JP2001259638A - Electronic water treating method - Google Patents

Abstract

PROBLEM TO BE SOLVED: To eliminate flaws of a conventional water treating method by simultaneously proceeding a magnetic force work by a coil and an electrolytic work by an electrode at a simultaneous time with an injection of gaseous ozone. SOLUTION: This electronic water treating method is a method simultaneously performing an oxidizing process of ion molecules being in a resonance relation with resonance magnetic force energy of the coil arranged in water by injecting the gaseous ozone in the water, a process for making a molecule group bonded to water molecules small by the magnetic force energy of the coil arranged in the water, and a process for electrolyzing the water molecules by electrolytic energy generating from the electrode arranged in the water. Also in this electronic water treating method a process for stopping supply of the gaseous ozone in the middle of the process, injecting air into the water and accelerating decomposition of dissolved ozone by the magnetic force of the coil, and a process for dissipating the dissolved ozone by electrolysis energy generating from the electrode and reorganizing a hydrogen bond, are added.

Description

DETAILED DESCRIPTION OF THE INVENTION

[0001]

BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for improving the function of drinking water, medical processing water, agricultural processing water, or for purifying agricultural wastewater, industrial wastewater, domestic wastewater, and the like. Things.

[0002]

2. Description of the Related Art Water treatment by magnetic force began in 1945 with the Belgian patent on reducing descaling, and has been put to practical use mainly in Russia. It promotes the growth of vegetables such as tomatoes, cucumber, soybeans, and peas, and promotes harvesting. It is reported that the results include a 40% increase, an increase in the fluidity of the concrete kneaded material, and an improvement in the dyeing yield of the fabric. Also in Japan, the invention of Japanese Patent Application Laid-Open No. 10-296266 has been proposed as a fluid activation processing apparatus. However, there is a problem that the action is weak with the energy of the magnetic force alone, and reproducibility cannot always be obtained.

[0003] Japanese Patent Application Laid-Open No. 5-2 / 1993 discloses water treatment by electrolysis
No. 28474 and the invention of JP-A-5-111690 have been proposed. This method is a water reforming method in which a DC pulse voltage is applied to an electrode arranged in water, and an oxidation-reduction potential is controlled by an electrolysis action to aggregate organic and inorganic substances in the water. In this method, the quality of the treated water is improved so as to be incomparable to the treatment by magnetic force. However, this method also has a problem that the treatment efficiency is reduced depending on the water quality due to the influence of metal ions and the like.

Although the direction of the treatment is different, the invention of Japanese Patent Application Laid-Open No. H11-90420 has been proposed as a liquid treatment system. In this method, after separation of suspended matter by microwave, flocculation by ultrasonic wave, deodorization by electromagnetic wave, decolorization and sterilization by ozone, sterilization, and adsorption of aggregate by magnetic force to reform water. Although this processing method has a very high processing capacity, the apparatus becomes large due to batch processing,
There is a problem that it is difficult to reduce a series of processing time.

[0005]

The prior arts have been effective, but not sufficiently satisfactory. Since it tries to change the characteristics of water by giving weak energy from the outside to much energy existing in water, it cannot be said that the energy to be given always takes precedence over existing energy. Therefore, there was a drawback that the best results were not always obtained. In addition, since a plurality of combinations are batch-processed, there is a disadvantage that the processing time is not shortened by the cooperative action even if each of them shows a good action alone.

Accordingly, the present invention has focused on a force that is said to act on water molecules. Water is a small molecule with a molecular weight of 18, but its Coulomb force, the force acting between charged ions, the London-Van der Waals force, which acts between all molecules and attracts each other, and the hydrogen bonding force. It is said to be working. It is said that hydrogen bonding is an important force that determines the properties of water and aqueous solutions. The present invention provides a novel water electronic treatment method which solves the conventional drawbacks by exhibiting a cooperative action by simultaneously performing a magnetic action by a coil and an electrolysis action by an electrode at the same time as the injection of ozone. With the goal.

