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JP2006198499A - Method for sterilizing water and sterilization apparatus - Google Patents

Method for sterilizing water and sterilization apparatus Download PDF

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JP2006198499A
JP2006198499A JP2005011761A JP2005011761A JP2006198499A JP 2006198499 A JP2006198499 A JP 2006198499A JP 2005011761 A JP2005011761 A JP 2005011761A JP 2005011761 A JP2005011761 A JP 2005011761A JP 2006198499 A JP2006198499 A JP 2006198499A
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Tadashi Mochizai
正 持麾
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a sterilization apparatus capable of sterilizing flow water continuously with a simple configuration and a low operation cost, without remaining a substance in sterilized water that affects the health of mankind, and safe and cheap. <P>SOLUTION: An injector 2 is disposed to a water flow pipe 1 through which flowing water flows to pressure-feed air or ozone 3 into this injector 2. Air or ozone 3 is passed through an air diffuser plate 4 and dispersed. Gas-liquid mixture flow water 5 is made at the constriction of the water flow pipe 1 and activated by passing through between an N pole 6 and an S pole 7 of a permanent magnet 8 disposed apart from the water flow pipe 1 to react with an oxygen radical to make a hydroxyl radical, thereby sterilizing water itself. <P>COPYRIGHT: (C)2006,JPO&NCIPI

Description

本発明は、水の殺菌方法とこの方法を実現する殺菌装置に関し、特に水自身を活性化してヒドロキシラジカル化することによって殺菌を行なう方法およびこの方法を実現する殺菌装置に関する。   The present invention relates to a water sterilization method and a sterilization apparatus that realizes this method, and more particularly to a method for sterilization by activating water itself to form a hydroxyl radical and a sterilization apparatus that realizes this method.

従来、水を殺菌する方法としては、化学的には塩素による方法、オゾンガスによる方法、次亜塩素酸ソーダなどの薬品による方法などが主なものであり、物理的には紫外線照射による方法、紫外線と光触媒による方法などが採用されていた。
しかし、塩素殺菌による残留塩素が人の健康に及ぼす影響は周知の通りで、原水の質によっては発がん物質であるトリハロメタンを発生する虞も有している。オゾン殺菌の場合は、水中におけるオゾンの分解速度が遅く、また充分に殺菌するためには高濃度のオゾンを注入する必要があるため、流水が装置を通過する時間内に分解されきれず、オゾンが残って残留オゾンの処理に手間がかかるという難点があり、一般での使用には問題が多い。さらに紫外線による殺菌方法は、紫外線発光源である照射管の寿命が8000〜12000時間と限られているため、頻繁な取替えが必要で、運転費用が高価なものになるという問題がある。
従来例として、例えば、電解槽で次亜塩素酸を発生させて殺菌する方法(特許文献1参照。)、オゾン水供給装置を用いる方法(特許文献2参照。)、紫外線を発生するフラッシュランプを用いる方法(特許文献3参照。)、酸化還元加熱殺菌による方法(特許文献4参照。)などが報告されているが何れも装置が大規模であったり、運転費用が高価であるという問題を有している。
特開2004−202466号公報 特開2004−330050号公報 特開2004−57844号公報 特開2004−330176号公報
Conventionally, as a method of sterilizing water, a chemical method such as chlorine, a method using ozone gas, a method using chemicals such as sodium hypochlorite, etc. are mainly used. And photocatalytic methods were used.
However, the effect of residual chlorine by chlorine sterilization on human health is well known, and depending on the quality of the raw water, there is a possibility of generating trihalomethane, which is a carcinogen. In the case of ozone sterilization, the decomposition rate of ozone in water is slow, and it is necessary to inject high-concentration ozone to fully sterilize. However, there is a problem that it takes time to process residual ozone, and there are many problems in general use. Furthermore, the sterilization method using ultraviolet rays has a problem that the life of an irradiation tube which is an ultraviolet light emission source is limited to 8000 to 12000 hours, so that frequent replacement is necessary and the operation cost becomes expensive.
As a conventional example, for example, a method of generating and sterilizing hypochlorous acid in an electrolytic cell (see Patent Document 1), a method of using an ozone water supply device (see Patent Document 2), and a flash lamp that generates ultraviolet rays. A method to be used (see Patent Document 3) and a method by oxidation-reduction heat sterilization (see Patent Document 4) have been reported, but all have problems that the apparatus is large-scale and the operation cost is expensive. is doing.
JP 2004-202466 A JP 2004-330050 A JP 2004-57844 A JP 2004-330176 A

