JP2006334505A - Water modifying catalyst, water modifying device, and water modifying method, and functional water - Google Patents

Water modifying catalyst, water modifying device, and water modifying method, and functional water Download PDF

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JP2006334505A
JP2006334505A JP2005162037A JP2005162037A JP2006334505A JP 2006334505 A JP2006334505 A JP 2006334505A JP 2005162037 A JP2005162037 A JP 2005162037A JP 2005162037 A JP2005162037 A JP 2005162037A JP 2006334505 A JP2006334505 A JP 2006334505A
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Hiroshi Kurata
大嗣 倉田
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SUNFU KK
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a water modifying catalyst, a water modifying device, and a water modifying method for modifying normal water to water with a low oxidation-reduction potential, and functional water. <P>SOLUTION: The water modifying device 10 modifying normal water to water with a low oxidation-reduction potential consists of a vessel 101 comprising an opening 102 serving as a supply port for supplying flowing water containing minerals, a static electricity generating part 111 generating static electricity by flowing water friction against the flowing water supplied from the opening 102, water modifying catalyst containing parts 112, 113, 114, 115 containing the water modifying catalyst brought into contact with the flowing water passing through the static electricity generating part 111 and comprising magnesium, silicon, iron oxide, and germanium, and an opening 103 serving as a water discharge port discharging the flowing water passing through the water modifying catalyst containing parts 112, 113, 114, 115. <P>COPYRIGHT: (C)2007,JPO&INPIT

Description

本発明は、通常の水を酸化還元電位の低い水に改質する水改質触媒、水改質装置及び水改質方法に関する。そして、このような水改質触媒、水改質装置及び水改質方法によって得られた、通常の水より酸化還元電位が低下した機能性水に関する。   The present invention relates to a water reforming catalyst, a water reforming apparatus, and a water reforming method for reforming ordinary water into water having a low redox potential. The present invention also relates to functional water obtained by such a water reforming catalyst, water reforming apparatus, and water reforming method and having a redox potential lower than that of normal water.

通常の水は、塩化銀電極測定で酸化還元電位が+200mV以上であるが、酸化還元電位が0mV以下の還元水と呼ばれる水がある。このような酸化還元電位が通常より低い水は、通常の水と異なり、様々な特性を示し、特に、生体の健康を維持向上する作用があるとして、近年、盛んに研究されている。   Normal water has a redox potential of +200 mV or higher as measured by a silver chloride electrode, but there is water called reduced water having a redox potential of 0 mV or lower. Recently, water having a lower oxidation-reduction potential than normal water exhibits various characteristics, and has been actively studied in recent years especially as having an effect of maintaining and improving the health of living bodies.

この酸化還元電位の低い水を生成する技術としては、例えば、特許文献1及び特許文献2がある。この特許文献1に開示の技術は、改質する水が導入される電解槽内に第1乃至第3電極を配置し、第1、第2電極間に交流を印加し、第3電極を接地し、第1、第2電極から第3電極に水の整流作用により直流電流を流し、水を電気分解してこの水の酸化還元電位を下げる水改質装置である。また、特許文献2に開示の技術は、酸化体(H、水素イオン)と還元体(OH、水酸化物イオン)の混合状態にある原料水を、シリカ系石英斑岩に金属を担持させた還元触媒と接触させながら、水素をガス圧0.1〜0.95MPaで、10秒〜10分間吹き込んで酸化還元電位が−400mV〜−600mVの水を生成する方法である。このシリカ系石英斑岩に担持させる金属は、例えば、アルカリ金属、マグネシウム、カルシウム、アルミニウム、亜鉛等の電気的陽性の大きい金属、或いは、鉄(II)、スズ(II)、チタン(III)、クロム(II)等の低原子価状態にある金属の塩類である。
特開平05−228475号公報 特開2005−000901号公報
As a technique for generating water having a low oxidation-reduction potential, there are, for example, Patent Document 1 and Patent Document 2. In the technique disclosed in Patent Document 1, first to third electrodes are arranged in an electrolytic cell into which water to be modified is introduced, an alternating current is applied between the first and second electrodes, and the third electrode is grounded. In this water reforming apparatus, a direct current is passed from the first and second electrodes to the third electrode by the rectifying action of water, and water is electrolyzed to lower the redox potential of this water. In addition, the technique disclosed in Patent Document 2 is a method in which raw water in a mixed state of an oxidant (H + , hydrogen ions) and a reductant (OH , hydroxide ions) is supported on a silica-based quartz porphyry. In this method, hydrogen is blown in at a gas pressure of 0.1 to 0.95 MPa for 10 seconds to 10 minutes while being brought into contact with the reduced catalyst, thereby generating water having a redox potential of −400 mV to −600 mV. The metal to be supported on this silica-based quartz porphyry is, for example, an alkali metal, magnesium, calcium, aluminum, zinc or other highly positive metal such as iron (II), tin (II), titanium (III), It is a salt of a metal in a low valence state such as chromium (II).
JP 05-228475 A JP-A-2005-000901

ところで、発明者は、通常の水より酸化還元電位が低下した水(機能性水)を得るべく様々な実験を重ねた結果、新たな技術を開発し、本発明を完成するに至った。   By the way, as a result of repeating various experiments to obtain water (functional water) having a lower oxidation-reduction potential than ordinary water, the inventor has developed a new technique and completed the present invention.

即ち、本発明は、通常の水を機能性水に改質する水改質触媒、水改質装置及び水改質方法を提供することを目的とする。そして、本発明は、このような水改質触媒、水改質装置及び水改質方法によって得られる機能性水を提供することを目的とする。   That is, an object of the present invention is to provide a water reforming catalyst, a water reforming apparatus, and a water reforming method for reforming ordinary water into functional water. And this invention aims at providing the functional water obtained by such a water reforming catalyst, a water reforming apparatus, and a water reforming method.

発明者は、機能性水を得るべく、様々な実験を重ねた結果、実質的にマグネシウム(Mg)とシリコン(Si)と酸化鉄とゲルマニウム(Ge)とを、ミネラルを含む流水に接触させると、接触後の水の酸化還元電位が通常の水より低下していることを見出した。   As a result of repeating various experiments to obtain functional water, the inventor substantially brought magnesium (Mg), silicon (Si), iron oxide, and germanium (Ge) into contact with running water containing minerals. It was found that the redox potential of water after contact was lower than that of normal water.

