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CN104876375A - Deep oxidization water treatment method and deep oxidization water treatment device - Google Patents

Deep oxidization water treatment method and deep oxidization water treatment device Download PDF

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CN104876375A
CN104876375A CN201510208520.6A CN201510208520A CN104876375A CN 104876375 A CN104876375 A CN 104876375A CN 201510208520 A CN201510208520 A CN 201510208520A CN 104876375 A CN104876375 A CN 104876375A
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water treatment
ozone
treatment method
deep
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刘毅
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Abstract

The invention relates to a deep oxidization water treatment method and a deep oxidization water treatment device; the deep oxidization water treatment method and the deep oxidization water treatment device are formed by utilizing a high dissolved ozone amount air dissolution technology and a micro-bubble aeration technology in combination with use of ozone, ultraviolet photocatalysis and a photosensitive chemical catalyst; dissolved oxygen and ozone are utilized; furthermore, a large number of hydroxyl radicals excited by ultraviolet photocatalysis chemical reaction can participate in the so-called oxidization chain reaction; and a deep oxidization technology is higher in oxidation capacity and rapider in oxidization speed. The deep oxidization water treatment method and the deep oxidization water treatment device disclosed by the invention are not only applied to sterilizing ordinary drinking water but also applied to oxidizing and degrading organic pollutants, which are difficult to biodegrade and high in concentration and toxicity; and the deep oxidization water treatment method and the deep oxidization water treatment device not only can be used as an independent sewage treatment method and an independent sewage treatment device but also can be used as a pre-processing method for reducing the concentration and the toxicity in sewage used with the existing biodegradable water treatment technological method and equipment in a matched manner.

Description

A kind of deep oxidation water treatment method and device
Technical field:
Adopt the molten gas technology of high molten ozone amount and microbubble aeration process, be combined ozone, ultraviolet catalytic and photosensitizing chemical catalyzer and form a kind of deep oxidation water treatment method and device, not only utilize dissolved oxygen and ozone, the great amount of hydroxy group free radical mainly utilizing chemical reaction to excite participates in oxidation and forms so-called chain reaction, be that a kind of oxidation capacity is higher, oxidation rate is advanced oxidation processes faster.This invention is not only applicable to the sterilization of common drinking water, is more suitable for the highly toxic organic pollutant of high density of difficult for biological degradation in oxidative degradation water.Both can using as independently sewage water treatment method and device, also can use as reducing the pre-treatment method of concentration of wastewater and toxicity and existing biodegradable water treatment method and coordinative composition of equipments.Belong to water-treatment technology field.
Background technology:
Ozone is a kind of strong oxidizer, can be oxidized various organism.20 century 70s, people begin one's study and utilize ozone as the sterilizing agent of tap water, swimming-pool water, and obtain good effect.Ozone not only can be applied in drinking water treatment, also can be used in the process of waste water.The effect of ozone in water and waste water can be generalized into three classes: one is be used as sterilizing agent or sterilant; Two is the oxygenants being used as oxidation organic pollutant; Three is for other processing units (comprising coagulation, flocculation, precipitation, bio-oxidation, charcoal absorption etc.) provide dissolved oxygen and ascending gas bubbles.
High pressure dissolving dissolved ozone is the effective ways improving ozone solution amount.Chinese patent (publication number CN104043356A), (publication number CN201330188Y) are proposed the method utilizing microbubble to improve water body dissolved-air rate in dissolving; Chinese patent (publication number CN103736409A), (publication number CN202415245U) adopt the way controlled respectively to gas-liquid mixing pump delivering gas amount and discharge to obtain dissolved air water at dissolving, and dissolved air water is equipped with suitable reliever again will produce a large amount of uniform microbubble.But dissolving function singleness in these technical schemes, only provides and store high concentrations dissolved air water.