従来の水の殺菌方法では、塩素やオゾンなどの薬品による殺菌方法では健康に影響を与える物質が水に残る虞があり、また紫外線を用いるなどの方法では運転費用が高価になるという問題があった。本発明はこのような問題を解決するためになされたもので、比較的簡単な構成でかつ廉価な運転費用で、連続して流水を殺菌することができ、殺菌した水に人の健康に影響するような物質が残ることがない安全、廉価な殺菌方法とその殺菌方法を実現する装置を提供することを課題とする。   In conventional water sterilization methods, chemicals such as chlorine and ozone may cause substances that affect health to remain in the water, and methods such as the use of ultraviolet rays are expensive to operate. It was. The present invention has been made to solve such problems, and can continuously sterilize running water with a relatively simple structure and low operating cost, and the sterilized water affects human health. It is an object of the present invention to provide a safe and inexpensive sterilization method that does not leave such a substance and a device that realizes the sterilization method.

上記課題を解決するため、本発明の請求項1の発明は、水の殺菌方法において、空気注入器を用いて空気を注入して気液混合を行った直後の通水管を流れる水を、高密度な磁束線の中を通過させて、前記水を活性化させるとともに前記空気中の酸素を活性化させ、前記水と前記酸素との反応によって生じるOH-(ヒドロキシルラジカル)を用いて殺菌を行うことを特徴とする。 In order to solve the above-mentioned problems, the invention of claim 1 of the present invention is a water sterilization method, wherein water flowing through a water pipe immediately after injecting air using an air injector and performing gas-liquid mixing is increased. Passing through the dense magnetic flux lines, the water is activated and oxygen in the air is activated, and sterilization is performed using OH (hydroxyl radical) generated by the reaction between the water and the oxygen. It is characterized by that.

上記課題を解決するため、本発明の請求項2の発明は、水の殺菌方法において、オゾンを注入して気液混合を行った直後の通水管を流れる水を、高密度な磁束線の中を通過させて、前記オゾンの分解によって生成された活性酸素と前記磁束線によって活性化された前記水との反応によって生じるOH-(ヒドロキシルラジカル)を用いて殺菌を行うことを特徴とする。 In order to solve the above-mentioned problem, the invention according to claim 2 of the present invention is a method for sterilizing water, in which water flowing through a water pipe immediately after ozone-injection and gas-liquid mixing is conducted in high-density magnetic flux lines. And is sterilized using OH (hydroxyl radical) generated by the reaction between the active oxygen generated by the decomposition of ozone and the water activated by the magnetic flux lines.

上記課題を解決するため、本発明の請求項3の発明は、水の殺菌装置において、流水を流す通水管と、前記流水に加圧された空気又はオゾンを注入して気液混合を行う注入器と、前記通水管を隔ててそのN極とS極が対向された少なくとも1対の永久磁石とを具備し、 気液混合された前記流水および前記空気又はオゾンが前記永久磁石から発生される磁束線を直角によぎることによって活性化され、OH-(ヒドロキシルラジカル)を形成して前記流水を殺菌することを特徴とする。 In order to solve the above-mentioned problem, the invention of claim 3 of the present invention is a water sterilization apparatus, wherein a water pipe for flowing water and injection for injecting air or ozone pressurized into the water to perform gas-liquid mixing And at least one pair of permanent magnets whose north and south poles face each other across the water pipe, and the flowing water and the air or ozone mixed with each other are generated from the permanent magnet. It is activated by crossing the magnetic flux lines at right angles to form OH (hydroxyl radical) to sterilize the running water.