ここで、酸化鉄は、酸化鉄(II)(FeO)、酸化鉄(III)(Fe)及び酸化鉄(III)鉄(II)(Fe(FeIIFeIII )の何れか1つ又は任意の2以上の組み合わせである。ミネラルとは、一般に、体を構成する諸元素のうち炭素(C)、水素(H)、酸素(O)及び窒素(N)を除いた成分であって、動物にとって必要な無機成分をいい、本発明では、少なくともカルシウム(Ca)及びシリコン(Si)を含み、この他に上記定義に該当する元素(例えばナトリウム(Na)、カリウム(K)、リン(P)及び塩素(Cl)等)を1又は複数含んでもよい。また、通常の水より酸化還元電位が低下した水(機能性水)とは、塩化銀電極測定で、酸化還元電位が+200mVより低い水をいい、還元水とは、上記のように、酸化還元電位が0mV以下の水をいう。 Here, iron oxide is iron oxide (II) (FeO), iron oxide (III) (Fe 2 O 3 ) and iron oxide (III) iron (II) (Fe 3 O 4 (Fe II Fe III 2 O 4). In general, a mineral is carbon (C), hydrogen (H), oxygen (O) and nitrogen (N) among the elements constituting the body. An excluded component, which is an inorganic component necessary for animals. In the present invention, it contains at least calcium (Ca) and silicon (Si), and other elements corresponding to the above definition (for example, sodium (Na), potassium) (K), phosphorus (P), chlorine (Cl), etc.) may be included, and water (functional water) having a lower oxidation-reduction potential than normal water is a silver chloride electrode measurement, Water with a redox potential lower than +200 mV There, the reduced water, as described above, the oxidation-reduction potential refers to the following water 0 mV.

詳細な理由は、今後の研究を待つ必要があるが、本発明者は、次のような現象が生じているものと推察している。   The detailed reason is that it is necessary to wait for future research, but the present inventors speculate that the following phenomenon occurs.

図1は、水改質の様子を模式的に示す図である。図1において、水が流動することによって得られる流水1は、容器2の内壁との流体摩擦により静電気3を発生させる。この静電気3のエネルギーを実質的にマグネシウムとシリコンと酸化鉄とゲルマニウムとから成る触媒(水改質触媒)4が吸収し、水改質触媒4は、エネルギー的に励起する。そして、エネルギー的に励起した水改質触媒4は、エネルギー波動5を放出して流水中に含まれる少なくともカルシウム及びシリコンを含むミネラル6との間で共鳴し、エネルギー波動5の授受を行う。このときに、水分子7のクラスタは、細分化され、さらに、水分子7の一部が酸素と水素とに分解される。酸素は、水中より外部へ出て行くが、水素は、Hの形で水中にしばらくとどまって酸化還元電位を低下させる。特に、水改質触媒のうちゲルマニウムは、約30℃を超えると陰イオンを盛んに発生させるようになるため、約30℃を超える水を用いる場合に、効果的に酸化還元電位を低下させる。 FIG. 1 is a diagram schematically showing the state of water reforming. In FIG. 1, running water 1 obtained by flowing water generates static electricity 3 due to fluid friction with the inner wall of a container 2. The energy of the static electricity 3 is absorbed by a catalyst (water reforming catalyst) 4 substantially composed of magnesium, silicon, iron oxide, and germanium, and the water reforming catalyst 4 is excited energetically. The energy-excited water reforming catalyst 4 releases energy waves 5 and resonates with minerals 6 containing at least calcium and silicon contained in the flowing water, and transfers energy waves 5. At this time, the cluster of water molecules 7 is subdivided, and a part of the water molecules 7 is further decomposed into oxygen and hydrogen. Oxygen goes out of the water, but hydrogen stays in the water for a while in the form of H + to reduce the redox potential. In particular, germanium among water reforming catalysts actively generates anions when the temperature exceeds about 30 ° C., and therefore effectively reduces the redox potential when water exceeding about 30 ° C. is used.

種々の実験結果によって、上述の目的を達成するために、本発明の一態様は、マグネシウムとシリコンと酸化鉄とゲルマニウムとから成り、ミネラルを含む帯電した水に接触することによって通常の水より酸化還元電位が低下した機能性水を生成する水改質触媒である。   According to various experimental results, in order to achieve the above-mentioned object, one embodiment of the present invention is composed of magnesium, silicon, iron oxide, and germanium, and is oxidized more than normal water by contact with charged water containing minerals. It is a water reforming catalyst that generates functional water having a reduced reduction potential.

そして、本発明の他の一態様は、ミネラルを含む流水を供給するための供給口と、前記給水口から供給された流水との流水摩擦により静電気を生成する静電気生成部と、前記静電気生成部を通過した流水に接触する、マグネシウムとシリコンと酸化鉄とゲルマニウムとから成る水改質触媒を内蔵する水改質触媒内蔵部と、前記水改質触媒内蔵部を通過した流水が排水される排水口とを備える容器から成り、通常の水より酸化還元電位が低下した機能性水を生成する水改質装置である。   According to another aspect of the present invention, a supply port for supplying running water containing minerals, a static electricity generating unit that generates static electricity by running water friction with the flowing water supplied from the water supply port, and the static electricity generating unit A water reforming catalyst built-in portion containing a water reforming catalyst made of magnesium, silicon, iron oxide, and germanium, which is in contact with the flowing water passing through the water, and waste water from which the flowing water passed through the water reforming catalyst built-in portion is drained It is a water reformer that is composed of a container having a mouth and generates functional water having a lower oxidation-reduction potential than ordinary water.

また、上述の水改質装置において、ミネラルを含む流水を生成して前記給水口に供給する流水生成部、及び、ミネラルを含む流水を前記給水口に供給する流水供給部のうちの何れか一方をさらに備えることを特徴とする。   Moreover, in the above-described water reforming apparatus, any one of a flowing water generation unit that generates flowing water containing minerals and supplies the flowing water to the water supply port, and a flowing water supply unit that supplies flowing water including minerals to the water supply port. Is further provided.

さらに、これら上述の水改質装置において、前記容器は、絶縁性材料で形成されることを特徴とする。   Furthermore, in these water reforming apparatuses described above, the container is formed of an insulating material.

そして、本発明の他の一態様は、マグネシウムとシリコンと酸化鉄とゲルマニウムとから成る水改質触媒を、ミネラルを含む帯電した水に接触させ、通常の水より酸化還元電位が低下した機能性水を生成する水改質方法である。   In another aspect of the present invention, a water reforming catalyst composed of magnesium, silicon, iron oxide, and germanium is brought into contact with charged water containing minerals, and the redox potential is lower than that of normal water. A water reforming method for producing water.

また、本発明の他の一態様は、マグネシウムとシリコンと酸化鉄とゲルマニウムとから成る水改質触媒をミネラルを含む帯電した水に接触させて生成される通常の水より酸化還元電位が低下した機能性水である。   In another embodiment of the present invention, the redox potential is lower than that of normal water produced by bringing a water reforming catalyst composed of magnesium, silicon, iron oxide, and germanium into contact with charged water containing minerals. Functional water.