[0007]

In order to achieve the above object, the present invention is directed to a first aspect of the present invention, in which an ozone gas is injected into water and a resonance relation is established between the resonance magnetic energy of a coil disposed in the water and the coil. A step of oxidizing certain ionic molecules, a step of reducing the molecular population bound to the water molecules by magnetic energy of a coil placed in water, and a step of electrolyzing water molecules by electrolysis energy generated from an electrode placed in water Is performed simultaneously, and the respective steps are performed uniformly and promptly by the circulation of water accompanying the floating of the bubbles of the ozone gas.

According to the present invention, by injecting ozone gas into water and imparting a resonance frequency to the separated ionic molecules in a coil in the water, the ionic molecules having a resonance relationship become Coulomb forces, that is, the ions having electric charges. The force acting between them is weakened and easily affected by ozone, and the charge balance between ions is lost, causing oxidation.

Further, water is vibrated at high speed by magnetic field lines generated by the magnetic energy of the coil, and a large molecular mass which is bonded by a hydrogen-bond and a London-van der Waals force which works between all molecules and attracts each other. Cut into molecular populations.

Further, by electrolyzing water molecules by electrolysis energy generated from electrodes placed in water,
In the vicinity of the anode, oxygen gas and hydrogen ions are generated and negatively charged substances in the water, such as hypochlorite ion, carbonate ion, and sulfite ion, gather, and near the cathode, hydrogen gas and hydroxide ions are collected. Generated and positively charged substances, such as sodium ions, potassium ions,
Calcium ions and positively charged light metals and heavy metal ions gather. Therefore, molecular bonds are broken, chlorine gas, carbon dioxide gas, and sulfur dioxide gas are released into the air, and harmful metals are separated, thereby improving the purity of water and relatively reducing the redox potential. I do.

As described above, by performing the respective processes which are excellent at the same time, the ion reaction by the resonance magnetic force and ozone, the ion reaction by the electrolysis, the cutting of the molecular group by the lines of magnetic force, the cutting of the molecular bond by the electrolysis, and the like. Processing is performed with each common item emphasized. Since this water treatment method does not include a step of decomposing ozone dissolved in water, the treatment time can be shortened, and is an electronic treatment method for water mainly used for wastewater treatment.

Next, the electronic treatment method of water according to claim 2 is a step of injecting ozone gas into water to oxidize ion molecules having a resonance relationship with a resonance magnetic energy of a coil arranged in the water. The process of reducing the molecular group bound to the water molecules by the magnetic energy of the arranged coil and the process of electrolyzing the water molecules by the electrolysis energy generated from the electrodes arranged in the water are performed simultaneously, and the supply of ozone gas during the process The process of stopping dissolved ozone by injecting air into the water to promote the decomposition of dissolved ozone by the magnetic energy of the coil placed in the water, and extinguishing the dissolved ozone by the electrolysis energy generated from the electrode placed in the water A step of reorganizing the connection is added, and each step is evenly and quickly performed by the circulation of water accompanying the floating of air bubbles. An electronic processing method of the water and performing.

According to the present invention, the oxidizing of the ion molecules, the cutting of the water molecule group, and the electrolysis of water are simultaneously performed, the supply of ozone gas is stopped, and air is injected into the water during the process. By continuing to cut molecular groups and continue electrolysis, water is vibrated at high speed by magnetic field lines generated by magnetic energy, excess oxygen atoms are separated from oxygen molecules, and the decomposition of dissolved ozone is promoted. It adds to the elimination of ozone and the reorganization of hydrogen bonds. Thereby, the reforming of water is performed simultaneously by one device.

Since the invention of claim 2 includes a process of decomposing ozone dissolved in water, it can be applied to a strict water treatment which dislikes a secondary ozone reaction such as processing water for drinking and processing water for medical treatment. It is a suitable water electronic treatment method.

