CN104803466B - A kind of water treatment facilities - Google Patents
A kind of water treatment facilities Download PDFInfo
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- CN104803466B CN104803466B CN201410033488.8A CN201410033488A CN104803466B CN 104803466 B CN104803466 B CN 104803466B CN 201410033488 A CN201410033488 A CN 201410033488A CN 104803466 B CN104803466 B CN 104803466B
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- water
- ejector
- treatment facilities
- anion
- water treatment
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 170
- 150000002500 ions Chemical class 0.000 claims abstract description 28
- 150000001450 anions Chemical class 0.000 claims abstract description 26
- 229910001385 heavy metal Inorganic materials 0.000 claims abstract description 24
- 238000006479 redox reaction Methods 0.000 claims abstract description 5
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 42
- 229910052742 iron Inorganic materials 0.000 claims description 21
- 230000005284 excitation Effects 0.000 claims description 3
- 239000007921 spray Substances 0.000 claims 1
- 238000004659 sterilization and disinfection Methods 0.000 abstract description 5
- 238000000034 method Methods 0.000 description 14
- 229910052739 hydrogen Inorganic materials 0.000 description 9
- 239000001257 hydrogen Substances 0.000 description 9
- SZVJSHCCFOBDDC-UHFFFAOYSA-N ferrosoferric oxide Chemical compound O=[Fe]O[Fe]O[Fe]=O SZVJSHCCFOBDDC-UHFFFAOYSA-N 0.000 description 8
- 230000000694 effects Effects 0.000 description 7
- 229920002338 polyhydroxyethylmethacrylate Polymers 0.000 description 6
- 230000008859 change Effects 0.000 description 5
- 238000010586 diagram Methods 0.000 description 5
- 229940056319 ferrosoferric oxide Drugs 0.000 description 4
- 230000036541 health Effects 0.000 description 4
- 230000008569 process Effects 0.000 description 4
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- DQMUQFUTDWISTM-UHFFFAOYSA-N O.[O-2].[Fe+2].[Fe+2].[O-2] Chemical compound O.[O-2].[Fe+2].[Fe+2].[O-2] DQMUQFUTDWISTM-UHFFFAOYSA-N 0.000 description 2
- 238000010521 absorption reaction Methods 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 229910052791 calcium Inorganic materials 0.000 description 2
- 239000011575 calcium Substances 0.000 description 2
- 238000001311 chemical methods and process Methods 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 230000005672 electromagnetic field Effects 0.000 description 2
- 230000005415 magnetization Effects 0.000 description 2
- 230000004060 metabolic process Effects 0.000 description 2
- 230000003647 oxidation Effects 0.000 description 2
- 238000007254 oxidation reaction Methods 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 238000000746 purification Methods 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 238000003911 water pollution Methods 0.000 description 2
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 1
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 1
- 238000005842 biochemical reaction Methods 0.000 description 1
- 230000033228 biological regulation Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 210000000170 cell membrane Anatomy 0.000 description 1
- 238000009388 chemical precipitation Methods 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 235000009508 confectionery Nutrition 0.000 description 1
- 239000013078 crystal Substances 0.000 description 1
- 201000010099 disease Diseases 0.000 description 1
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 description 1
- 239000003651 drinking water Substances 0.000 description 1
- 235000020188 drinking water Nutrition 0.000 description 1
- 230000005684 electric field Effects 0.000 description 1
- 238000005868 electrolysis reaction Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000008398 formation water Substances 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 230000036039 immunity Effects 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 238000005342 ion exchange Methods 0.000 description 1
- 230000003908 liver function Effects 0.000 description 1
- 159000000003 magnesium salts Chemical class 0.000 description 1
- 239000000696 magnetic material Substances 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 235000010755 mineral Nutrition 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 230000002085 persistent effect Effects 0.000 description 1
- 230000008092 positive effect Effects 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 238000009738 saturating Methods 0.000 description 1
- 239000000741 silica gel Substances 0.000 description 1
- 229910002027 silica gel Inorganic materials 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- CEIZFXOZIQNICU-UHFFFAOYSA-N tenuazonic acid Chemical compound CCC(C)C1NC(=O)C(C(C)=O)=C1O CEIZFXOZIQNICU-UHFFFAOYSA-N 0.000 description 1
- 239000011573 trace mineral Substances 0.000 description 1
- 235000013619 trace mineral Nutrition 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/70—Treatment of water, waste water, or sewage by reduction
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/20—Heavy metals or heavy metal compounds
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Water Treatment By Electricity Or Magnetism (AREA)
- Physical Water Treatments (AREA)
Abstract
The invention discloses a kind of water treatment facilities, including：Pipeline, ion generator and ejector, wherein：Ejector is docked with the pipeline, air intake, the flow inlet for pipeline of plugging into, water export with input anion air；Ion generator connects the air intake of ejector, for producing anion, anion is in the presence of ejector from air intake is sucked into ejector, to cause anion to be sufficiently mixed with the water in ejector, and then anion is occurred redox reaction with the heavy metal ion in water, heavy metal ion in water is reduced to atom, separated out from water.By the above-mentioned means, the present invention can greatly reduce the heavy metal ion content in water, water is carried out disinfection, purified.