さらに、上述の機能性水は、界面活性水、洗浄水、風呂水、溶媒及び消火水の何れか1つであることを特徴とする。   Furthermore, the above-mentioned functional water is any one of surface active water, washing water, bath water, solvent, and fire extinguishing water.

このような水改質触媒、水改質装置及び水改質方法は、通常の水より酸化還元電位が低下した機能性水を生成することができる。そして、この機能性水は、酸化還元電位が低下しているので、通常の水に較べて様々な特性を示し、特に、界面活性水、洗浄水、風呂水、溶媒又は消火水に用いると有効である。   Such a water reforming catalyst, a water reforming apparatus, and a water reforming method can generate functional water having a redox potential lower than that of normal water. Since this functional water has a reduced oxidation-reduction potential, it exhibits various characteristics compared to ordinary water, and is particularly effective when used for surface active water, washing water, bath water, solvent or fire extinguishing water. It is.

以下、本発明に係る実施形態を図面に基づいて説明する。なお、各図において同一の符号を付した構成は、同一の構成であることを示し、その説明を省略する。
(実施の形態)
図2は、水改質装置の外観構成及び内部構成を示す図である。図2(A)は、水改質装置の外観構成を示し、図2(B)は、水改質装置の内部構成を示す断面図である。
Embodiments according to the present invention will be described below with reference to the drawings. In addition, the structure which attached | subjected the same code | symbol in each figure shows that it is the same structure, The description is abbreviate | omitted.
(Embodiment)
FIG. 2 is a diagram illustrating an external configuration and an internal configuration of the water reforming apparatus. 2A shows an external configuration of the water reformer, and FIG. 2B is a cross-sectional view showing an internal configuration of the water reformer.

図2において、水改質装置10は、略円筒形の容器101を備え、容器101の両面には、略円形の開口部102、103が形成されている。そして、容器101の内部には、開口部102から所定間隔を空けて、通水可能にマグネシウムが充填されたマグネシウム充填部112と、通水可能にシリコンが充填されたシリコン充填部113と、通水可能に酸化鉄が充填された酸化鉄充填部114と、通水可能にゲルマニウムが充填されたゲルマニウム充填部115とが形成されている。容器101は、例えばプラスチック等の樹脂製である。   In FIG. 2, the water reforming apparatus 10 includes a substantially cylindrical container 101, and substantially circular openings 102 and 103 are formed on both surfaces of the container 101. Then, inside the container 101, a predetermined interval from the opening 102, a magnesium filling portion 112 filled with magnesium so as to allow water to pass through, and a silicon filling portion 113 filled with silicon so as to allow water to pass therethrough, and An iron oxide filling portion 114 filled with iron oxide so that water can flow and a germanium filling portion 115 filled with germanium so that water can flow through are formed. The container 101 is made of a resin such as plastic.

マグネシウム充填部112、シリコン充填部113、酸化鉄充填部114及びゲルマニウム充填部115には、マグネシウム、シリコン、酸化鉄(本実施形態ではFe)及びゲルマニウムを質量比で50乃至51.7%、49乃至47.7%、0.5乃至0.3%及び0.5乃至0.3%の各割合でそれぞれ充填した。なお、この範囲は、本実施形態における比であり、この範囲を越えても酸化還元電位が低下する効果を確認している。この効果を有する範囲は、鋭意、探求中である。また、流速、水温、容器101の形状等の機能性水を生成する条件、及び、機能性水の用途等に応じてこの比は変わる。 The magnesium filling portion 112, the silicon filling portion 113, the iron oxide filling portion 114, and the germanium filling portion 115 contain magnesium, silicon, iron oxide (Fe 2 O 3 in this embodiment), and germanium in a mass ratio of 50 to 51.7. %, 49 to 47.7%, 0.5 to 0.3% and 0.5 to 0.3%, respectively. This range is the ratio in the present embodiment, and the effect of reducing the oxidation-reduction potential is confirmed even when the range is exceeded. The range having this effect is eagerly under investigation. In addition, this ratio varies depending on conditions for generating functional water such as the flow rate, water temperature, and the shape of the container 101 and the use of the functional water.

このような水改質装置10の開口部102から、ミネラルを含む流水を供給すると、開口部102からマグネシウム充填部112までの空間111で、流水は、容器101の内壁との流体摩擦により静電気を発生させ、帯電する。ここで、ミネラルには、少なくともカルシウム及びシリコンが含まれている。また、流水中のミネラルは、天然水、水道水、及び、市販のナチュラルミネラルウォータやミネラルウォータやナチュラルウォータに含有されている程度の量でよい。そして、帯電した流水は、マグネシウム充填部112、シリコン充填部113、酸化鉄充填部114及びゲルマニウム充填部115をこの順で順次に通過し、開口部103から機能性水となって排水される。   When flowing water containing minerals is supplied from the opening 102 of the water reforming apparatus 10, the flowing water generates static electricity due to fluid friction with the inner wall of the container 101 in the space 111 from the opening 102 to the magnesium filling portion 112. Generate and charge. Here, the mineral contains at least calcium and silicon. Moreover, the quantity of the grade contained in the natural water, a tap water, and the commercially available natural mineral water, mineral water, and natural water may be sufficient as the mineral in running water. The charged flowing water sequentially passes through the magnesium filling portion 112, the silicon filling portion 113, the iron oxide filling portion 114, and the germanium filling portion 115 in this order, and is discharged from the opening 103 as functional water.

開口部102は、ミネラルを含む流水を供給するための供給口の一例であり、容器101の内部の空間111は、流水との流体摩擦により静電気を生成する静電気生成部の一例であり、マグネシウム充填部112、シリコン充填部113、酸化鉄充填部114及びゲルマニウム充填部115は、水改質触媒内蔵部の一例であり、開口部103は、流水が排水される排水口の一例である。   The opening 102 is an example of a supply port for supplying flowing water containing minerals, and the space 111 inside the container 101 is an example of a static electricity generating unit that generates static electricity by fluid friction with the flowing water, and is filled with magnesium. The part 112, the silicon filling part 113, the iron oxide filling part 114, and the germanium filling part 115 are examples of a water reforming catalyst built-in part, and the opening 103 is an example of a drain outlet from which running water is drained.