The advantages such as oxidation organic pollutants ability is strong although ozonation technology has, decomposition rate fast, non-secondary pollution, are used alone ozone, still there is O 3solubleness in water is low, and affect the problem of oxidation efficiency, ozone oxidation has selectivity, and different types of organic matter degradation ability and speed exist very big-difference.In ozone oxidation process, add UV-light and the catalyzer with photocatalytic effect is one of effective ways addressed this problem, belong to the category of degree of depth oxygen technology.Advanced oxidation processes, also known as high-level oxidation technology (Advanced Oxidation Process, AOP) refer to oxidation capacity exceed all common oxidants or oxidizing potential close to or reach Hydroxyl radical HO level, serial free chain reaction can be carried out with organic pollutant, thus destroy its structure, make it progressively be degraded to harmless low-molecular-weight organism, be finally degraded to CO 2, H 2the technology of O and other mineral salts is hot fields of current water technology research.Ultraviolet catalytic oxidation is owned by France in advanced oxidation processes, and it is mainly with water-soluble ozone O 3, hydrogen peroxide H 2o 2, oxygen O 2with air as oxygenant, under thermal effect, produce Hydroxyl radical HO.Photocatalytic oxidation is in reaction soln, add a certain amount of catalyzer, makes it under the irradiation of UV-light (UV), produce Hydroxyl radical HO, is processed by the strong oxidation of HO to organic pollutant.
Ozone content, illumination frequency and intensity, catalyst component and quality etc. all can affect the ability of oxidizing reaction and the oxidation rate of sewage.Chinese patent (publication number CN202625991U) proposes a kind of ultraviolet light ozone catalyst reaction device, but catalyzed reaction environment is in non-pressure vessel, ozone saturation solubility is smaller, low ability and the speed that still govern ultraviolet catalytic oxidation reaction of the ozone saturation solubility of the ozone oxidation reaction (later claiming ozonize) under photochemical catalysis.
According to the phase of used catalyst, ozone catalytic is divided into homogeneous catalysis ozonize and multi-phase catalytic ozonation.The former is liquid catalyst mainly, and the latter's mainly solid catalyst.Because homogeneous catalyst can form homogeneous concentration in the solution, therefore there is the advantages such as activity is high, speed of response is fast.But post catalyst reaction and sewage blending, be difficult to again separate, cause catalyzer to cause financial loss because of loss, too increase the burden of the subsequent disposal of catalytic ozonation reaction, add the complicacy of catalytic ozonation technique, improve cost of water treatment.Compared with homogeneous catalyst, heterogeneous catalyst exists in solid form, is easily separated from water, and technical process is simple, has both avoided the loss of catalyzer, and has also reduced follow-up processing cost.In the research of nearly more than ten years, heterogeneous catalyst obtains more favor.
The aerating apparatus of routine techniques can only produce grade bubble, and bubble directly floats.Ozone or other gas residence time in water is very short, so molten ozone amount is lower in water.Because ozone can not fully dissolve in the middle of water body, some pollutent retaining on a small quantity in water body is difficult to remove clean, even if the method for the excessive ozone that exposes to the sun as usually adopted, produces effects also not obvious.It is also one of difficult problem processing chemical pollution that trace chemistry pollutent difficulty is removed.The method for subsequent processing such as biological degradation are often needed to be supplemented.
The present invention proposes a kind of method of more high efficiency deep oxidation organic pollutants on the basis setting up a new chemical reaction equipment system, producing great amount of hydroxy group free radical by increasing photo-catalysis function in the tank body of the molten ozone water environment of height, reaching the object increasing oxidation capacity, improve oxidative degradation rate.
Summary of the invention:
The present invention relates to a kind of water treatment method and device of deep oxidation, water treatment procedure is divided into three sections, and order completes in three kinds of devices, they are photochemical catalysis oxidation reaction apparatus and continuity reaction microbubble aerating apparatus under ozone and sewage mixing device, high pressure respectively.
Ozone and sewage mixing device are made up of source of oxygen and the reducing valve of attaching troops to a unit, oxygen flow meter, oxygen conveying pipe, ozonizer, gas-liquid mixing pump, Venturi liquid gas combining nozzle etc.
The working process of ozone and sewage mixing device is, gas-liquid mixed mouth inspiration simultaneously sewage and the ozone that have adjusted flow of Venturi tube structure, gas-liquid mixing pump quick runner smashes the molten ozone water of the high molten ozone amount of bubble formation, and pump outlet end exports high pressure solution (ozone) air water.
In ozone and sewage mixing device, the inlet pipe between ozonizer and Venturi liquid gas combining nozzle is provided with check valve, oppositely enters ozonizer with bilge water resisting.
In ozone and sewage mixing device, the adjustment of ozone flow is to meet saturated dissolved gas institute air demand under mixing pump output pressure for the upper limit, and exceed this saturated tolerance and gas-liquid mixing pump output pressure will be caused to decline, even fluid stops flowing.