Description
Technical field
The present invention relates to water treatment field, more particularly to a kind of water treatment facilities.
Background technology
With industrial progress and social development, water pollution is also on the rise, into global No.1 environmental improvement problem.
In some industry prosperities area, clean sweet spring water has not existed, and water pollution is increasingly severe, constrains expanding economy, together
When also have influence on people health, existence.
Current requirement of the people to quality of drinking water is not only cleaning, and also wants to it and have preferable bioactivity,
Such water can promote the metabolism of human body, the health being beneficial to man.The size of hydrone to the dissolving power of water itself, ooze
Saturating power, surface tension, density and biochemical reaction have stronger influence.In the presence of the magnetic field and electric field, hydrone is each other
Syntagmatic can be changed, and big conclusion micel can be dissociated into small conclusion micel and simple hydrone in water, from
And activate water.Water through overactivation enhances the osmosis to cell membrane, is easy to absorption of human body, thus promotes human body newly old
Metabolism, strengthens liver function, helps to exclude vivotoxin, improves immunity of organisms.During activated water, add simultaneously
Mineral matter alkalescence can be penetrated into electrolytic process bear child in water, add trace element necessary to health, especially
It is soluble calcium, to health, prevention various diseases play positive effect.Device effect currently used for the nanosizing of water has
Limit, the hydrone of formation is still than larger water clusters.
Antiscale, the scale removal of water are approved using magnetization treatment by users.It is passed through using the magnetized water of needs
The method in magnetic field makes water produce magnetic efficiency to realize.When water is by magnetic field, hydrone under the influence of a magnetic field, is changed
The physical arrangement of water, makes calcium in water, the acicular crystal of magnesium salts foulant change over crystalline particulate body, prevents them from interweaving
It is attached to together as hard incrustation scale on wall or tube wall, and bottom is deposited in as small particle, is discharged with blowdown,
The effect of incrustation scale is prevented so as to reaching, original old incrustation scale also by the effect of treated water can be allowed to gradually to degrade, soft
Change, loosen, be cracked, until coming off, reach the purpose of scale removal.In the prior art, prepare magnetized water device include magneto and
Two kinds of electromagnetic type, makes the purpose of magnetic water by the passage form from different magnetic material and current to reach, but magnetization
Effect is not fine, it is impossible to solve the process problem of big flow water quality.
The method of the removal heavy metal in waste water of current development and application mainly has chemical method, physical-chemical process and biology
Method, including chemical precipitation, electrolysis, ion exchange, UF membrane, activated carbon and silica gel absorption, bioflocculation, biological adsorption, plant
The methods such as regulation.In general, secondary pollution is easily caused all by remaining years pollution transportation using chemical method, physical-chemical process, and it is right
It is difficult to handle in the harmful heavy metal pollution of large watershed, low concentration.
The content of the invention
Present invention solves the technical problem that be to provide a kind of water treatment facilities, can greatly reduce heavy metal in water from
Sub- content, carries out disinfection to water, purification.