以上に述べたように、本発明の水の殺菌方法は、磁力と酸素との相乗効果によって水自身からOH-(ヒドロキシルラジカル)を形成し、このOH-(ヒドロキシルラジカル)によって殺菌を行うので、簡単な構成でかつ廉価な運転費用で連続して流水を殺菌することができ、殺菌した水には人の健康に影響するような物質が残ることがないので、安全かつ廉価な殺菌方法とその殺菌方法を実現する装置を提供することができる。 As described above, the water sterilization method of the present invention forms OH (hydroxyl radical) from water itself by the synergistic effect of magnetic force and oxygen, and sterilizes with this OH (hydroxyl radical). Since it is possible to sterilize running water continuously with a simple structure and at low operating costs, and since there are no substances remaining in the sterilized water that affect human health, a safe and inexpensive sterilization method and its An apparatus for realizing the sterilization method can be provided.

以下、本発明にかかる水の殺菌装置を添付図面を参照にして詳細に説明する。   Hereinafter, a water sterilizer according to the present invention will be described in detail with reference to the accompanying drawings.

図1は、本発明の水の殺菌装置の内部構造を示す一部透視斜視図である。また、図2はこの殺菌装置の一実施の形態の断面図である。図1及び図2において、符号1は通水管、符号2は注入器(エジェクター)、符号3は空気又はオゾン、符号4は散気板、符号5は気液混合流水、符号6は永久磁石のN極、符号7は永久磁石のS極、符号8はN極、S極一対の永久磁石、符号9はフランジ、符号10は筺体である。   FIG. 1 is a partially transparent perspective view showing the internal structure of the water sterilizer of the present invention. Moreover, FIG. 2 is sectional drawing of one Embodiment of this sterilizer. 1 and 2, reference numeral 1 is a water pipe, reference numeral 2 is an injector, reference numeral 3 is air or ozone, reference numeral 4 is a diffuser plate, reference numeral 5 is a gas-liquid mixed flowing water, and reference numeral 6 is a permanent magnet. N pole, reference numeral 7 is an S pole of a permanent magnet, reference numeral 8 is a pair of permanent magnets of N pole and S pole, reference numeral 9 is a flange, and reference numeral 10 is a casing.

図1、図2に示すような構成で、通水管1の下部から流水を流し込み、注入器2へは空気又はオゾン3を圧送する。空気又はオゾン3は散気板4を通過して分散され、通水管1の絞り込んだ部分での水の流れによって生まれる負圧により流水と混合され、この混合で生まれた気液混合流水5が永久磁石8のN極6とS極7との間を通過する。すると、フレミングの法則にしたがって、起電流が気液混合流水5と直角方向に発生する。この起電流の強度Eは、N極6、S極7間の磁束密度Bと流水5の速度Vとに比例し、式(1)で表すことができる。   In the configuration shown in FIGS. 1 and 2, running water is poured from the lower portion of the water pipe 1, and air or ozone 3 is pumped to the injector 2. The air or ozone 3 is dispersed through the diffuser plate 4 and mixed with the flowing water by the negative pressure generated by the flow of water in the narrowed portion of the water flow pipe 1, and the gas-liquid mixed flowing water 5 generated by this mixing is permanent. It passes between the N pole 6 and the S pole 7 of the magnet 8. Then, in accordance with Fleming's law, an electromotive current is generated in a direction perpendicular to the gas-liquid mixed flowing water 5. The intensity E of the electromotive current is proportional to the magnetic flux density B between the N pole 6 and the S pole 7 and the velocity V of the flowing water 5 and can be expressed by the equation (1).

(数1)
E=kBV (1)
ただし、Eは起電流の強度、kは定数、Bは磁束密度、Vは流水の速度である。
(Equation 1)
E = kBV (1)
However, E is the intensity of the electromotive current, k is a constant, B is the magnetic flux density, and V is the velocity of flowing water.

このようにして発生される起電流すなわち電子の流れによって、水は微弱な電気分解作用を呈し、水分子の双極性が高まり、水が還元力のあるものに活性化され、反応性の高いものになる。
一方、流水に含まれる空気中の酸素は電子受容体であり、基底状態の酸素Oは電子を受容することにより、式(2)に示すようにスーパーオキシドを経て活性酸素(一重項酸素、酸素ラジカル)を生成する。
Due to the electromotive current generated in this way, ie, the flow of electrons, water exhibits a weak electrolysis action, the bipolar nature of water molecules increases, water is activated to have a reducing power, and has high reactivity. become.
On the other hand, oxygen in the air contained in the flowing water is an electron acceptor, and oxygen O 2 in the ground state accepts electrons, so that active oxygen (singlet oxygen, Oxygen radicals).