Under high pressure, photochemical catalysis oxidation reaction apparatus is by high pressure dissolving and the water inlet interface that is contained in outside tank, the release valve of water outlet mouthpiece, tensimeter, rate of discharge variable valve, water sampling valve, dissolved air water transfer lime, tank top automatic blow off valve valve air relief, backflow tracheae, pot bottom, is contained in the compositions such as the ultraviolet lamp in tank, light-sensitive catalyst.
Under high pressure, the working process of photochemical catalysis oxidation reaction apparatus is: the dissolution of contaminated water under high pressure has the ozone higher than meltage saturated under normal pressure, under UV-light and UV sensitive catalyst environment, ozone oxidation reaction can produce the stronger hydroxyl radical free radical of a large amount of oxidation susceptibility, be equipped with other oxydised component, as ozone ion, dissolved oxygen molecule etc., obtain stronger oxidation capacity and oxidation rate faster.
Under high pressure in photochemical catalysis oxidation reaction apparatus, catalyzer should have large surface-area, and to facilitate the sewage of irradiating ultraviolet light and contact flow, catalyzer can exist with the form of coating form and filler, is not subject to the restriction of concrete existence form and shape.
Under high pressure in photochemical catalysis oxidation reaction apparatus, the automatic vent valve air gate that top is installed connects a backflow tracheae, backflow tracheae is confluxed by threeway and oxygen conveying pipe, and in reaction unit, a small amount of oxygen overflowed is used again, and device systems runs and realizes gas-tight.
Under high pressure in photochemical catalysis oxidation reaction apparatus, the generation of tank pressure and maintain by tensimeter, go out water regulating valve and air input variable valve (oxygen flow meter) completes jointly, tensimeter not only shows pressure, also be the foundation that air input regulates: display pressure when air input is zero is maximum, when air input excess, display pressure can sharply decline, and when pressure-stabilisation is in the level a little less than top pressure, air input is appropriate.
Continuity reaction microbubble aerating apparatus is made up of high-pressure sewage Outlet Pipe and micro bubble releasing device, and wherein transfer lime gos deep into the former container bottom of sewage, and transfer lime head installs one or one group of micro bubble releasing device.
The working process of continuity reaction microbubble aerating apparatus is: high pressure dissolved air water is by micro bubble releasing device to sewage water bottom release dissolved air water, and in high pressure dissolved air water, dissolved gases overflows and is crashed to pieces into the bubble of micro-or nano size under the effect of reliever turbulence structure.The long-time disperse of microbubble is in the middle of water body, and the oxygen in bubble, ozone continue to dissolve to water body, add in reaction unit and to produce and the hydroxyl radical free radical retained continues its oxidation reaction process in water body.
The micro bubble releasing device of continuity reaction microbubble aerating apparatus excites turbulent flow moving and vibration, and in order to smash the tuyere arrangement of bubble, the present invention adopts vibration two-slices series of holes structure release device, but is not limited to use this reliever.
The vibration two-slices series of holes structure release device that continuity reaction microbubble aerating apparatus adopts is made up of the same size thin slice orifice plate of reliever main body, installation sealing-ring, front and back arranged in co-axial alignment, the elastic seal ring providing sealing and interval to support for orifice plate and scatterer.High pressure dissolved air water is by producing fixing high-frequency vortex street after vertical orifice plate, vortex street two orifice plates between the high frequency oscillation of dissolved air water by producing during the first orifice plate, the partition adjustable space initiation of this concussion between two orifice plates is resonated and continues and strengthen this resonance, separate out in saturated dissolved gas earthquake under high pressure, smashed by concussion again and become microbubble, microbubble enters water body with current by scatterer, and undersaturation sewage water body will continue the oxidizing gas absorbing and dissolve in bubble.
Beneficial effect:
1) ozone is without waste.The ozone of gaseous phase is easy to reduction after generation becomes oxygen, and after ozone generation, direct and sewage mixing, at utmost can utilize ozone;
2) oxidation efficiency is improved.The rotation of gas-liquid mixing pump quick runner is pressurization is also mixing process.Gas-liquid mixed supercharging can make the pressure ratio of liquids and gases, and kinetic energy ratio and potential energy ratio etc. change.Now, ozone forms a large amount of microbubbles, and gas diameter is 0.2-0.3um, therefore O 3suddenly increase with the contact area of water, the total area is higher than general bubble by 10 3-10 4doubly, O 3dissolution rate significantly improve, so water outlet is in high pressure saturated dissolved gas state substantially.In high pressure dissolving, in water, molten ozone amount is sufficient, is conducive to oxidation reaction;
3) increase oxidation capacity, improve oxidation rate.Under the katalysis of ultraviolet lamp and photosensitizing chemical catalyzer, generate the hydroxyl radical free radical that a large amount of oxidation susceptibility is stronger, the hydroxyl radical free radical that the oxygen molecule dissolved in water, ozone ion and activity are stronger and Components of Organic Pollutants close contact in the liquid phase, not only increase oxidation capacity, and improve oxidation rate.