In the above-described electronic treatment method for water according to the first and second aspects, the ion molecules having a resonance relationship with the magnetic energy of the coil exert Coulomb force, that is, the force acting between charged ions. Since it is weakened and easily oxidized under the influence of ozone, the charge balance between the ions is lost, some of the ions of the components are lost. Therefore, it cannot return to the original state when recombining, and if it is bonded to ions of other components existing in water or if there is no ion that can be bonded, it separates and precipitates. The desired hydrogen bond is controlled using this reaction. In the non-resonant component, the molecular cluster (cluster) becomes smaller due to the London-van der Waals force, but the property of water does not change because it is not affected by the Coulomb force.

In addition, the fundamental energy, the modulation frequency, and the DC energy alone or selectively, and the electronic energy of the composite component are selectively applied from the coil and the electrode. Can efficiently act on both long and short molecules.
Further, by generating an appropriate composite waveform, the potential of the electrode can be changed and the scale can be prevented from adhering to the electrode, so that the processing capacity does not decrease.

According to the first and second aspects of the present invention, the ozone gas, the electrolysis energy, and the magnetic energy can be generated by the floating action of the bubbles of the ozone gas and the convection of the water by the floating action of the bubbles. Since each action does not cause unevenness and each action is performed in a coordinated manner, rapid electronic treatment of water can be performed.

[0018]

DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Next, an embodiment of the present invention will be described with reference to FIGS.
This will be described in detail with reference to FIG. FIG. 1 is a perspective view showing an embodiment of an apparatus used in the electronic water treatment method of the present invention. FIG. 2 is a block diagram of an electronic circuit in a control unit of the apparatus used for the electronic water treatment method shown in FIG. FIG. 3 is a cross-sectional view of the energy radiation unit of the device used in the electronic water treatment method shown in FIG. FIG. 4 shows a connection diagram of coils and electrodes in the energy radiation unit shown in FIG.

The control unit 1 shown in FIG. 1 houses the electronic circuit shown in FIG. The operation panel of the control unit 1 includes a basic frequency variable knob 2, a modulation frequency variable knob 3, a basic frequency display 4, a modulation frequency display 5, a DC applied voltage variable knob 6, an output display 7, and a processing time variable knob. 8, an operation display lamp 9, a timer operation start switch 10, and a power switch 11 are provided. The rear panel of the control unit 1 has an air supply hose 1
2, an intake hose 13, an output terminal 14, and a fuse 15.
Are wired. The knob 2.3.6.8 is connected to a resistor or a capacitor having the same number.

The frequency selected by the fundamental frequency variable knob 2 is generated by a fundamental frequency transmitter 17, amplified by a buffer amplifier 18, processed by a prescaler 19, sent to a counter 20, digitized, and displayed as a fundamental frequency. It is digitally displayed by the device 4. Modulation frequency variable knob 3
The frequency selected in is also processed in the same way as the fundamental frequency,
The data is digitally displayed by the modulation frequency display 5 via the modulation frequency transmitter 21, the buffer amplifier 22, the prescaler 23, and the counter 24. Since the modulation frequency transmitter 21 is provided with a transmitter similar to the basic frequency transmitter 17 and a separate modulator, the signal generated by the basic frequency transmitter 17 and the transmission within the modulation frequency transmitter 21 are transmitted. The signal obtained by the device can be synthesized by the modulator,
It is possible to obtain respective single frequencies and composite frequencies.