このような構成の水改質装置10によって生成される機能性水は、活性水素が水中に留まっている間、陰イオン化されているため、改質前の水に較べて表面張力が小さく、界面活性を有した界面活性水となっている。そして、機能性水は、イオン分解を助長するため、洗浄水、風呂水、溶媒及び油火災を消火するための消火水として好適である。   Since the functional water generated by the water reforming apparatus 10 having such a configuration is anionized while the active hydrogen remains in the water, the surface tension is small compared to the water before the reforming, and the interface It is surface active water with activity. And functional water is suitable as fire-fighting water for extinguishing washing water, bath water, a solvent, and an oil fire in order to promote ion decomposition.

次に、このような構成の水改質装置10を用いて通常の水を機能性水に変えた実施例について説明する。
(実施例1)
実施例1では、水改質装置10の給水口としての開口部102と排水口としての開口部103とを管で連通し、この管に水中ポンプを介挿することによって、水が循環するように構成した。水改質装置10の容器101の内容量は、10リットルであり、流速は、1m/sである。このように構成した水改質装置10に兵庫県芦屋市の水道水を用いて、機能性水を生成する実験を行った。その結果を表1及び図3に示す。水道水には、カルシウム及びシリコンの他、殺菌のための微量の塩素等が含まれている。
Next, an embodiment in which normal water is changed to functional water using the water reforming apparatus 10 having such a configuration will be described.
Example 1
In the first embodiment, the opening 102 serving as the water supply port of the water reformer 10 and the opening 103 serving as the drain port are connected by a pipe, and water is circulated by inserting an underwater pump into the pipe. Configured. The internal volume of the container 101 of the water reformer 10 is 10 liters, and the flow rate is 1 m / s. An experiment was conducted to generate functional water using tap water of Ashiya City, Hyogo, for the water reformer 10 configured as described above. The results are shown in Table 1 and FIG. In addition to calcium and silicon, tap water contains a small amount of chlorine for sterilization.

Figure 2006334505
Figure 2006334505

循環させながら水改質装置10に作用させたところ、表1及び図3の特性曲線aから分かるように、酸化還元電位が+550mVの水道水は、10分経過後には酸化還元電位が−150mVの還元水となり、20分経過後には酸化還元電位が−200mVの還元水となり、30分経過後には酸化還元電位が−350mVの還元水となり、そして、40分経過後には酸化還元電位が−352mVの還元水となった。このように水改質装置10に作用させた直後から10分経過までは、比較的急激に酸化還元電位が低下し、30分経過後以降では、それ以上の酸化還元電位の低下があまり見られず、酸化還元電位が略−350mVで維持された。酸化還元電位は、塩化銀電極測定で行った。以下も同様である。   When the water reforming apparatus 10 was operated while circulating, tap water with a redox potential of +550 mV had a redox potential of −150 mV after 10 minutes, as can be seen from the characteristic curve a in Table 1 and FIG. After 20 minutes, the redox potential becomes -200 mV reduced water, after 30 minutes the redox potential becomes -350 mV reduced water, and after 40 minutes, the redox potential becomes -352 mV. It became reduced water. As described above, the oxidation-reduction potential decreases relatively rapidly from 10 minutes after the water reforming apparatus 10 is applied, and after 30 minutes, the oxidation-reduction potential is further decreased. The oxidation-reduction potential was maintained at about -350 mV. The redox potential was measured by silver chloride electrode measurement. The same applies to the following.

以上のように、実質的にマグネシウムとシリコンと酸化鉄とゲルマニウムとから成る水改質触媒を内蔵する水改質装置10に微量のミネラルを含む水道水を通水したところ、その酸化還元電位が低下し、通常の水より酸化還元電位の低い機能性水が得られ、さらに、還元水が得られた。
(実施例2)
次に、容器101の材質を変えて同様の実験を行った。その結果を表2、表3及び図4に示す。表2及び図4に実線で示す特性曲線bは、容器101を絶縁性材料であるプラスチックで形成した場合であり、表3及び図4に一点鎖線で示す特性曲線cは、容器101を導電性材料であるステンレス鋼で形成した場合である。
As described above, when tap water containing a trace amount of mineral is passed through the water reforming apparatus 10 containing a water reforming catalyst substantially composed of magnesium, silicon, iron oxide, and germanium, the oxidation-reduction potential is Functional water having a lower oxidation-reduction potential than normal water was obtained, and further reduced water was obtained.
(Example 2)
Next, the same experiment was performed by changing the material of the container 101. The results are shown in Table 2, Table 3, and FIG. A characteristic curve b indicated by a solid line in Table 2 and FIG. 4 is a case where the container 101 is formed of plastic which is an insulating material, and a characteristic curve c indicated by a one-dot chain line in Table 3 and FIG. In this case, the material is stainless steel.

Figure 2006334505
Figure 2006334505

Figure 2006334505
Figure 2006334505

表2及び図4の特性曲線bから分かるように、容器101を絶縁性材料で形成した場合では、酸化還元電位が+550mVの水道水は、10分経過後には酸化還元電位が−100mVの還元水となり、20分経過後には酸化還元電位が−150mVの還元水となり、30分経過後には酸化還元電位が−200mVの還元水となり、40分経過後には酸化還元電位が−202mVの還元水となった。一方、容器101を導電性材料で形成した場合では、表3及び図4の特性曲線cから分かるように、酸化還元電位が+550mVの水道水は、1時間経過後には酸化還元電位が+200mVとなり、2時間経過後には酸化還元電位が+100mVとなり、3時間経過後には酸化還元電位が+98mVとなった。   As can be seen from the characteristic curve b in Table 2 and FIG. 4, when the container 101 is formed of an insulating material, tap water having a redox potential of +550 mV is reduced water having a redox potential of −100 mV after 10 minutes. After 20 minutes, the redox potential becomes -150 mV reduced water, after 30 minutes the redox potential becomes -200 mV reduced water, and after 40 minutes the redox potential becomes -202 mV reduced water. It was. On the other hand, when the container 101 is made of a conductive material, as can be seen from the characteristic curve c in Table 3 and FIG. 4, tap water with a redox potential of +550 mV becomes a redox potential of +200 mV after 1 hour, After 2 hours, the redox potential was +100 mV, and after 3 hours, the redox potential was +98 mV.

このように容器101を導電性材料で形成した場合では、水道水を水改質装置10に作用させたところ、通常の水より酸化還元電位の低下が見られるが、酸化還元電位が0mV以下に至らなかった。容器101を導電性材料で形成した場合では、容器101を絶縁性材料で形成した場合に較べて、酸化還元電位の低下が小さく、時間もかかっている。   When the container 101 is formed of a conductive material in this way, when the tap water is applied to the water reforming apparatus 10, the oxidation-reduction potential is lower than that of normal water, but the oxidation-reduction potential is 0 mV or less. It did not come. In the case where the container 101 is formed of a conductive material, the reduction in oxidation-reduction potential is small and time is required as compared with the case where the container 101 is formed of an insulating material.