4) catalyst choice leeway is large.Catalyzer or the optionally catalyzer of broad spectrum suitably can be selected according to pollutant type.By appropriately combined, the eutrophy sewage of common Nitrogen-and Phosphorus-containing, chemical dye sewage etc. can not only be processed, the reluctant trade effluent that agricultural chemicals, hormone and electroplating wastewater, percolate etc. are generally acknowledged can also be processed.
5) ozone utilization rate is high, consumption is little.Due to gas-liquid two-phase simultaneously and suck gas-liquid mixing pump continuously, mixing pump does not allow to suck excess air, and gas exceedes saturated dissolved gas, and pump pressure will be caused to reduce even flow is zero; This characteristic using saturated quantity of dissolved gas as restricted condition of gas-liquid mixing pump has also achieved the feature that ozone utilization rate of the present invention is high, air consumption is little.
6) subsidiary stink is little.Due to inexcessive use ozone, the sewage smells also corresponding minimizing that ozone taste and band carry;
7) oxidizing reaction is lasting, sphere of action is large.The ozone of saturated dissolving under high pressure produces microbubble aeration under reliever effect in normal pressure waste water container, and microbubble is that milk state spreads in water body, and ozone continues to dissolve to undersaturation water body, and ozone oxidation reaction still proceeds in water body.
8) non-secondary pollution thing.Deep oxidation water treatment method only introduces a kind of material of oxygen.Only can react and generate oxidizing gas, oxide precipitation and water, can not secondary pollution be produced.
9) volumetric efficiency is high.Device systems is simple, and function is concentrated.So volume is little, function is strong.
10) use flexibly.Both can separately as the deep oxidation method and apparatus of process chemical organic compounds waste water, also as the pre-treating process of biological treatment of sewage, necessary reduction organic contamination substrate concentration can be provided for subsequent bio water technology and weaken anticipating of chemical toxicity.
Accompanying drawing explanation
Accompanying drawing 1 is equipment composition and the treatment scheme schematic diagram of deep oxidation water treatment method embodiment;
Accompanying drawing 2 is the longitudinal cross-section sectional views along axis for dissolved air water micro bubble releasing device;
Embodiment
Below in conjunction with accompanying drawing 1 and specific embodiment, technical solution of the present invention is described in detail, further to understand object of the present invention, scheme and effect.
Deep oxidation water treatment device is made up of photochemical catalysis oxidation reaction apparatus under ozone and sewage mixing device, high pressure and continuity reaction microbubble aerating apparatus.
In described ozone and sewage mixing device, oxygen sends into oxygen conveying pipe (4) from source of oxygen (1) after reducing valve (2) decompression and oxygen flow meter (3) adjust flux, ozonizer (5) changes the oxygen sent to (partly) into ozone sends ozone transfer lime (6) to, the entrance end of gas-liquid mixing pump (9) is equipped with the combining nozzle (8) of Venturi tube structure, Venturi mixes valve inspiration sewage under mixing pump suction function, be located at bore little, the inlet mouth at the water flow section place that flow rate of water flow is fast also produces larger negative-pressure sucking.The ozone of ozone transfer lime mixes with sewage continuously according to the flow regulated.The rotation of mixing pump quick runner is pressurization is also mixing process, and gas-liquid mixed supercharging can make the pressure ratio of liquids and gases, and kinetic energy ratio and potential energy ratio etc. change.Now, ozone forms a large amount of microbubbles, and gas diameter is 0.2-0.3um, therefore O 3suddenly increase with the contact area of water, the total area is higher than general bubble by 10 3-10 4doubly, O 3dissolution rate significantly improve, so water outlet is in high pressure saturated dissolved gas state substantially.Inlet pipe between ozonizer and Venturi liquid gas combining nozzle is provided with check valve, oppositely enters ozonizer with bilge water resisting.In ozone and sewage mixing device, the adjustment of ozone flow is to meet saturated dissolved gas institute air demand under mixing pump output pressure for the upper limit, and exceed this saturated tolerance and gas-liquid mixing pump output pressure will be caused to decline, even fluid stops flowing.Concrete operations are then the vision-control airsheds according to tensimeter (16).