In the power amplifier 25, the modulation frequency transmitter 2
1 and amplifies the output signal and mixes the voltage selected by the DC applied voltage variable knob 6. The output display 7 displays only the mixed DC component. The signals obtained here are the frequency from the fundamental frequency transmitter 17, the frequency from the modulation frequency transmitter 21, the modulation combined frequency, the DC voltage,
A variety of signals including the frequency + DC voltage from the fundamental frequency transmitter 17, the frequency + DC voltage from the modulation frequency transmitter 21, and the modulation combined frequency + DC voltage are transmitted to the power transmission cord 16 connected to the output terminal 14. Can be

The variable processing time knob 8 can select a time within a range of 30 minutes to 60 minutes, and when the timer operation start switch 10 is pressed, the timer 26 operates. afterwards,
The operation of the timer 26 is stopped according to the set value of the processing time variable knob 8. At this time, the operation indicator lamp 9 indicates that the timer 26 is operating. In conjunction with the operation of the timer 26, the fundamental frequency transmitter 17, the modulation frequency transmitter 2
1. Power amplifier 25, air supply pump 27, intake pump 2
8. Ozone generator 29 is individually controlled.

The power switch 11 connects the power of 100 V AC supplied from the power plug 30 to the power circuit 31 via the fuse 15. The power supply circuit 31 generates a necessary voltage in the electronic circuit and supplies it to each circuit in the electronic circuit.

The air supply pump 27 is an air source that circulates water in the water container 32. When the ozone generator 29 is in operation, it sends out ozone gas to the air supply hose 12, generates ozone gas from the air stone 33, and generates ozone water. make. Also,
When the ozone generator 29 is stopped, air is sent to the air stone 33.

The suction pump 28 is provided for the purpose of preventing the ozone gas or air sent from the air pump 27 from increasing the pressure inside the water container 32 and leaking the ozone gas or air from the contact surface with the container lid 34. The operation of introducing undissolved ozone gas or air accumulated in the upper portion of the water container 32 into the ozone killer 35 via the intake hose 13 is performed.

FIG. 3 is a sectional view of the energy radiation unit. The energy radiating unit includes an inner container 38 having a coil 36 and an electrode 37 therein, a nipple 39 for relaying air sent from the air supply hose 12 to an air stone 33 located at the bottom of the inner container 38, Container 3
2, a nipple 40 of an intake hose 13 for inhaling ozone gas or air, an electric power delivery cord 16, and a coil 3.
6, a container lid 34 to which a terminal 41 for relaying the electrode 37 is attached, and a water container 32 in which the container lid 34 is fitted airtightly.

When the ozone gas or air is sent from the air supply hose 12 to the air stone 33, fine bubbles of the ozone gas or air are generated from the air stone 33, and the water in the inner container 38 is released by the air lift into the upper opening. At the same time, an amount of water that flows out of the container 42 through the opening 43 provided at the bottom of the inner container 38 flows into the inner container 38, and the water is stirred.

FIG. 4 shows a difference in connection between the coil 36 and the electrode 37 in the energy radiation unit. FIG.
4A is mainly used in a low frequency band, and the parallel connection 45 in FIG. 4B is mainly used in a high frequency band.

Next, the operation and action of the electronic water treatment method of the present invention will be described along the flow. First, a commercial power supply is obtained from the power plug 30 shown in FIG. A predetermined amount of water is put in the water container 32, and the container lid 34 is closed. Here power switch 1
When 1 is turned on, the current set frequency is displayed on the fundamental frequency display 4 and the modulation frequency display 5. The basic frequency variable knob 2 sets the frequency of the processing function originally intended. The modulation frequency variable knob 3 sets a frequency for enhancing the processing function of the fundamental frequency, or sets a frequency having a plurality of processing functions for another purpose. Next, when the timer operation start switch 10 is pressed, all the circuits start operating. Finally, the DC applied voltage variable knob 6 is used to set the intensity of the energy that causes the electrode 37 to perform an electrolysis action according to the value displayed on the output display 7.

In the first half of the timer operation, the ozone generator 29
Operates, and the ozone gas becomes fine bubbles from the air stone 33 and dissolves in the water. There is a lot of energy in water. When molecules that exist in the form of ions bind or leave, they absorb and release energy.