従って、静電気を水改質のエネルギー源にしているものと推察され、水の流体摩擦による静電気が生じ易い絶縁性の容器101で水改質装置10を構成した方が導電性の容器101で水改質装置10を構成した場合に較べて、酸化還元電位の低下度合いや低下に要する時間の点で優れた性能を示す。   Accordingly, it is presumed that static electricity is used as an energy source for water reforming, and the water reforming apparatus 10 is configured by the insulating container 101 that is likely to generate static electricity due to fluid friction of water. Compared with the case where the reformer 10 is configured, the performance is superior in terms of the degree of reduction in the redox potential and the time required for the reduction.

なお、絶縁性材料としては、例えば、プラスチック等の樹脂、及び、土器、陶器や磁器等のセラミックス等を挙げることができる。また、導電性材料としては、例えば、アルミニウム、鉄及び銅等の金属やステンレス鋼等の合金を挙げることができる。   Examples of the insulating material include resins such as plastic and ceramics such as earthenware, earthenware, and porcelain. Examples of the conductive material include metals such as aluminum, iron and copper, and alloys such as stainless steel.

次に、流水生成部や流水供給部を備えた水改質装置の実施形態について説明する。
(他の実施の形態)
図5は、流水生成部を備えた水改質装置の構成を示す図である。図5(A)は、流水生成部として水中ポンプを用いた水改質装置の構成を示す図であり、図5(B)は、流水生成部としてミネラル水貯水槽を用いた水改質装置の構成を示す図である。
Next, an embodiment of a water reforming apparatus including a running water generation unit and a running water supply unit will be described.
(Other embodiments)
FIG. 5 is a diagram illustrating a configuration of a water reforming apparatus including a running water generation unit. FIG. 5A is a diagram showing a configuration of a water reforming apparatus using a submersible pump as a running water generation unit, and FIG. 5B is a water reforming apparatus using a mineral water reservoir as a running water generation unit. FIG.

図5(A)において、水改質装置Aは、ミネラルを含む水を貯留する水槽であるミネラル水貯水槽11と、図2を用いて説明した水改質装置10と同様の構成である水改質部12と、機能性水を貯留する水槽である機能性水貯水槽13と、ミネラル水貯水槽11と水改質部12とを通水可能に連通する管15と、水改質部12と機能性水貯水槽13とを通水可能に連通する管16と、管15に介挿された水中ポンプ14とを備えて構成される。   In FIG. 5A, a water reforming apparatus A is water having the same configuration as the mineral water storage tank 11 which is a water tank for storing water containing minerals and the water reforming apparatus 10 described with reference to FIG. A reforming unit 12, a functional water storage tank 13 that is a water tank for storing functional water, a pipe 15 that allows the mineral water storage tank 11 and the water reforming unit 12 to pass through, and a water reforming unit 12 and the functional water reservoir 13 are configured to include a pipe 16 that allows water to pass therethrough and a submersible pump 14 interposed in the pipe 15.

このような構成の水改質装置Aでは、ミネラル水貯水槽11に貯留されたミネラルを含む水は、水中ポンプが作動することにより水中ポンプ14で流水となって管15を介して水改質部12に送水される。ミネラルを含む流水は、水改質部12で上述したように酸化還元電位が通常の水よりも低下して機能性水となって、管16を介して機能性水貯水槽13に送水され、機能性水貯水槽13で貯留される。このように水中ポンプ14は、ミネラルを含む流水を生成して水改質部12の給水口に供給する流水生成部として機能している。   In the water reforming apparatus A having such a configuration, water containing minerals stored in the mineral water storage tank 11 becomes water flowing through the submersible pump 14 when the submersible pump is operated, and is reformed through the pipe 15. Water is sent to the section 12. As described above, the water containing minerals has a redox potential lower than that of normal water in the water reforming unit 12 to become functional water, and is sent to the functional water storage tank 13 through the pipe 16. It is stored in the functional water reservoir 13. Thus, the submersible pump 14 functions as a flowing water generating unit that generates flowing water containing minerals and supplies it to the water supply port of the water reforming unit 12.

なお、水改質部12における酸化還元電位の低下の度合いは、流水摩擦によって生じる静電気量や、マグネシウム充填部112のマグネシウムとシリコン充填部113のシリコンと酸化鉄充填部114の酸化鉄とゲルマニウム充填部115のゲルマニウムと水が接触する接触面積や、これらと水が作用する作用時間等に応じて変化する。このため、水改質部12に1回通水しただけでは、所望の酸化還元電位が得られない場合もある。このような場合では、水改質部12に複数回通水するために、図5(A)に破線で示すように、機能性水貯水槽13の水をミネラル水貯水槽11へ還流する還流管17をさらに設けてもよく、さらに、必要に応じて水中ポンプ18を設けてもよい。   The degree of reduction of the oxidation-reduction potential in the water reforming unit 12 depends on the amount of static electricity caused by running water friction, the magnesium filling portion 112, the silicon filling portion 113, the silicon filling portion 113, the iron oxide filling and the germanium filling amount. It changes in accordance with the contact area where germanium and water contact the part 115, the action time during which these and water act, and the like. For this reason, a desired oxidation-reduction potential may not be obtained only by passing water through the water reforming unit 12 once. In such a case, in order to pass water through the water reforming unit 12 a plurality of times, as shown by a broken line in FIG. 5A, the water in the functional water reservoir 13 is refluxed to the mineral water reservoir 11. A pipe 17 may be further provided, and a submersible pump 18 may be further provided as necessary.

また、図5(B)において、水改質装置Bは、ミネラルを含む水を貯留する水槽であるミネラル水貯水槽21と、図2を用いて説明した水改質装置10と同様の構成である水改質部22と、機能性水を貯留する水槽である機能性水貯水槽23と、ミネラル水貯水槽21と水改質部22とを通水可能に接続する接続部24と、水改質部22と機能性水貯水槽23とを通水可能に接続する接続部25とを備えて構成され、重量が作用する方向(重力作用方向G)に沿って上から下へ、ミネラル水貯水槽21、接続部24、水改質部22、接続部25及び機能性水貯水槽23の順に配置される。   5B, the water reforming apparatus B has the same configuration as the mineral water storage tank 21 that is a tank for storing water containing minerals and the water reforming apparatus 10 described with reference to FIG. A water reforming unit 22, a functional water storage tank 23 that is a water tank for storing functional water, a connection unit 24 that connects the mineral water storage tank 21 and the water reforming unit 22 so as to allow water to flow, and water Mineral water is provided with a connecting portion 25 that connects the reforming portion 22 and the functional water reservoir 23 so that water can pass through, from the top to the bottom along the direction in which the weight acts (gravity acting direction G). The water storage tank 21, the connection part 24, the water reforming part 22, the connection part 25, and the functional water storage tank 23 are arranged in this order.