Under high pressure in photochemical catalysis oxidation reaction apparatus, high pressure dissolved air water enters high pressure dissolving (12) by water inlet interface (11).The UV-light that the ultraviolet lamp (13) installed in tank sends and light-sensitive catalyst (14) produce photochemical reaction to the sewage with high molten ozone amount (under high pressure, the molten tolerance of water saturation is the several times under normal pressure) entered in tank.Ozone oxidizing reaction under the katalysis of UV-light produces great amount of hydroxy group free radical, the redox potential of hydroxyl radical free radical is 2.8V, higher than the 2.07V of ozone, it can make the contaminant molecule splitting of chain in sewage, and therefore under high pressure, photocatalysis oxidation reaction has stronger oxidation capacity.Sewage in high pressure dissolving is still in flow state, and water outlet mouthpiece (15) is connected to tensimeter (16) and rate of discharge variable valve (17), in order to regulate and to maintain the pressure in tank.For convenience of monitoring, between variable valve and dissolving, be provided with water sampling valve (18); The top of dissolving is provided with automatic blow off valve valve air relief (19), purging valve outlet is connected to backflow tracheae (20), a small amount of non-dissolved oxygen gas that dissolved air water overflows enters backflow tracheae (20), confluxed by threeway and oxygen hose (4) and get back to ozonizer (5) and be again used, device systems runs and realizes No leakage.Be provided with release valve (21) bottom dissolving, facilitate cleaning operation.Under high pressure, the working process of photochemical catalysis oxidation reaction apparatus is: under dissolving (12) inner high voltage, the ozone of high saturated meltage contacts with UV sensitive catalyst (14) oxidizing reaction occurred in ultraviolet lamp (13) irradiate light and can produce the stronger hydroxyl radical free radical of a large amount of oxidation susceptibility, with other oxydised component, as ozone, dissolved oxygen molecule etc. participate in oxidizing reaction together, obtain stronger oxidation capacity and oxidation rate.
In described continuity reaction microbubble aerating apparatus, the molten gas sewage of being released by rate of discharge variable valve (17) enters high-pressure sewage Outlet Pipe (22), the water bottom of the former container of sewage (23) is imbedded in Outlet Pipe outlet, and transfer lime head installs one or one group of micro bubble releasing device (24).Micro bubble releasing device excites turbulent flow moving and vibration, and in order to smash the tuyere arrangement of bubble, the reliever of the vibration two-slices series of holes structure that the present invention adopts can produce microbubble.Fig. 2 is the reliever structure of a kind of two-slices series of holes structure that the present invention adopts.Reliever is at sewage water body release dissolved air water, and the molten gas in current is that gaseous state overflows and is crashed to pieces by turbulence driver, presents microbubble and spreads in water body and continue its aerating oxidation behavior.Sewage in waste water container can through device circular treatment of the present invention, until water treatment quality reaches the quality level of expectation for it.
The dissolved air release sectional view that the present invention by reference to the accompanying drawings shown in 2 adopts is described in detail.The reliever that the present invention adopts is made up of the same size thin slice orifice plate (26) of reliever main body (24), installation sealing-ring (25), front and back arranged in co-axial alignment, the elastic seal ring (27) providing sealing and interval to support for orifice plate and scatterer (28).Water is by producing the vortex street of fixed frequency after vertical orifice plate, vortex street high frequency oscillation between two orifice plates that dissolved air water is produced by the first orifice plate (26), resonance and continuity are easily caused in the partition adjustable space of this concussion between two orifice plates, separate out in the molten gas earthquake of hypersaturated state, smashed by concussion again and become microbubble, microbubble enters water body with current by scatterer (28), and undersaturation sewage water body will continue the oxidizing gas absorbing and dissolve in bubble.

Claims (15)

1. the water treatment method of a deep oxidation and device, it is characterized in that, water treatment procedure is divided into three sections, and order completes in three kinds of devices, and they are photochemical catalysis oxidation reaction apparatus and continuity reaction microbubble aerating apparatus under ozone and sewage mixing device, high pressure respectively.
