WO2015109723A1 - Water treatment device and water nanonization method - Google Patents

Abstract

The present invention discloses a water treatment device and water nanonization method, comprising: an excitation device and a container, the container being provided with a water inlet and a water outlet; the excitation device excites the water stored in the container, such that the water molecular groups in the water split into at least two water molecular groups or water molecules. By the described means, the present invention causes larger water molecular groups to break down into very small water molecular groups or individual water molecules, forming nanonized water that is readily absorbed by plant bodies.

Description

Water treatment device and method for nanometerization of water

[Technical Field]

The present invention relates to the field of water treatment, and more particularly to a method of water treatment apparatus and nanocrystallization of water.

 【Background technique】

With industrial progress and social development, water pollution has become increasingly serious, becoming the world's number one environmental governance problem. In some industrially developed areas, clean Ganquan has ceased to exist, water pollution has become more and more serious, restricting the development of the economy, and also affecting people's health and survival.

At present, people's requirements for the quality of drinking water are not only clean, but also hope that they have good biological activity. Such water can promote the metabolism of the human body and benefit human health. The size of water molecules has a strong influence on the water's own solubility, penetration, surface tension, density and biochemical reactions. Under the action of the magnetic field and the electric field, the combination relationship between the water molecules changes, and the large molecular clusters in the water are dissociated into small associating molecular groups and simple water molecules, thereby activating water. The activated water enhances the osmotic effect on the cell membrane and facilitates absorption by the human body, thereby enhancing the body's metabolism, enhancing liver function, helping to eliminate toxins in the body, and improving the body's immunity. In the process of activating water, the minerals added at the same time will penetrate into the alkaline children's water during the electrolysis process, which increases the trace elements necessary for human health, especially soluble calcium, which is active for human health and prevention of various diseases. The role. At present, the device for nanocrystallization of water has limited effect, and the formed water molecules are still relatively large water molecules.

The anti-scaling and descaling of water has been recognized by the users. It is achieved by using a magnetized water through a magnetic field to produce a magnetization effect on the water. When the water passes through the magnetic field, the water molecules change the physical structure of the water under the action of the magnetic field, so that the needle-like crystals of the calcium and magnesium salts in the water are changed into granular crystals, so that they cannot be intertwined and become hard. The scale adheres to the wall or the wall of the pipe, and becomes tiny particles deposited on the bottom, which is discharged with the sewage, thereby preventing the scale. The original old scale can also be gradually denuded by the action of the treated water. Soften, loose, crack, until it falls off, to achieve the purpose of descaling. In the prior art, the device for preparing magnetized water comprises two types of permanent magnet type and electromagnetic type, and the purpose of making water magnetization is achieved by selecting different magnetic materials and water passage paths, but the magnetization effect is not very good, and the large flow rate cannot be solved. Water quality treatment issues.

At present, methods for removing heavy metals in wastewater have been developed, including chemical methods, physical and chemical methods, and biological methods, including chemical precipitation, electrolysis, ion exchange, membrane separation, activated carbon and silica gel adsorption, bioflocculation, biosorption, plant remediation, etc. method. In general, chemical and physical chemical methods are used to transfer residual pollution, which is likely to cause secondary pollution, and is difficult to treat harmful heavy metal pollution in large watersheds and low concentrations.

 [Summary of the Invention]

The technical problem to be solved by the present invention is to provide a water treatment device and a method for nanocrystallization of water, which can decompose water molecules in water into small water molecules or individual water molecules, thereby forming nanometer water. Easy to be absorbed by plants.

In order to solve the above technical problems, the present invention provides a water treatment apparatus comprising: an excitation device and a container, the container being provided with a water inlet and a water outlet, the excitation device exciting the water stored in the container, such that The water clusters in the water split into at least two water molecules or water molecules.

Among them, the excitation device is a far infrared ray generating device.

Among them, the far infrared ray has a wavelength of 8 to 14 μm.