(数2)
+2e-→O -→O-+O- (2)
(Equation 2)
O 2 + 2e → O 2 → O + O (2)

また、オゾンOは磁束線を通過の際に分解を早め、基底状態の酸素Oに遷移する過程で、式(3)に示すようにスーパーオキシドを生成し、さらに分解して活性酸素(一重項酸素、酸素ラジカル)を生成する。 In addition, ozone O 3 accelerates decomposition when passing through the magnetic flux lines, and in the process of transition to ground state oxygen O 2 , superoxide is generated as shown in formula (3), and further decomposed into active oxygen ( Singlet oxygen, oxygen radical).

(数3)
→O -+O-→O-+O-+O- (3)
(Equation 3)
O 3 → O 2 + O → O + O + O (3)

活性化され、還元力のある水は、この活性酸素と反応して式(4)に示すようにヒドロキシルラジカルOH-を生成する。
これによって、流水は弱アルカリ化し、水と活性酸素による水自身の殺菌が可能になる。
Activated and reducing water reacts with this active oxygen to produce hydroxyl radical OH as shown in formula (4).
As a result, the running water becomes weakly alkaline, and water itself can be sterilized with water and active oxygen.

(数4)
O+O-→2OH- (4)
(Equation 4)
H 2 O + O → 2OH (4)

上記の式中で、
基底状態の酸素
- スーパーオキシド
- 活性酸素(一重項酸素、酸素ラジカル)
OH- ヒドロキシルラジカル
である。
In the above formula,
O 2 ground state oxygen
O 2 - superoxide
O - active oxygen (singlet oxygen, oxygen radicals)
OH - hydroxyl radical.

次に、以上に述べた本発明の水の殺菌装置を具体化した一実施の形態について説明する。この実施の形態は、図2の断面図に示すように、通水管1に注入器2をフランジ9で接続し、通水管1の左右に2対のNd−Fe−B系の永久磁石をN極6とS極7が対向するように配設し、全体を筺体10の中に収容した。   Next, an embodiment embodying the water sterilization apparatus of the present invention described above will be described. In this embodiment, as shown in the cross-sectional view of FIG. 2, an injector 2 is connected to the water pipe 1 with a flange 9, and two pairs of Nd—Fe—B permanent magnets are arranged on the left and right sides of the water pipe 1. The pole 6 and the S pole 7 were disposed so as to face each other, and the whole was accommodated in the housing 10.

この実施例の仕様を表1に示す。なお、通水管1の内径に対して必要な永久磁石8の数が実験によりおおよそ決まっており、通水管1の内径が20mmφの場合で2対、25mmφの場合で3対、40mmφの場合で4対ぐらいが好ましい数である。また、散気板4にも受けられた空気吐出口の径は、細かい方が気泡の径が小さくなって気液混合し易いという面があるが、通過する空気の量が少なくなり、大きいと気泡の径が大きくなって気液混合し難いが、通過する空気量が増えるので、実験的に最適な値に決められる。

Figure 2006198499
Table 1 shows the specifications of this example. The number of permanent magnets 8 required for the inner diameter of the water pipe 1 is roughly determined by experiment, and two pairs when the inner diameter of the water pipe 1 is 20 mmφ, three pairs when 25 mmφ, and four when 40 mmφ. A pair is the preferred number. In addition, the air discharge port received by the diffuser plate 4 has a surface in which the smaller the bubble diameter is, the easier it is for gas-liquid mixing because the bubble diameter is small. Although the bubble diameter becomes large and gas-liquid mixing is difficult, the amount of air passing therethrough increases, so the optimum value is determined experimentally.
Figure 2006198499

