en) * 2006-05-19 2007-11-29 Ichiro Shoda Method for generating electrolytic water and electrolytic water generator
JP4641003B2 (en) * 2006-05-19 2011-03-02 一郎 庄田 Electrolyzed water generation method and electrolyzed water generator
JP2008100180A (en) * 2006-10-19 2008-05-01 Hakatako Kanri Kk Water treatment apparatus
WO2012176554A1 (en) * 2011-06-21 2012-12-27 パナソニック株式会社 Electrolyzed water producing device
CN104591445A (en) * 2015-01-07 2015-05-06 成都邦研科技有限公司 Acidic electrolyzed oxidizing water generator based on double electrolysis
CN104591446A (en) * 2015-01-07 2015-05-06 成都邦研科技有限公司 Softening-electrolysis integrated acidic electrolyzed oxidizing water reactor
CN104628194A (en) * 2015-01-07 2015-05-20 成都邦研科技有限公司 Double-filtration acidic oxidation potential water reactor
CN104628194B (en) * 2015-01-07 2016-08-24 成都邦研科技有限公司 Double filtration acidic oxidized electric potential water reactor

Also Published As

Publication number Publication date
AU3461197A (en) 1998-07-31
WO1998029347A1 (en) 1998-07-09

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