Wherein, in each of the water molecules clustered by the water molecule group, the number of water molecules is not more than two.

Among them, the split water molecules are sprayed directly on the surface of the plant.

Among them, the upper part of the container is open.

Among them, the upper part of the container is transparent and can transmit far infrared rays.

In order to solve the above technical problems, the present invention also provides a method for nanocrystallization of water, comprising: exciting water stored in a container; and splitting water molecules in the water into at least two water molecules or water molecules .

Wherein, energizing the water stored in the container comprises: generating far infrared rays; and exciting the water stored in the container with the far infrared rays.

Among them, the far infrared ray has a wavelength of 8 to 14 μm.

Through the above scheme, the beneficial effects of the present invention are: exciting the water stored in the container by the excitation device, so that the water molecular group in the water splits into at least two water molecules or water molecules, thereby decomposing the larger water molecules. It is a small water molecule or a single water molecule that forms nano-sized water that is easily absorbed by plants.

 [Description of the Drawings]

1 is a schematic structural view of a water treatment apparatus for nanocrystallization of water according to a first embodiment of the present invention;

2 is a schematic view showing a method of nanocrystallization of water according to a first embodiment of the present invention;

3 is a schematic flow chart of a method for nanocrystallization of water according to a first embodiment of the present invention;

4 is a schematic structural view of a water treatment apparatus for removing heavy metals according to a first embodiment of the present invention;

Figure 5 is a schematic structural view of a water treatment apparatus for descaling according to a first embodiment of the present invention;

Figure 6 is a cross-sectional structural view showing a two-half ring magnet in a water treatment device for descaling according to a first embodiment of the present invention;

Figure 7 is a schematic illustration of a water treatment system in accordance with a first embodiment of the present invention.

 【detailed description】

Please refer to FIG. 1. FIG. 1 is a schematic structural view of a water treatment apparatus for nanometerization of water according to a first embodiment of the present invention. As shown in Fig. 1, the water treatment apparatus 10 for nanocrystallization of water of the present embodiment includes a container 11, a water inlet 12, a water outlet 13, and an excitation device 14, and arrows indicate the flow direction of water. The container 11 is used to store water to be treated, and the excitation device 14 energizes the water stored in the container 11 such that the water molecules in the water split into at least two water molecules or water molecules.

In the embodiment of the present invention, water flows in from the water inlet 12, passes through the container 11, and flows out from the water outlet 13. The water in the vessel 11 is composed of a number of large water clusters. Large water molecules are formed by hydrogen bonding of many individual water molecules. The hydrogen bond energy is not high and can resonate with far infrared rays. The excitation device 14 is a far infrared generating device for generating far infrared rays having a wavelength of 8 to 14 μm. The upper portion of the container 11 may be open or transparent to facilitate the irradiation of far infrared rays into the water to be treated. The far-infrared rays are irradiated into the container 11, and the hydrogen bonds between the far-infrared rays and the water molecules resonate, thereby breaking the hydrogen bonds between the water molecules. As shown in FIG. 2, two water molecules are hydrogen-bonded to form a water molecule group, and when far-infrared rays are irradiated and resonate with the hydrogen bond, the hydrogen bonds bonded between the two water molecules are broken by the resonance, so that Two water molecules composed of water molecules are split into two individual water molecules. Here, the two water molecules may also be water molecules, and the two hydrogen bonds form a large water molecule group, and the large water molecule group resonates with the irradiated far infrared rays, the hydrogen bond breaks, and splits into at least two water molecules. Group or water molecule. Thus, under the continuous excitation of far infrared rays, large water molecules in the water are continuously split into small water molecules, which are further split into smaller water molecules or even individual water molecules. Finally, in the water molecule group where each water molecule group is split, the proportion of water molecules in which the number of water molecules does not exceed two is required to form nanometerized water, and the split water molecule group can be directly sprayed on the plant surface, which is easy. It is absorbed by the plant; of course, it can also be sprayed in the soil and enter the roots of the plant from the soil.