接続部24は、例えば、ミネラル水貯水槽21の略円筒形状の排水口の側面外周に形成されたメネジと、水改質部22の略円筒形状の給水口の側面内周に形成されたオネジとで構成することができる。同様に、接続部25は、例えば、水改質部22の略円筒形状の排水口の側面外周に形成されたメネジと、機能性水貯水槽23の略円筒形状の給水口の側面内周に形成されたオネジとで構成することができる。また例えば、接続部24は、ミネラル水貯水槽21の略円筒形状の排水口に形成されたフランジと、水改質部22の略円筒形状の給水口に形成されたフランジとを備え、両フランジをネジ留めすることで構成することができる。同様に、接続部25は、例えば、水改質部22の略円筒形状の排水口に形成されたフランジと、機能性水貯水槽23の略円筒形状の給水口に形成されたフランジとを備え、両フランジをネジ留めすることで構成することができる。   For example, the connecting portion 24 is a female screw formed on the outer periphery of the side surface of the substantially cylindrical drain port of the mineral water reservoir 21 and a male screw formed on the inner surface of the side surface of the substantially cylindrical water supply port of the water reforming unit 22. And can be configured. Similarly, the connecting portion 25 is formed on, for example, the female screw formed on the outer periphery of the substantially cylindrical drainage port of the water reforming unit 22 and the inner periphery of the side surface of the substantially cylindrical water supply port of the functional water reservoir 23. It can be composed of formed male screws. Further, for example, the connecting portion 24 includes a flange formed at the substantially cylindrical drainage port of the mineral water storage tank 21 and a flange formed at the substantially cylindrical water supply port of the water reforming unit 22. It can comprise by screwing. Similarly, the connection unit 25 includes, for example, a flange formed in a substantially cylindrical drain of the water reforming unit 22 and a flange formed in a substantially cylindrical water supply port of the functional water reservoir 23. It can be configured by screwing both flanges.

このような構成の水改質装置Bでは、ミネラル水貯水槽21に貯留されたミネラルを含む水は、自然流下によって流水となって接続部24を介して水改質部22に送水される。ミネラルを含む流水は、水改質部22で上述したように酸化還元電位が通常の水よりも低下して機能性水となって、接続部25を介して機能性水貯水槽23に送水され、機能性水貯水槽23で貯留される。このように水改質部22に対して重力作用方向G上で上の位置に配置されたミネラル水貯水槽21は、ミネラルを含む流水を生成して水改質部22の給水口に供給する流水生成部として機能している。   In the water reforming apparatus B having such a configuration, water containing minerals stored in the mineral water storage tank 21 becomes flowing water by natural flow and is sent to the water reforming unit 22 via the connection unit 24. As described above, the water containing minerals has a redox potential lower than that of normal water in the water reforming unit 22 and becomes functional water, and is fed to the functional water storage tank 23 through the connection unit 25. It is stored in the functional water reservoir 23. As described above, the mineral water reservoir 21 disposed at the upper position in the gravity action direction G with respect to the water reforming unit 22 generates running water containing minerals and supplies it to the water supply port of the water reforming unit 22. It functions as a running water generator.

図6は、流水供給部を備えた水改質装置の構成を示す図である。図6(A)は、水道栓から吐出する流水を利用する場合の水改質装置の構成を示す図であり、図6(B)は、水道管中の流水を利用する場合の水改質装置の構成を示す図である。   FIG. 6 is a diagram illustrating a configuration of a water reforming apparatus including a running water supply unit. FIG. 6 (A) is a diagram showing a configuration of a water reforming apparatus when using running water discharged from a water tap, and FIG. 6 (B) is a water reforming process when using running water in a water pipe. It is a figure which shows the structure of an apparatus.

図6(A)において、水改質装置Cは、図2を用いて説明した水改質装置10と同様の構成である水改質部32であって、その給水口に水道栓31と接続するための水道栓接続部321をさらに備える。水道栓接続部321は、例えば浄水器を水道栓に接続する公知の接続構造を採用することができ、このような接続構造は、例えば、特開平9−14531号公報や特開2001−241074号公報等に多数公開されている。このような構成の水改質装置Cでは、水道栓31が開栓されると、流水の水道水が水道栓接続部321を介して水改質部32に供給され、機能性水となって水改質部32の排水口から吐出される。このように水道栓接続部321は、ミネラルを含む流水を給水口に供給する流水供給部として機能している。   6A, a water reformer C is a water reformer 32 having a configuration similar to that of the water reformer 10 described with reference to FIG. 2, and a water tap 31 is connected to the water supply port. A water tap connection 321 is further provided. The water tap connection part 321 can adopt, for example, a known connection structure for connecting a water purifier to a water tap. Such a connection structure is, for example, Japanese Patent Laid-Open No. 9-14531 and Japanese Patent Laid-Open No. 2001-241074. A large number of publications have been made public. In the water reforming apparatus C having such a configuration, when the tap 31 is opened, running tap water is supplied to the water reforming unit 32 via the tap connection unit 321 and becomes functional water. It is discharged from the drain port of the water reforming unit 32. Thus, the water tap connection part 321 functions as a running water supply part that feeds running water containing minerals to the water supply port.

また、図6(B)において、水改質装置Dは、図2を用いて説明した水改質装置10と同様の構成である水改質部42であって、その給水口及び排水口に水道管41と接続するための水道管接続部421、422をさらに備える。水道管接続部421、422は、例えば、上記接続部24、25の構成を採用し得る。このような構成の水改質装置Dでは、水道管41に介挿され、水道管41中を流れる流水の水道水が水道管接続部421を介して水改質部32に供給され、機能性水となって水道管接続部422を介して水道管41に送水される。このように水道管接続部421は、ミネラルを含む流水を給水口に供給する流水供給部として機能している。なお、水道管41は、導水管、送水管、配水管及び給水管の何れでもよい。   In FIG. 6B, a water reformer D is a water reformer 42 having the same configuration as the water reformer 10 described with reference to FIG. Water pipe connection portions 421 and 422 for connecting to the water pipe 41 are further provided. For the water pipe connecting portions 421 and 422, for example, the configuration of the connecting portions 24 and 25 can be adopted. In the water reforming apparatus D having such a configuration, tap water that is inserted into the water pipe 41 and flows through the water pipe 41 is supplied to the water reforming section 32 through the water pipe connection section 421, and the functionality is improved. Water is supplied to the water pipe 41 via the water pipe connection part 422. Thus, the water pipe connection part 421 functions as a flowing water supply part that supplies flowing water containing minerals to the water supply port. The water pipe 41 may be any of a water conduit, a water supply pipe, a water distribution pipe, and a water supply pipe.