図3に、本実施の形態の水の殺菌装置を用いた水の殺菌処理システムの構成を示す。図3に示すシステム構成で水の殺菌処理を行い、殺菌処理結果の水と未処理の水とを対比した。図3の構成では水槽11に未処理の原水12を100l貯水し、内径21.6φのステンレス管13で配管し、途中に設けたポンプ14によってこの原水12を本実施例の水の殺菌装置15に供給してこれを通過させて受水層16に流し込む。本実施例の水の殺菌装置15には別途エアーポンプ17により空気が圧送される。   In FIG. 3, the structure of the water sterilization processing system using the water sterilizer of this Embodiment is shown. Water was sterilized with the system configuration shown in FIG. 3, and the water resulting from the sterilization was compared with untreated water. In the configuration of FIG. 3, 100 l of untreated raw water 12 is stored in a water tank 11, piped with a stainless steel pipe 13 having an inner diameter of 21.6φ, and the raw water 12 is sterilized by a pump 14 provided in the middle of this embodiment. And is passed through the water receiving layer 16. Air is separately pumped by the air pump 17 to the water sterilizer 15 of the present embodiment.

試験は本装置をワンパスした処理水を未処理の原水12と比較して行う。比較した項目はつぎの通りである。
PH(Potential of Hydrogen)
酸化還元電位
一般生菌の数
大腸菌の数
レジオネラ菌の数
The test is performed by comparing the treated water that has passed through this device with the untreated raw water 12. The items compared are as follows.
PH (Potential of Hydrogen)
Redox potential Number of live bacteria Number of E. coli Number of Legionella

処理結果を表2〜表6に示す。

Figure 2006198499
表2から分かるように、本実施例の水の殺菌装置を用いると、PHは原水である水道水の7.1に対して、ワンパス処理で7.9とアルカリ側に変化しており、ヒドロキシルラジカルOH-の発生が高いことを示している。 The processing results are shown in Tables 2 to 6.
Figure 2006198499
As can be seen from Table 2, when the water sterilization apparatus of this example is used, the pH is changed to 7.9 and alkali side by one-pass treatment with respect to 7.1 of tap water which is raw water. This shows that the generation of radical OH is high.

Figure 2006198499
表3から分かるように、本実施例の水の殺菌装置を用いると、酸化還元電位は原水である水道水の272mVから、ワンパス処理で196mVと約72%に低下する。これにより還元力が高まり、ヒドロキシルラジカルOH-の発生が促進されることを示している。
Figure 2006198499
As can be seen from Table 3, when the water sterilization apparatus of this example is used, the oxidation-reduction potential decreases from 272 mV of tap water, which is raw water, to 196 mV and about 72% by one-pass treatment. This indicates that the reducing power is increased and the generation of hydroxyl radical OH is promoted.

Figure 2006198499
表4から分かるように、本実施例の水の殺菌装置を用いると、港湾内の海水中に含まれている一般生菌の数が、1mlあたり520個であったものがワンパス処理で8個と激減している。これにより、本装置の殺菌作用が優れていることが分かる。
Figure 2006198499
As can be seen from Table 4, when the water sterilization apparatus of this example is used, the number of general viable bacteria contained in the seawater in the harbor was 520 per ml, which is 8 by one-pass treatment. It is drastically decreasing. Thereby, it turns out that the bactericidal action of this apparatus is excellent.

Figure 2006198499
表5から分かるように、本実施例の水の殺菌装置を用いると、浄化槽処理水中の大腸菌が本装置でのワンパス処理で完全に陰性になっており、これにより、本装置の殺菌作用が優れていることが分かる。
Figure 2006198499
As can be seen from Table 5, when the water sterilization apparatus of this example is used, Escherichia coli in the septic tank treated water is completely negative in the one-pass treatment in this apparatus, and this makes the sterilization action of this apparatus excellent. I understand that

Figure 2006198499
表6から分かるように、本実施例の水の殺菌装置を用いると、浴槽中にレジオネら菌が、当初100ml中に140cfu(colony forming unit)あったものが、ワンパス処理で検出されなくなっている。これにより、本装置の殺菌効果が非常に高いことが分かる。
Figure 2006198499
As can be seen from Table 6, when the water sterilization apparatus of this example was used, Legione et al. Bacteria in the bathtub were initially not detected by one-pass treatment in 140 cfu (colony forming unit) in 100 ml. . Thereby, it turns out that the bactericidal effect of this apparatus is very high.