2. the water treatment method of deep oxidation as claimed in claim 1 and device, it is characterized in that, described ozone and sewage mixing device are made up of source of oxygen and the reducing valve of attaching troops to a unit, oxygen flow meter, oxygen conveying pipe, ozonizer, gas-liquid mixing pump, Venturi liquid gas combining nozzle etc.
3. the water treatment method of deep oxidation as claimed in claim 1 and device, it is characterized in that, the working process of described ozone and sewage mixing device is, gas-liquid mixed mouth inspiration simultaneously sewage and the ozone that have adjusted flow of Venturi tube structure, gas-liquid mixing pump quick runner smashes the molten ozone water of the high molten ozone amount of bubble formation, and pump outlet end exports high pressure solution (ozone) air water.
4. the water treatment method of deep oxidation as claimed in claim 1 and device, it is characterized in that, in described ozone and sewage mixing device, the inlet pipe between ozonizer and Venturi liquid gas combining nozzle is provided with check valve, oppositely enters ozonizer with bilge water resisting.
5. the water treatment method of deep oxidation as claimed in claim 1 and device, it is characterized in that, in described ozone and sewage mixing device, the adjustment of ozone flow is to meet saturated dissolved gas institute air demand under mixing pump output pressure for the upper limit, exceeding this saturated tolerance will cause gas-liquid mixing pump output pressure to decline, and even fluid stops flowing.
6. the water treatment method of deep oxidation as claimed in claim 1 and device, it is characterized in that, under described high pressure, photochemical catalysis oxidation reaction apparatus is by high pressure dissolving and the water inlet interface that is contained in outside tank, the release valve of water outlet mouthpiece, tensimeter, rate of discharge variable valve, water sampling valve, dissolved air water transfer lime, tank top automatic blow off valve valve air relief, backflow tracheae, pot bottom, is contained in the compositions such as the ultraviolet lamp in tank, light-sensitive catalyst.
7. the water treatment method of deep oxidation as claimed in claim 1 and device, it is characterized in that, under described high pressure, the working process of photochemical catalysis oxidation reaction apparatus is: the dissolution of contaminated water under high pressure has the ozone higher than meltage saturated under normal pressure, under UV-light and UV sensitive catalyst environment, ozone oxidation reaction can produce the stronger hydroxyl radical free radical of a large amount of oxidation susceptibility, with other oxydised component, as ozone ion, dissolved oxygen molecule etc. participate in oxidizing reaction together, obtain stronger oxidation capacity and oxidation rate faster.
8. the water treatment method of deep oxidation as claimed in claim 1 and device, it is characterized in that, under described high pressure in photochemical catalysis oxidation reaction apparatus, catalyzer should have large surface-area, facilitate the sewage of irradiating ultraviolet light and contact flow, catalyzer can exist with the form of coating form and filler, is not subject to the restriction of concrete existence form and shape.
9. the water treatment method of deep oxidation as claimed in claim 1 and device, it is characterized in that, under described high pressure in photochemical catalysis oxidation reaction apparatus, the automatic vent valve air gate that top is installed connects a backflow tracheae, backflow tracheae is confluxed by threeway and oxygen conveying pipe, in reaction unit, a small amount of oxygen overflowed is used again, and device systems runs and realizes gas-tight.
10. the water treatment method of deep oxidation as claimed in claim 1 and device, it is characterized in that, under described high pressure in photochemical catalysis oxidation reaction apparatus, the generation of tank pressure and maintain by tensimeter, go out water regulating valve and air input variable valve (oxygen flow meter) completes jointly, tensimeter not only shows pressure, also be the foundation that air input regulates: display pressure when air input is zero is maximum, when air input exceedes saturated dissolved gas amount, display pressure can sharply decline, when pressure-stabilisation is in the level a little less than top pressure, air input is appropriate.
The water treatment method of 11. deep oxidations as claimed in claim 1 and device, it is characterized in that, described continuity reaction microbubble aerating apparatus is made up of high-pressure sewage Outlet Pipe and micro bubble releasing device, wherein transfer lime gos deep into the former container bottom of sewage, and transfer lime head installs one or one group of micro bubble releasing device.