The energy reaction due to ions temporarily responds to the weak energy given from the outside, but returns to the original state over time when the supply of energy is stopped. For example, salt crystals are shaped like stacked dice. Positively charged sodium ions and negatively charged chlorine ions are regularly and alternately located at each apex of the die. In this case, an attractive force acts between the sodium ions and the chloride ions, and a repulsive force acts between the sodium ions and the chlorine ions, which is called the Coulomb force. Coulomb force is the force acting between charged ions.

Therefore, by imparting a resonant frequency to the separated ion molecules to the coil 36, Coulomb force, that is, the force acting between charged ions, is weakened, and the ion molecules are easily affected by ozone. As a result, the charge balance between ions is lost and oxidation occurs, so that some ions of the component are lost. Therefore, it cannot return to the original state when recombining, and if it is bonded to ions of other components present in water or if there is no bondable ion, it separates and precipitates. The desired hydrogen bond is controlled using this reaction. In the non-resonant component, the molecular cluster (cluster) is reduced by the London-van der Waals force, but is not affected by the Coulomb force, so that there is no change in the properties of water. In addition, the action of ozone is caused by the air lift effect of the air bubbles generated from the air stone 33, whereby water can flow and processing can be performed quickly and uniformly.

At the same time as the release of the ozone gas, the coil 36 and the electrode 37 also operate. Water molecules have a positive charge and a negative charge that are separated from each other, so that a dipolar attractive force acts between polar molecules. In addition, a molecule such as methane is a nonpolar molecule because positive and negative charges are not separated, and does not exert an internal attractive force.

However, since the London-Van der Waals force has been proved to work between polar molecules and between polar and non-polar molecules, this attractive force acts on all molecules. . The range of action is said to be about three times the diameter of the molecule, and if it is further apart, the attractive force will be lost. At this time, the power amplifier 2
The coil 36 generates magnetic lines of force in response to the AC signal sent from 5 to give vibration to the water, thereby causing the water to resonate. Therefore, the fact that a plurality of waveform signals can be synthesized by providing a modulation circuit can easily exert an effect even on a molecular group that is complexly coupled to water molecules.

The operation so far corresponds to the first aspect of the present invention. Since the treated water obtained by this treatment contains dissolved ozone, it is not suitable for drinking water or medical treatment water. When used for purification of agricultural wastewater, industrial wastewater, domestic wastewater, etc., the processing time can be greatly reduced. Also, when water is given to plants just before treatment, the effect of dissolved ozone increases the oxygen coefficient, and the partially deficient ions combine with the ions required for carbon assimilation to promote leaf growth. Was done.

In the latter half of the timer operation, the ozone generator 29
Is stopped, and only air is discharged from the air stone 33. Also in this time zone, bubbles of oxygen and hydrogen are generated by the electrolysis effect of the electrode 37. In the first half, the electric current for electrolysis to the electrode 37 was suppressed by the influence of excess oxygen atoms of ozone. However, when the ozone generator 29 was stopped, the influence of ozone gradually weakened and the electric current was recovered. Further, since hydrogen generated by electrolysis easily reacts with excess oxygen atoms, dissolved ozone is reduced, and the process proceeds rapidly in the direction of ozone annihilation.

As the action of ozone is weakened, the ion molecules of the components having a resonance relationship with the AC signal sent from the power amplifier 25 are disturbed by the influence of ozone, disturbing the charge balance between the ions, and being oxidized. Cannot be recombined to its original state because some of the ions are missing, and can be combined with the ions of other components present in the water or separated and precipitated if there are no ions that can be combined .

The desired hydrogen bond is controlled using this reaction. In addition, components that are not in a resonance relationship have a smaller molecular population (cluster) due to the London-van der Waals force, but are not affected by the Coulomb force. Return to the state. Therefore, there is no change in the properties of water. Thus, the presence of components that are selectively recombined and components that are not recombined can change the nature of water.