Please refer to FIG. 3. FIG. 3 is a schematic flow chart of a method for nanocrystallization of water according to a first embodiment of the present invention. As shown in FIG. 3, the method includes:

S10: Exciting water stored in the container 11.

The water to be treated flows through the container 11 and is excited in the container 11. First, far infrared rays having a wavelength of 8 to 14 μm, such as 9, 10, 11, 12, or 13 μm, are generated, and the water stored in the container 11 is excited by far infrared rays. The upper portion of the container 11 may be open or transparent to facilitate the irradiation of far infrared rays into the water to be treated. Prior to far infrared illumination, the water to be treated consists of a number of large water clusters. Large water molecules are formed by hydrogen bonding of many individual water molecules. The hydrogen bond energy is not high and can resonate with far infrared rays.

S11: The water molecule cluster in the water splits into at least two water molecules or water molecules.

In S11, under the excitation of far infrared rays, the hydrogen bonds in the water molecules are continuously broken under the action of resonance, and the water molecules are split into at least two water molecules or water molecules, and finally the water molecules split by each water molecule group. In the group, the number of water molecules is no more than two, which forms nano-sized water. The split water molecules are sprayed directly on the surface of the plant and are easily absorbed by the plant.

Please refer to FIG. 4. FIG. 4 is a schematic structural diagram of a water treatment system for removing heavy metals according to a first embodiment of the present invention. As shown in FIG. 4, the water treatment system 20 for removing heavy metals of the present embodiment includes: a jet 21, an ion generator 22, and a pipe, wherein the jet 21 is connected to the pipe and has an air inlet for inputting negative ion air. 23. The water inlet 24 and the water outlet 25 of the connecting pipe. The direction of the arrow indicates the direction of flow of the water flow. The ionizer 22 is connected to the air inlet 23 of the jet 21 for generating negative ions. The negative ions are sucked from the air inlet 23 into the jet 21 by the action of the jet 21, so that the negative ions are sufficiently mixed with the water in the jet 21, thereby causing the negative ions to undergo a redox reaction with heavy metal ions in the water, and the said Heavy metal ions are reduced to atoms, which are separated from the water and discharged with the water. As such, the water treatment system 20 can greatly reduce the heavy metal ion content in the water, disinfect and purify the water.

In the embodiment of the present invention, the jet 21 is a tubular body, and the inner diameter of the tubular body is distributed in the middle of the small center. The two ends of the tubular body are respectively a water inlet 24 and a water outlet 25, and the air inlet 23 is opened in a tubular shape. The middle position of the body with a small inner diameter. In other embodiments of the present invention, the fluidizer 21 may have other configurations as long as the negative ions can be sufficiently mixed with water.

Referring to FIG. 5, FIG. 5 is a schematic structural view of a water treatment apparatus for descaling according to a first embodiment of the present invention. As shown in FIG. 5, the water treatment device 30 for descaling of the present embodiment includes: an iron pipe 303 and two first magnets 301 and a second magnet 302 respectively disposed in a semi-annular shape, and first magnets 301 and second The magnets 302 are respectively attached to opposite sides of the iron pipe 303, and the first magnet 301 and the second magnet 302 are disposed to generate a sufficiently large magnetic field change rate in the axial direction of the iron pipe 303 so as to be along the axial direction of the iron pipe 303. The ions in the flowing water are accelerated to react with ferric oxide produced on the wall of the iron pipe to produce triiron tetroxide. The cross section of the first magnet 301 and the second magnet 302 is as shown in FIG. 6. The first magnet 301 and the second magnet 302 each form a constant magnetic field, and the magnetic field strength of the magnetic field is equal, and both are B. The magnetic lines of force of the two semi-annular first magnets 301 and the second magnets 302 are both closed and do not intersect each other, with the boundary AA' and the boundary CC' as boundaries, with magnetic fields within the two boundaries, and no magnetic field outside the two boundaries.