In order to solve the above technical problems, the invention provides a kind of water treatment facilities, including：Pipeline, ion generator and
Ejector, wherein：Ejector is docked with pipeline, and the water of air intake, pipeline of plugging into input anion air is flowed into
Mouth, water export；Ion generator connects the air intake of ejector, for producing anion, work of the anion in ejector
Under from air intake is sucked into ejector, to cause anion to be sufficiently mixed with the water in ejector, and then make anion
Occur redox reaction with the heavy metal ion in water, the heavy metal ion in water is reduced to atom, separated out from water；
Wherein, ejector is tubular body, and the internal diameter of tubular body is the big distribution in middle small two, the two open ends point of tubular body in the axial direction
Not Wei flow inlet, water export, air intake is opened in the less centre position of internal diameter of tubular body；Water treatment facilities is also wrapped
Iron pipe and two the first magnet and the second magnet set respectively in semi-circular are included, iron pipe is a part for pipeline, the first magnetic
Iron and the second magnet wrap the opposite sides for being attached to iron pipe respectively；Water treatment facilities also includes exciting bank and container, and container is provided with
Water inlet and delivery port, exciting bank enter row energization to the water stored in container so that the water clusters in water be split into
Few two water clusters or hydrone.
Wherein, exciting bank is generating far infrared rays.
Wherein, the wavelength of far infrared is 8 to 14 microns.
Wherein, in the water clusters that each water clusters split off, moisture quantum count is no more than two.
Wherein, the water clusters split off are sprayed directly on plant surface.
Wherein, the upper opening of container.
Wherein, the upper transparent of container, can pass through far infrared.
By such scheme, the beneficial effects of the invention are as follows：Anion is produced by ion generator, in the work of ejector
Under from air intake is sucked into ejector, to cause anion to be sufficiently mixed with the water in ejector, and then make anion
Occur redox reaction with the heavy metal ion in water, the heavy metal ion in water be reduced to atom, separated out from water,
The heavy metal ion content in water can be greatly reduced, water is carried out disinfection, purified.
Brief description of the drawings
Fig. 1 is the structural representation of the water treatment facilities of the nanosizing for water of first embodiment of the invention；
Fig. 2 is the method for making Nano schematic diagram of the water of first embodiment of the invention；
Fig. 3 is the schematic flow sheet of the method for the nanosizing of the water of first embodiment of the invention；
Fig. 4 is the structural representation for being used to remove the water treatment facilities of removing heavy metals of first embodiment of the invention；
Fig. 5 is the structural representation of the water treatment facilities for de-sludging of first embodiment of the invention；
Fig. 6 be first embodiment of the invention the water treatment facilities for de-sludging in two half-ring-shaped magnets cross-sectional structure
Schematic diagram；
Fig. 7 is the water treatment system schematic diagram of first embodiment of the invention.
Embodiment
Referring to Fig. 1, Fig. 1 is the structural representation of the water treatment facilities of the nanosizing for water of first embodiment of the invention
Figure.As shown in figure 1, the water treatment facilities 10 of the nanosizing for water of the present embodiment includes container 11, water inlet 12, delivery port
13 and exciting bank 14, arrow represents the flow direction of water.Container 11 is used to store pending water, and exciting bank 14 is to container 11
The water of middle storage enters row energization so that the water clusters in water are split at least two water clusters or hydrone.
In embodiments of the present invention, water is flowed into from water inlet 12, after the processing of container 11, is flowed out from delivery port 13.Hold
Water in device 11 is made up of many big water clusters.And big water clusters are then to pass through hydrogen bond knot by many single hydrones
Conjunction is formed, and the energy of hydrogen bond is not high, can produce resonance with far infrared.Exciting bank 14 is far infrared generating means, is used for
Produce the far infrared that wavelength is 8 to 14 microns.The top of container 11 can be opening or transparent, with convenient
Far-infrared engergy is irradiated in pending water.Far infrared is irradiated in container 11, the hydrogen bond between far infrared and hydrone
Resonance is produced, and then interrupts the hydrogen bond between hydrone.As shown in Fig. 22 hydrones are by Hydrogenbond formation water clusters,
When far infrared irradiates and produces resonance with the hydrogen bond, the hydrogen bond combined between 2 hydrones is broken in the presence of resonance, is made
2 molecular water clusters of moisture split into 2 single hydrones.Herein, 2 hydrones can also be hydrone
Group, both form big water clusters by Hydrogenbond, and the far infrared of the big water clusters and irradiation produces resonance, and hydrogen bond breaks
Split, be split at least two water clusters or hydrone.In this way, under the Persistent Excitation of far infrared, big hydrone in water
Group constantly splits into the water clusters of small, is further split into smaller water clusters even single hydrone.It is final each
In the water clusters that water clusters split off, moisture quantum count is no more than two, so as to form the water of nanosizing, divides
The water clusters come are sprayed directly on plant surface, it is easy to absorbed by plant.