以上、本発明を水の殺菌装置の実施例に沿って説明したが、この実施例に限られることなく本発明の主旨を逸脱しない範囲での変更を有する水の殺菌装置もこの発明の対象とするものであり、さらに、この装置で用いられる水の殺菌方法も本発明の対象とするものである。   As mentioned above, although this invention was demonstrated along the Example of the water sterilizer, the water sterilizer which has a change in the range which does not deviate from the main point of this invention without being restricted to this Example is also the object of this invention. Furthermore, the water sterilization method used in this apparatus is also an object of the present invention.

以上に述べたように本発明は水の殺菌する方法とその装置に関し、特に浴用水や公衆浴場、湯沸し温泉、プール、魚介類の養殖場、貯水タンクの水や湯などを、連続的に効果的に殺菌することができるので、水などの液体を殺菌する広い分野での利用の可能性が考えられる。   As described above, the present invention relates to a method and apparatus for sterilizing water, in particular, bath water, public baths, hot water hot springs, pools, seafood farms, water tank water and hot water, etc. Therefore, it can be used in a wide range of fields for sterilizing liquids such as water.

本発明の水の殺菌装置の内部構造を示す一部透視斜視図である。It is a partially transparent perspective view which shows the internal structure of the water sterilizer of this invention. 本発明の水の殺菌装置の一実施の形態の断面図である。It is sectional drawing of one Embodiment of the water sterilizer of this invention. 本発明の水の殺菌装置を用いた水の殺菌処理システムの構成図である。It is a block diagram of the water sterilization processing system using the water sterilizer of this invention.

符号の説明Explanation of symbols

1 通水管
2 注入器(エジェクター)
3 空気又はオゾン
4 散気板
5 気液混合流水
6 永久磁石のN極
7 永久磁石のS極
8 永久磁石
9 フランジ
10 筺体
11 水槽
12 未処理の原水
13 ステンレス管
14 ポンプ
15 水の殺菌装置
16 受水槽
17 エアーポンプ
1 water pipe 2 injector (ejector)
DESCRIPTION OF SYMBOLS 3 Air or ozone 4 Diffuser plate 5 Gas-liquid mixed flowing water 6 N pole of permanent magnet 7 S pole of permanent magnet 8 Permanent magnet 9 Flange 10 Housing 11 Water tank 12 Untreated raw water 13 Stainless steel pipe 14 Pump 15 Water sterilizer 16 Receiving tank 17 Air pump

Claims (3)

空気注入器を用いて空気を注入して気液混合を行った直後の通水管を流れる水を、高密度な磁束線の中を通過させて、前記水を活性化させるとともに前記空気中の酸素を活性化させ、前記水と前記酸素との反応によって生じるOH-(ヒドロキシルラジカル)を用いて殺菌を行うことを特徴とする水の殺菌方法。 The water flowing through the water pipe immediately after performing air-liquid mixing by injecting air using an air injector passes through the high-density magnetic flux lines to activate the water and oxygen in the air And sterilizing using OH (hydroxyl radical) generated by the reaction between the water and oxygen. オゾンを注入して気液混合を行った直後の通水管を流れる水を、高密度な磁束線の中を通過させて、前記オゾンの分解によって生成された活性酸素と前記磁束線によって活性化された前記水との反応によって生じるOH-(ヒドロキシルラジカル)を用いて殺菌を行うことを特徴とする水の殺菌方法。 The water flowing through the water pipe just after ozone injection and gas-liquid mixing passes through the high-density magnetic flux lines, and is activated by the active oxygen generated by the decomposition of the ozone and the magnetic flux lines. A method for sterilizing water, wherein sterilization is performed using OH (hydroxyl radical) generated by the reaction with water. 流水を流す通水管と、前記流水に加圧された空気又はオゾンを注入して気液混合を行う注入器と、前記通水管を隔ててそのN極とS極が対向された少なくとも1対の永久磁石とを具備し、
気液混合された前記流水および前記空気又はオゾンが前記永久磁石から発生される磁束線を直角によぎることによって活性化され、OH-(ヒドロキシルラジカル)を形成して前記流水を殺菌することを特徴とする水の殺菌装置。
A water flow pipe for flowing water, an injector for injecting pressurized air or ozone into the flow water to perform gas-liquid mixing, and at least a pair of N and S poles facing each other across the water pipe A permanent magnet,
The flowing water mixed with gas and liquid and the air or ozone are activated by crossing the magnetic flux lines generated from the permanent magnet at right angles to form OH (hydroxyl radical) to sterilize the flowing water. Water sterilizer.
JP2005011761A 2005-01-19 2005-01-19 Method for sterilizing water and sterilization apparatus Pending JP2006198499A (en)