The operation so far corresponds to the second aspect of the present invention. Since the treated water obtained by this treatment does not contain dissolved ozone, it can be used as a drinking water or a medical water. This is a water treatment method suitable for strict water treatment that dislikes a secondary ozone reaction.

In order to perform the above operation efficiently, an energy radiating unit mechanism as shown in FIG. 3 was employed. Air supply hose 12
When the ozone gas is further fed, fine bubbles are generated from the air stone 33, and the ozone gas dissolves in the water to generate ozone water. At this time, the ozone gas that could not be dissolved in the water accumulates in the upper part of the container. In order to prevent the accumulated ozone gas from leaking out of the container, an intake pump 28 having the same capacity as the air supply pump 27 is operated, and the ozone is decomposed by the ozone killer 35 via the intake hose 13 so that the ozone is decomposed into the atmosphere. Releases air that does not contain ozone gas.

Since the air stone 33 is in the water, the air lift is generated by the rise of the air bubbles, and a flow of the water is created.
The water in the inner container 38 flows out of the inner container 38 through the upper opening 42 by the air lift. In addition, an amount equal to the amount that flows out flows into the inner container 38 through the opening 43 at the bottom of the inner container 38. Water inside inner container 38 and inner container 3
8 circulates, the air stone 33
Since the ozone energy action generated from the water, the electrolysis energy action generated by the electrode 37, and the magnetic energy action generated by the coil 36 are connected by a water circulation line, the respective processes are performed simultaneously.

In the sectional view of the energy radiation unit in FIG. 3, the electrode 37 and the coil 36 are connected in series 44 in FIG. 4, but they may be operated in parallel connection 45 in FIG. When power is input to the coil and the electrode, they operate as L and C. In the operation of the series connection 44, the DC power is supplied to the electrode 3
7, only the AC component acts on the coil 36, so that the electrolysis effect at the electrode 37 can be set to the maximum and is suitable for use in the DC to low frequency band. Also,
In the case of the parallel connection 45, since direct current power is applied to the coil 36, the coil 36 is considered to have a low resistance in terms of direct current. Since the power is suppressed in consideration of heat generation,
It is suitable for use in high-frequency bands where power can be efficiently converted to energy by coils to keep the processing capacity constant.

According to the embodiment of the present invention, the fundamental frequency 8
When the growth of mature ferns was confirmed with water treated by the treatment method of claim 1 at 0HZ, modulation frequency of 61 KHZ, and DC applied voltage at a medium level, the growth coefficient of roots increased and the size of leaves increased by 30%. It has been recognized that the number has increased. Normally, in potted plants, the growth of roots is suppressed by the size of the pot, so the overall size is determined by the size of the pot. However, in the treated water according to the present invention, since the characteristics of the water are changed due to the improvement of the oxygen coefficient and the change of the hydrogen bond, the roots can be densely packed under the same conditions.

Further, when the cloth is dyed with water treated by the treatment method of claim 1 at a fundamental frequency of 430 Hz, no modulation frequency, and a high level of DC applied voltage, the dye reacts with ions present on the surface of the fiber. The dyeing properties are improved, the adsorption speed is increased, the color unevenness is less likely to occur, and the dyeing yield is improved. This is a result of the fact that the state of the ion of the dye reacts quickly with the ion of the fiber and the state of the ion that inhibits the reaction has been eliminated.

A yellow-brown suspended matter was confirmed in the water treated by the treatment method of claim 2 at a fundamental frequency of 430 HZ, a modulation frequency of 61 KHZ, and a high level of a DC applied voltage, and was analyzed by atomic absorption spectrometry. As a result, a large amount of iron oxide was detected. In order to oxidize iron in water to this level by the ozone reaction alone, 1 g / h or more of ozone gas is necessary. However, in the present invention, since only about 100 mg / h of ozone gas is generated, the line of magnetic force at the set frequency is This is the result of weakening Coulomb's power in response to the molecular level.