Referring to Fig. 3, Fig. 3 is the method flow schematic diagram of the nanosizing of the water of first embodiment of the invention.Such as Fig. 3 institutes
Show, this method includes：
S10：Row energization is entered to the water being stored in container 11.
Pending water flows through container 11, and enters row energization in container 11.It is remote for 8 to 14 microns that wavelength is produced first
Infrared ray, recycles far infrared to enter row energization to the water being stored in container 11.The top of container 11 can be opening,
Can be transparent, to facilitate far-infrared engergy to be irradiated in pending water.Before far infrared irradiation, pending water
It is made up of many big water clusters.And big water clusters are then to be formed by many single hydrones by Hydrogenbond.Hydrogen
The energy of key is not high, can produce resonance with far infrared.
S11：Water clusters in water are split at least two water clusters or hydrone.
In S11, under the excitation of far infrared, the hydrogen bond in hydrone is constantly broken in the presence of resonance, moisture
During quantum splitting is at least two water clusters or hydrone, the water clusters that final each water clusters split off, hydrone
Quantity is no more than two, and then forms the water of nanosizing, and the water clusters split off are sprayed directly on plant surface, it is easy to
Absorbed by plant.
Referring to Fig. 4, Fig. 4 is the structural representation for being used to remove the water treatment facilities of removing heavy metals of first embodiment of the invention
Figure.As shown in figure 4, the present embodiment be used for go the water treatment facilities 20 of removing heavy metals to include：Ejector 21, ion generator 22
And pipeline, wherein, ejector 21 is docked with pipeline, air intake 23, pipeline of plugging into input anion air
Flow inlet 24, water export 25.The direction of arrow represents the flow direction of current.Ion generator 22 connects the sky of ejector 21
Gas entrance 23, for producing anion.Anion is sucked into ejector 21 in the presence of ejector 21 from air intake 23,
To cause anion to be sufficiently mixed with the water in ejector 21, and then anion is set to occur oxidation also with the heavy metal ion in water
Original reaction, is reduced to atom by the heavy metal ion in water, is separated out from water, and as current are discharged.In this way, the water
Processing unit 20 can greatly reduce the heavy metal ion content in water, and water is carried out disinfection, purification.
In embodiments of the present invention, ejector 21 is tubular body, and the internal diameter of tubular body is big for middle small two in the axial direction
Distribution, the two open ends of tubular body are respectively flow inlet 24, water export 25, and air intake 23 is opened in the internal diameter of tubular body
Less centre position.In other embodiments of the invention, ejector 21 can also be with other structures, as long as can make to bear
Ion is sufficiently mixed with water.
Referring to Fig. 5, Fig. 5 is the structural representation of the water treatment facilities for de-sludging of first embodiment of the invention.Such as
Shown in Fig. 5, the water treatment facilities 30 for de-sludging of the present embodiment includes：Iron pipe 303 and two are set in semi-circular respectively
The first magnet 301 and the second magnet 302, the first magnet 301 and the second magnet 302 are wrapped respectively is attached to relative the two of iron pipe 303
Side, the first magnet 301 and the second magnet 302 are arranged on the axis direction of iron pipe 303 produce sufficiently large rate of change of magnetic,
So that the di-iron trioxide that the ion in the water flowed along the axis direction of iron pipe 303 is accelerated into being produced on iron pipe wall is acted on
Produce ferroso-ferric oxide.The cross section of first magnet 301 and the second magnet 302 is as shown in fig. 6, the first magnet 301 and the second magnetic
The constant magnetic field of each self-forming of iron 302, the magnetic field intensity in magnetic field is equal, is all B.This two semiorbicular Hes of first magnet 301
The magnetic line of force of second magnet 302 is all closed, and is not intersected, with border AA ' and border CC ' for boundary, has magnetic within two borders
, there is no magnetic field outside two borders.