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Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100778069B1 (en) 2006-08-30 2007-11-29 주식회사 네가트론 Fluid imparting device
WO2008023704A1 (en) * 2006-08-21 2008-02-28 Eiji Matsumura Gas/liquid mixing device
KR101241760B1 (en) 2012-12-21 2013-03-15 주식회사 엘크린시스템 Pasteurization system using generating module of micro bubble
KR101304364B1 (en) * 2009-12-29 2013-09-11 김종석 Water sterilizer using ozone
JP2014010107A (en) * 2012-07-02 2014-01-20 Tadashi Mochizai Method and device for attenuating or eliminating radiation dose of radioactive substance
KR101395160B1 (en) 2013-09-10 2014-05-15 김종석 Dissolved oxygen water manufacturing equipment
KR101398018B1 (en) * 2011-12-30 2014-05-27 (주)버블랜드 Magnetization micro bubbles device for washing machine
WO2016010412A1 (en) * 2014-07-17 2016-01-21 Ser See Seng An apparatus for treating water using magnetic field

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Publication number Priority date Publication date Assignee Title
JPS5284844A (en) * 1975-12-30 1977-07-14 Pincon Andrew J Device of purifying water by means of ozone treatment
JP2000229292A (en) * 1999-02-10 2000-08-22 Ibe:Kk Air and water treating device, air and water treating method and oil and water mixing method
JP2000263062A (en) * 1999-01-12 2000-09-26 Shigemi Sawada Apparatus for producing reformed water, method for producing reformed water, apparatus for producing emulsion fuel, and method for producing emulsion fuel

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5284844A (en) * 1975-12-30 1977-07-14 Pincon Andrew J Device of purifying water by means of ozone treatment
JP2000263062A (en) * 1999-01-12 2000-09-26 Shigemi Sawada Apparatus for producing reformed water, method for producing reformed water, apparatus for producing emulsion fuel, and method for producing emulsion fuel
JP2000229292A (en) * 1999-02-10 2000-08-22 Ibe:Kk Air and water treating device, air and water treating method and oil and water mixing method

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2008023704A1 (en) * 2006-08-21 2008-02-28 Eiji Matsumura Gas/liquid mixing device
KR101122979B1 (en) * 2006-08-21 2012-03-19 노부코 하기와라 Gas/liquid mixing device
CN101516489B (en) * 2006-08-21 2012-07-04 松村荣治 Gas/liquid mixing device
US8403305B2 (en) 2006-08-21 2013-03-26 Eiji Matsumura Gas/liquid mixing device
KR100778069B1 (en) 2006-08-30 2007-11-29 주식회사 네가트론 Fluid imparting device
KR101304364B1 (en) * 2009-12-29 2013-09-11 김종석 Water sterilizer using ozone
KR101398018B1 (en) * 2011-12-30 2014-05-27 (주)버블랜드 Magnetization micro bubbles device for washing machine
JP2014010107A (en) * 2012-07-02 2014-01-20 Tadashi Mochizai Method and device for attenuating or eliminating radiation dose of radioactive substance
KR101241760B1 (en) 2012-12-21 2013-03-15 주식회사 엘크린시스템 Pasteurization system using generating module of micro bubble
KR101395160B1 (en) 2013-09-10 2014-05-15 김종석 Dissolved oxygen water manufacturing equipment
WO2016010412A1 (en) * 2014-07-17 2016-01-21 Ser See Seng An apparatus for treating water using magnetic field

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