The force F generated by the charged particles in the changing magnetic field satisfies the following relationship:

F∝ΔB/Δt,

That is, the force F is proportional to the rate of change of the magnetic field. The first magnet 301 and the second magnet 302 each form a constant magnetic field, and the two magnetic fields are high-strength magnetic fields, and both have a size B. At the boundary AA', the magnetic field is from nothing, and the rate of change of the magnetic field ΔB/Δt is large, so the force F is relatively large. The generated iron oxide is adhered to the wall of the iron pipe 303, and acts with ions in the water to produce triiron tetroxide. The electromagnetic field enhances the molecular activity of the water molecules and the scale component, and the original scale on the pipe wall of the iron pipe 303 falls off under the action of the ferroferric oxide and the electromagnetic field orientation force F on the pipe wall of the active water molecule and the iron pipe 303. It then drains with the water. The triiron tetroxide is relatively stable at normal temperature. After the old scale is removed, the ferroferric oxide forms a protective film on the wall of the iron pipe 303 for preventing scale adhesion, so that the pipe wall is no longer fouled, and the pipe can be kept open forever. In the embodiment of the present invention, the pipes for conveying water may all be iron pipes, or only the portion enclosed by the first magnet 301 and the second magnet 302 may be the iron pipe 303, and the pipes disposed on both sides of the iron pipe 303. Pipes for the rest of the material, such as plastic pipes, have the same effect of removing scale.

Please refer to FIG. 7. FIG. 7 is a schematic diagram of a water treatment system according to a first embodiment of the present invention. As shown in FIG. 7, the water treatment system includes the water treatment device 20 for removing heavy metals, the water treatment device 10 for nanocrystallization of water, and the water treatment device 30 for descaling described above. The water flow sequentially flows through the water treatment device 20 for removing heavy metals, the water treatment device 30 for descaling, and the water treatment device 10 for nanocrystallization of water to achieve a better water treatment effect. Of course, in other embodiments of the invention, the three water treatment devices may also be connected in other sequences, or may be composed of only one or two water treatment devices.

In summary, the present invention excites the water stored in the container by the excitation device, so that the water molecules in the water split into at least two water molecules or water molecules, thereby decomposing the larger water molecules into small ones. Water clusters or individual water molecules form nano-sized water that is easily absorbed by plants.

The above is only the embodiment of the present invention, and is not intended to limit the scope of the invention, and the equivalent structure or equivalent process transformation of the present invention and the contents of the drawings may be directly or indirectly applied to other related technologies. The fields are all included in the scope of patent protection of the present invention.

Claims (10)

1. A water treatment device, characterized in that the water treatment device comprises: an excitation device and a container, the container is provided with a water inlet and a water outlet, and the excitation device excites water stored in the container, so that The water clusters in the water split into at least two water molecules or water molecules.
2. A water treatment device according to claim 1, wherein said excitation means is a far infrared ray generating means.
3. The water treatment apparatus according to claim 2, wherein said far infrared ray has a wavelength of any one of 8 to 14 μm.
4. The water treatment device according to claim 1, wherein the number of water molecules in each of the water molecule groups split by the water molecule group is not more than two.
5. A water treatment device according to claim 1 wherein said split water molecules are sprayed directly onto the surface of the plant.
6. The water treatment device according to claim 1, wherein an upper portion of the container is open.
7. The water treatment device according to claim 1, wherein the upper portion of the container is transparent and can transmit far infrared rays.
8. A method of nanocrystallization of water, characterized in that the method comprises:

   Inspiring water stored in the container;

   The water clusters in the water split into at least two water molecules or water molecules.
9. The method of claim 8 wherein said energizing said water stored in said container comprises:

   Producing far infrared rays;

   The water stored in the container is excited by the far infrared rays.
10. The method of claim 9 wherein said far infrared ray has a wavelength of from 8 to 14 microns.