The power F that electrically charged particle is produced in variation magnetic field meets following relational expression：
F∝ΔB/Δt,
I.e. power F is proportional to the rate of change in magnetic field.First magnet 301 and the constant magnetic field of each self-forming of the second magnet 302, two
Magnetic field is high-strength magnetic field, and size is all B.In border AA ' places magnetic field from scratch, the rate of change Δ B/ Δs t in magnetic field is very big, therefore
Power F is than larger.The di-iron trioxide of generation is attached with the tube wall of iron pipe 303, four oxidations three are produced with the ionization in water
Iron.Electromagnetic field strengthens hydrone and composition of scale molecular activity, original old dirt on the tube wall of iron pipe 303, in active moisture
Come off in the presence of ferroso-ferric oxide and electromagnetic field dipole-dipole force F on the tube wall of son and iron pipe 303, then as current are discharged.
Relatively stablize under ferroso-ferric oxide normal temperature, after old dirt is removed, ferroso-ferric oxide is formed for avoiding incrustation scale in the tube wall of iron pipe 303
The diaphragm of attachment makes tube wall no longer fouling, can permanent retention pipeline it is unimpeded.In embodiments of the present invention, the pipeline of conveying water can
It can also be that attached part is wrapped for iron pipe 303 by the first magnet 301 and the second magnet 302 to be entirely iron pipe, and set
In the both sides of iron pipe 303 pipeline be remaining material pipeline, such as plastic conduit, it goes the effect of scale removal to be the same.
Referring to Fig. 7, Fig. 7 is the water treatment system schematic diagram of first embodiment of the invention.As shown in fig. 7, water process system
System include it is previously described for go removing heavy metals water treatment facilities 20, for water nanosizing water treatment facilities 10 and
Water treatment facilities 30 for de-sludging.Current flow through water treatment facilities 20, the water for de-sludging for removing removing heavy metals successively
The water treatment facilities 10 of processing unit 30 and nanosizing for water, to reach the effect of more preferable water process.Certainly, at this
In the other embodiment of invention, these three water treatment facilities can also be connected in other sequences, or only one or two kinds of water
Processing unit is constituted.
In summary, the present invention produces anion by ion generator, and from air intake in the presence of ejector
It is sucked into ejector, to cause anion to be sufficiently mixed with the water in ejector, and then makes anion and the heavy metal in water
Redox reaction occurs for ion, and the heavy metal ion in water is reduced into atom, separated out from water, can greatly reduce water
In heavy metal ion content, water is carried out disinfection, purify.
Embodiments of the invention are the foregoing is only, are not intended to limit the scope of the invention, it is every to utilize this hair
Equivalent structure or equivalent flow conversion that bright specification and accompanying drawing content are made, or directly or indirectly it is used in other related skills
Art field, is included within the scope of the present invention.
Claims (7)
1. a kind of water treatment facilities, it is characterised in that including：Pipeline, ion generator and ejector, wherein：
The ejector is docked with the pipeline, and the water of air intake, pipeline of plugging into input anion air is flowed into
Mouth, water export；
The ion generator connects the air intake of the ejector, and for producing anion, the anion is in ejector
In the presence of from the air intake is sucked into the ejector, to cause the water in the anion and ejector fully to mix
Close, and then the anion is occurred redox reaction with the heavy metal ion in water, by the heavy metal ion in water
Atom is reduced to, is separated out from water；
Wherein, the ejector is tubular body, and the internal diameter of the tubular body is the big distribution in middle small two, the pipe in the axial direction
The two open ends of shape body are respectively the flow inlet, water export, and the air intake is opened in the internal diameter of the tubular body
Less centre position；
The water treatment facilities also includes iron pipe and two the first magnet and the second magnet set respectively in semi-circular, described
Iron pipe is a part for the pipeline, and first magnet and second magnet are wrapped respectively is attached to relative the two of the iron pipe
Side；
The water treatment facilities also includes exciting bank and container, and the container is provided with water inlet and delivery port, the excitation
Device enters row energization to the water stored in the container so that the water clusters in the water are split at least two water clusters
Or hydrone.
2. water treatment facilities according to claim 1, it is characterised in that the exciting bank is that far infrared is filled
Put.
3. water treatment facilities according to claim 2, it is characterised in that the wavelength of the far infrared is 8 to 14 microns.