Further, after the water treated by the treatment method of claim 1 at a fundamental frequency of 100 HZ, a modulation frequency of 37 KHZ, and a medium level of DC applied voltage was left for one day, it was used as water for diluting the leaf spray liquid of tea cultivation. As a result, the leaf thickness increased and the outer shape grew significantly, resulting in an increase in sales of about 20% compared to normal production. This is a result of enhancing the ionic activity of the foliar spray solution under the influence of the magnetic field lines at the set frequency and increasing the absorption rate of tea leaves to cells in order to finely structure the molecular population (cluster).

[0047]

As described above, according to the present invention,
By setting the transmission frequency, modulation frequency, and DC voltage, electrons are transferred by the particularly stable magnetic action and electrolysis action linked to the ozone action, so that water can be easily and efficiently reproducible. Electronic processing.

Since all the processing items of the conventional apparatus are included, the functions of the processing water for drinking, the processing water for medical treatment, and the processing water for agriculture can be achieved by one apparatus. Treatment such as purification of domestic wastewater is also possible. Therefore, there is no need to install a plurality of devices, which is extremely economical.

[Brief description of the drawings]

FIG. 1 is a perspective view showing one embodiment of an apparatus used in the electronic water treatment method of the present invention.

FIG. 2 is a block diagram of an electronic circuit housed in a control unit of an apparatus used for the electronic water treatment method shown in FIG.

FIG. 3 is a cross-sectional view of an energy radiation unit of the apparatus used in the electronic water treatment method shown in FIG.

FIG. 4 is a connection diagram of coils and electrodes in the energy radiation unit shown in FIG. 3;

[Description of numbering]

 DESCRIPTION OF SYMBOLS 1 Control unit part 2 Basic frequency variable knob 3 Modulation frequency variable knob 4 Basic frequency display 5 Modulation frequency display 6 DC applied voltage variable knob 7 Output display 8 Processing time variable knob 9 Operation display lamp 10 Timer operation start switch 11 Power supply Switch 12 Air supply hose 13 Intake hose 14 Output terminal 15 Fuse 16 Power supply code 17 Basic frequency oscillator 18 Buffer amplifier 19 Prescaler 20 Counter 21 Modulation frequency oscillator 22 Buffer amplifier 23 Prescaler 24 Counter 25 Power amplifier 26 Timer 27 Air supply pump 28 Intake Pump 29 Ozone generator 30 Power plug 31 Power supply circuit 32 Water container 33 Airstone 34 Container lid 35 Ozone killer 36 Coil 37 Electrode 38 Inner container 39 Nipple 40 D Coupler 41 Terminal 42 Opening 43 Opening 44 Series connection 45 Parallel connection

Claims (2)

[Claims] 1. A step of injecting ozone gas into water to oxidize ionic molecules having a resonance relationship with the resonance magnetic energy of a coil placed in water, and molecules bonded to water molecules by the magnetic energy of the coil placed in water. Simultaneously perform the process of reducing the population and the process of electrolyzing water molecules by electrolysis energy generated from electrodes placed in water, and evenly and quickly perform each process by circulating water with the emergence of ozone gas bubbles. An electronic treatment method of water, which is performed. 2. A step of injecting ozone gas into water to oxidize ion molecules having a resonance relationship with a resonance magnetic energy of a coil arranged in water, and a step of oxidizing ionic molecules in the water by the magnetic energy of the coil arranged in water. By simultaneously performing the process of reducing the population and the process of electrolyzing water molecules by electrolysis energy generated from electrodes placed in the water, stopping the supply of ozone gas and injecting air into the water during the process, The process of promoting the decomposition of dissolved ozone by the magnetic energy of the coil placed in the water and the process of eliminating dissolved ozone by the electrolysis energy generated from the electrode placed in the water and reorganizing the hydrogen bond are added, and air bubbles are added. An electronic treatment method for water, wherein each step is performed evenly and quickly by circulating water accompanying the floating of the water.