なお、上述の実施形態では、容器101は、円筒形であるが、直方体でも円錐台でもよく、要は、実質的にマグネシウムとシリコンと酸化鉄とゲルマニウムとから成る水改質触媒を内蔵し、一方から他方へ流水が通水し得る形状であればよい。   In the above-described embodiment, the container 101 has a cylindrical shape, but may be a rectangular parallelepiped or a truncated cone. In short, a water reforming catalyst substantially including magnesium, silicon, iron oxide, and germanium is incorporated, Any shape that allows water to flow from one side to the other may be used.

そして、上述では、マグネシウム充填部112、シリコン充填部113、酸化鉄充填部114及びゲルマニウム充填部115を設けることによって、実質的にマグネシウムとシリコンと酸化鉄とゲルマニウムとから成る水改質触媒を容器101に内蔵したが、容器101の内壁をマグネシウムで覆ったマグネシウム被覆部、容器101の内壁をシリコンで覆ったマグネシウム被覆部、容器101の内壁を酸化鉄で覆った酸化鉄被覆部、及び、容器101の内壁をゲルマニウムで覆ったゲルマニウム被覆部を設けることによって、実質的にマグネシウムとシリコンと酸化鉄とゲルマニウムとから成る水改質触媒を容器101に内蔵してもよい。被覆は、容器101の内壁を全て覆ってもよく、一部を覆ってもよい。   In the above description, the water reforming catalyst substantially composed of magnesium, silicon, iron oxide, and germanium is provided in the container by providing the magnesium filling unit 112, the silicon filling unit 113, the iron oxide filling unit 114, and the germanium filling unit 115. 101, a magnesium coating part in which the inner wall of the container 101 is covered with magnesium, a magnesium coating part in which the inner wall of the container 101 is covered with silicon, an iron oxide coating part in which the inner wall of the container 101 is covered with iron oxide, and a container By providing a germanium covering portion in which the inner wall of 101 is covered with germanium, a water reforming catalyst substantially composed of magnesium, silicon, iron oxide, and germanium may be incorporated in the container 101. The covering may cover the entire inner wall of the container 101 or a part thereof.

また、静電気生成部として機能する空間111を省略し、水改質触媒内蔵部として機能するマグネシウム充填部112やシリコン充填部113や酸化鉄充填部114やゲルマニウム充填部115を静電気生成部として兼用してもよい。   Further, the space 111 functioning as a static electricity generation unit is omitted, and the magnesium filling unit 112, the silicon filling unit 113, the iron oxide filling unit 114, and the germanium filling unit 115 functioning as a water reforming catalyst built-in unit are also used as the static electricity generation unit. May be.

さらに、上述の水改質装置10や水改質部12、22、32、42において、図7に示すように、空間111に開口部102から、流水中に混入しているゴミ等の異物を除去するためのフィルタ1111と、ミネラルを吸着して流水中のミネラルを微量にする例えば活性炭等の吸着剤から構成される吸着部1112と、流水中の雑菌を殺して流水を殺菌するためのチタン(Ti)を充填したチタン充填部1113とをさらに備えてもよい。このように構成することで、流水中の異物を取り除き、触媒の不活性化を促す過剰のミネラルを除去し、殺菌した機能性水を得ることができる。   Furthermore, in the water reforming apparatus 10 and the water reforming units 12, 22, 32, and 42, as shown in FIG. 7, foreign substances such as dust mixed in the running water are introduced into the space 111 from the opening 102. A filter 1111 for removing, an adsorbing part 1112 composed of an adsorbent such as activated carbon that adsorbs minerals to make the minerals in running water a trace amount, and titanium for killing miscellaneous bacteria in running water and sterilizing running water You may further provide the titanium filling part 1113 filled with (Ti). By comprising in this way, the foreign material in a running water is removed, the excess mineral which accelerates | stimulates the inactivation of a catalyst can be removed, and the sterilized functional water can be obtained.

そして、図7に破線で示すように、流水及び/又はチタンに紫外線を放射する紫外線光源116を容器101にさらに配設してもよい。例えば、チタン充填部1113の周壁の一部に紫外線光源116を放射方向を容器101内に向けてさらに配設してもよい。このように構成することで紫外線によって直接的に及び/又は光触媒のチタンを介して間接的にさらに効果的に流水を殺菌することができる。   Then, as indicated by a broken line in FIG. 7, an ultraviolet light source 116 that emits ultraviolet light to running water and / or titanium may be further provided in the container 101. For example, an ultraviolet light source 116 may be further disposed on a part of the peripheral wall of the titanium filling portion 1113 with the radiation direction directed into the container 101. By comprising in this way, flowing water can be more effectively sterilized directly by ultraviolet rays and / or indirectly through photocatalyst titanium.

水改質の様子を模式的に示す図である。It is a figure which shows the mode of water reforming typically. 水改質装置の外観構成及び内部構成を示す図である。It is a figure which shows the external appearance structure and internal structure of a water reforming apparatus. 水改質の実験結果を示す図である。It is a figure which shows the experimental result of water reforming. 容器を材質を変えた場合における水改質の実験結果を示す図である。It is a figure which shows the experimental result of the water reforming | change in the case of changing the material of a container. 流水生成部を備えた水改質装置の構成を示す図である。It is a figure which shows the structure of the water reforming apparatus provided with the flowing water production | generation part. 流水供給部を備えた水改質装置の構成を示す図である。It is a figure which shows the structure of the water reforming apparatus provided with the flowing water supply part. 水改質装置の他の内部構造を示す図である。It is a figure which shows the other internal structure of a water reforming apparatus.