4. water treatment facilities according to claim 1, it is characterised in that the moisture that each water clusters split off
In son group, moisture quantum count is no more than two.
5. water treatment facilities according to claim 1, it is characterised in that the water clusters split off directly spray
In plant surface.
6. water treatment facilities according to claim 1, it is characterised in that the upper opening of the container.
7. water treatment facilities according to claim 1, it is characterised in that the upper transparent of the container, can be through remote red
Outside line.
Priority Applications (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201410033488.8A CN104803466B (en) | 2014-01-23 | 2014-01-23 | A kind of water treatment facilities |
| PCT/CN2014/079256 WO2015109722A1 (en) | 2014-01-23 | 2014-06-05 | Water treatment apparatus |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201410033488.8A CN104803466B (en) | 2014-01-23 | 2014-01-23 | A kind of water treatment facilities |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN104803466A CN104803466A (en) | 2015-07-29 |
| CN104803466B true CN104803466B (en) | 2017-10-17 |
Family
ID=53680734
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201410033488.8A Expired - Fee Related CN104803466B (en) | 2014-01-23 | 2014-01-23 | A kind of water treatment facilities |
Country Status (2)
| Country | Link |
|---|---|
| CN (1) | CN104803466B (en) |
| WO (1) | WO2015109722A1 (en) |
Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN2776958Y (en) * | 2005-03-10 | 2006-05-03 | 陈为泰 | Decontamination device of drinking water |
| CN201046923Y (en) * | 2007-05-17 | 2008-04-16 | 彭艺勇 | Drink magnetizing activating health care device |
| CN202643386U (en) * | 2012-01-06 | 2013-01-02 | 刘应龙 | Strong magnetized circulating water processing apparatus |
| CN203360095U (en) * | 2013-07-10 | 2013-12-25 | 江苏上田环境修复有限公司 | Device for treating underground water polluted by organic matters |
Family Cites Families (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO1996037439A1 (en) * | 1995-05-26 | 1996-11-28 | Marcelino Fernandez Fernandez | Laser device for purifying contaminated waters |
| EP0936188A1 (en) * | 1998-01-20 | 1999-08-18 | Hee Jung Kim | Process for reducing viscosity of water through electrolysis |
| CN2367605Y (en) * | 1999-03-10 | 2000-03-08 | 范玉明 | Multifunction oxygen-rich water-purifying machine |
| CN1135283C (en) * | 1999-03-23 | 2004-01-21 | 杉野庆一 | Water treatment equipment |
| JP2002307073A (en) * | 2001-04-12 | 2002-10-22 | Hitachi Zosen Corp | Turbid water treatment equipment |
| CN201554939U (en) * | 2009-11-27 | 2010-08-18 | 刘雄辉 | Faucet with jet nozzle |
| KR101152433B1 (en) * | 2010-04-23 | 2012-06-05 | 최정수 | Nozzle for generating nano bubble and oral cleaning device whit the same |
| CN103214065A (en) * | 2012-01-19 | 2013-07-24 | 桂雷珠 | Induction coil negative ion water generator |
| CN202785732U (en) * | 2012-05-31 | 2013-03-13 | 鹤山市雷迅新农机械科技有限公司 | Energy pool |
-
2014
- 2014-01-23 CN CN201410033488.8A patent/CN104803466B/en not_active Expired - Fee Related
- 2014-06-05 WO PCT/CN2014/079256 patent/WO2015109722A1/en active Application Filing
Patent Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN2776958Y (en) * | 2005-03-10 | 2006-05-03 | 陈为泰 | Decontamination device of drinking water |
| CN201046923Y (en) * | 2007-05-17 | 2008-04-16 | 彭艺勇 | Drink magnetizing activating health care device |
| CN202643386U (en) * | 2012-01-06 | 2013-01-02 | 刘应龙 | Strong magnetized circulating water processing apparatus |
| CN203360095U (en) * | 2013-07-10 | 2013-12-25 | 江苏上田环境修复有限公司 | Device for treating underground water polluted by organic matters |
Also Published As
| Publication number | Publication date |
|---|---|
| WO2015109722A1 (en) | 2015-07-30 |
| CN104803466A (en) | 2015-07-29 |
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