符号の説明Explanation of symbols

1 流水 2 容器
3 静電気 4 水改質触媒
5 エネルギー波動 6 ミネラル
7 水分子 10、A、B、C、D、水改質装置
11、21 ミネラル水貯水槽 12、22 水改質部
13、23、32、42 機能性水貯水槽
14 水中ポンプ 15、16 管
24、25 接続部 321 水道栓接続部
421、422 水道管接続部 101 容器
102、103 開口部 111 空間
112 マグネシウム充填部 113 シリコン充填部
114 酸化鉄充填部 115 ゲルマニウム充填部
116 紫外線光源 1111 フィルタ
1112 吸着部 1113 チタン充填部
DESCRIPTION OF SYMBOLS 1 Flowing water 2 Container 3 Static electricity 4 Water reforming catalyst 5 Energy wave 6 Mineral 7 Water molecule 10, A, B, C, D, Water reformer 11, 21 Mineral water storage tank 12, 22 Water reformer 13, 23 , 32, 42 Functional water reservoir 14 Submersible pump 15, 16 Pipes 24, 25 Connection part 321 Water tap connection part 421, 422 Water pipe connection part 101 Container 102, 103 Opening part 111 Space 112 Magnesium filling part 113 Silicon filling part 114 Iron oxide filling part 115 Germanium filling part 116 Ultraviolet light source 1111 Filter 1112 Adsorption part 1113 Titanium filling part

Claims (7)

マグネシウムとシリコンと酸化鉄とゲルマニウムとから成り、ミネラルを含む帯電した水に接触することによって通常の水より酸化還元電位が低下した機能性水を生成する水改質触媒。   A water reforming catalyst that is composed of magnesium, silicon, iron oxide, and germanium, and that generates functional water having a reduced redox potential compared to normal water by contacting charged water containing minerals. ミネラルを含む流水を供給するための供給口と、
前記給水口から供給された流水との流水摩擦により静電気を生成する静電気生成部と、
前記静電気生成部を通過した流水に接触する、マグネシウムとシリコンと酸化鉄とゲルマニウムとから成る水改質触媒を内蔵する水改質触媒内蔵部と、
前記水改質触媒内蔵部を通過した流水が排水される排水口とを備える容器から成り、通常の水より酸化還元電位が低下した機能性水を生成する水改質装置。
A supply port for supplying running water containing minerals;
A static electricity generating unit that generates static electricity by running water friction with running water supplied from the water supply port;
A water reforming catalyst built-in portion containing a water reforming catalyst made of magnesium, silicon, iron oxide, and germanium, which is in contact with flowing water that has passed through the static electricity generation unit;
A water reforming apparatus comprising a container provided with a drain port through which flowing water that has passed through the water reforming catalyst built-in portion is drained, and that generates functional water having a lower oxidation-reduction potential than normal water.
ミネラルを含む流水を生成して前記給水口に供給する流水生成部、及び、ミネラルを含む流水を前記給水口に供給する流水供給部のうちの何れか一方をさらに備えること
を特徴とする請求項2に記載の水改質装置。
The water supply production | generation part which produces | generates the flowing water containing a mineral, and supplies it to the said water supply port, The flowing water supply part which supplies the water supply containing a mineral to the said water supply port is further provided. 2. The water reforming apparatus according to 2.
前記容器は、絶縁性材料で形成されること
を特徴とする請求項2又は請求項3に記載の水改質装置。
The water reformer according to claim 2 or 3, wherein the container is formed of an insulating material.
マグネシウムとシリコンと酸化鉄とゲルマニウムとから成る水改質触媒を、ミネラルを含む帯電した水に接触させ、通常の水より酸化還元電位が低下した機能性水を生成する水改質方法。   A water reforming method in which a water reforming catalyst composed of magnesium, silicon, iron oxide, and germanium is brought into contact with charged water containing minerals to generate functional water having a lower redox potential than normal water. マグネシウムとシリコンと酸化鉄とゲルマニウムとから成る水改質触媒をミネラルを含む帯電した水に接触させて生成される通常の水より酸化還元電位が低下した機能性水。   Functional water with a redox potential lower than that of normal water produced by bringing a water reforming catalyst comprising magnesium, silicon, iron oxide and germanium into contact with charged water containing minerals. 前記機能性水は、界面活性水、洗浄水、風呂水、溶媒及び消火水の何れか1つであることを特徴とする請求項6に記載の機能性水。   The functional water according to claim 6, wherein the functional water is any one of surface active water, washing water, bath water, a solvent, and fire extinguishing water.
JP2005162037A 2005-06-01 2005-06-01 Water modifying catalyst, water modifying device, and water modifying method, and functional water Revoked JP2006334505A (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101049762B1 (en) * 2010-06-29 2011-07-19 동양워터테크(주) Maintain water quality devices using electrostatic field generator
JP2014104455A (en) * 2012-11-30 2014-06-09 Hiroshi Ota Vessel having hydrogen generating function, and hydrogen addition method
JP5966138B1 (en) * 2015-10-13 2016-08-10 竹内 忠司 Enzyme hot bath
JP2018513016A (en) * 2015-05-12 2018-05-24 景煥粒子能科技発展有限公司 Composite material, preparation method and apparatus for preparing particle energy multifunctional active water

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6090095A (en) * 1983-10-24 1985-05-21 Katsujiro Ito Activated mineral stone
JPS6168192A (en) * 1984-09-11 1986-04-08 Masaharu Tatsumi Water cleaning device
JPH0324190A (en) * 1989-06-22 1991-02-01 Keisuke Matsuo Preservative
JP2001152129A (en) * 1999-11-22 2001-06-05 Chitoshi Fujiwara Mineral powder composition
JP2002301481A (en) * 2001-04-05 2002-10-15 Araki Komuten:Kk Active water making method and apparatus therefor
JP2003024956A (en) * 2001-07-17 2003-01-28 Norihiro Okumura Method for producing alkaline ionic water and water modifying device
JP2005013925A (en) * 2003-06-27 2005-01-20 Ikuko Uragami Reduced water generation member

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6090095A (en) * 1983-10-24 1985-05-21 Katsujiro Ito Activated mineral stone
JPS6168192A (en) * 1984-09-11 1986-04-08 Masaharu Tatsumi Water cleaning device
JPH0324190A (en) * 1989-06-22 1991-02-01 Keisuke Matsuo Preservative
JP2001152129A (en) * 1999-11-22 2001-06-05 Chitoshi Fujiwara Mineral powder composition
JP2002301481A (en) * 2001-04-05 2002-10-15 Araki Komuten:Kk Active water making method and apparatus therefor
JP2003024956A (en) * 2001-07-17 2003-01-28 Norihiro Okumura Method for producing alkaline ionic water and water modifying device
JP2005013925A (en) * 2003-06-27 2005-01-20 Ikuko Uragami Reduced water generation member

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101049762B1 (en) * 2010-06-29 2011-07-19 동양워터테크(주) Maintain water quality devices using electrostatic field generator
JP2014104455A (en) * 2012-11-30 2014-06-09 Hiroshi Ota Vessel having hydrogen generating function, and hydrogen addition method
JP2018513016A (en) * 2015-05-12 2018-05-24 景煥粒子能科技発展有限公司 Composite material, preparation method and apparatus for preparing particle energy multifunctional active water
US10266435B2 (en) 2015-05-12 2019-04-23 Jinghuan Particle Energy Technology Development Co., Ltd. Composite material, method and device for preparing particle-energy multifunctional active water
JP5966138B1 (en) * 2015-10-13 2016-08-10 竹内 忠司 Enzyme hot bath

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