The water treatment method of 12. deep oxidations as claimed in claim 1 and device, it is characterized in that, the working process of described continuity reaction microbubble aerating apparatus is: high pressure dissolved air water is by micro bubble releasing device to sewage water bottom release dissolved air water, and in high pressure dissolved air water, dissolved gases overflows and is crashed to pieces into the bubble of micro-or nano size under the effect of reliever turbulence structure.The long-time disperse of microbubble is in the middle of water body, and the oxygen in bubble, ozone continue to dissolve to water body, add in reaction unit and to produce and the hydroxyl radical free radical retained continues its oxidation reaction process in water body.
The water treatment method of 13. deep oxidations as claimed in claim 1 and device, it is characterized in that, the micro bubble releasing device of described continuity reaction microbubble aerating apparatus excites turbulent flow moving and vibration, in order to smash the tuyere arrangement of bubble, the present invention adopts vibration two-slices series of holes structure release device, but is not limited to use this reliever.
The water treatment method of 14. deep oxidations as claimed in claim 1 and device, it is characterized in that, the vibration two-slices series of holes structure release device that described continuity reaction microbubble aerating apparatus adopts is made up of the same size thin slice orifice plate of reliever main body, installation sealing-ring, front and back arranged in co-axial alignment, the elastic seal ring providing sealing and interval to support for orifice plate and scatterer.
The water treatment method of 15. deep oxidations as claimed in claim 1 and device, it is characterized in that, the principle of work of the vibration two-slices series of holes structure release device that described continuity reaction microbubble aerating apparatus adopts is: high pressure dissolved air water is by producing fixing high-frequency vortex street after vertical orifice plate, vortex street high frequency oscillation between two orifice plates that dissolved air water is produced by the first orifice plate, the partition adjustable space initiation of this concussion between two orifice plates is resonated and continues this resonance, separate out in saturated dissolved gas earthquake under high pressure, smashed by concussion again and become microbubble, microbubble enters water body with current by scatterer, undersaturation sewage water body will continue the oxidizing gas absorbing and dissolve in bubble, continue its oxidation behavior.
CN201510208520.6A 2015-04-29 2015-04-29 Deep oxidization water treatment method and deep oxidization water treatment device Pending CN104876375A (en)

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Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007083207A (en) * 2005-09-26 2007-04-05 Fuji Electric Systems Co Ltd Accelerated oxidized water treatment method and apparatus
CN102060370A (en) * 2010-12-03 2011-05-18 沈阳工业大学 Method for rapid disinfection of medical wastewater
CN102755846A (en) * 2012-07-28 2012-10-31 甘肃金桥给水排水设计与工程(集团)有限公司 Micro-bubble dissolved air generation device
CN103880231A (en) * 2014-04-04 2014-06-25 王忠岱 Zero-discharge treatment method of oily water of ship

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007083207A (en) * 2005-09-26 2007-04-05 Fuji Electric Systems Co Ltd Accelerated oxidized water treatment method and apparatus
CN102060370A (en) * 2010-12-03 2011-05-18 沈阳工业大学 Method for rapid disinfection of medical wastewater
CN102755846A (en) * 2012-07-28 2012-10-31 甘肃金桥给水排水设计与工程(集团)有限公司 Micro-bubble dissolved air generation device
CN103880231A (en) * 2014-04-04 2014-06-25 王忠岱 Zero-discharge treatment method of oily water of ship

Cited By (16)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105645509A (en) * 2016-01-11 2016-06-08 汤奇岳 Green energy water, and preparation device, method and application thereof
CN106865689A (en) * 2017-04-10 2017-06-20 佛山科学技术学院 The photocatalysis treatment device and processing method of a kind of percolate
CN111115788B (en) * 2018-10-30 2023-04-07 中国石油化工股份有限公司 Treatment method of quenching wastewater in acrylonitrile production process
CN111115788A (en) * 2018-10-30 2020-05-08 中国石油化工股份有限公司 Treatment method of quenching wastewater in acrylonitrile production process
CN113905809A (en) * 2019-03-28 2022-01-07 恩博特系统有限责任公司 Gas injection system for optimizing nanobubble formation in disinfection solutions
CN113905809B (en) * 2019-03-28 2024-12-03 恩博特系统有限责任公司 Gas injection system for optimizing nanobubble formation in disinfectant solutions
CN110759456A (en) * 2019-11-04 2020-02-07 重庆环益科技有限公司 Hydrogen feeding method for swimming pool, hot spring and bathing circulating water system
CN111573929A (en) * 2020-04-26 2020-08-25 北京中矿未来科技集团有限公司 O-shaped catalyst3Photocatalytic advanced oxidation high-concentration wastewater reaction system and method
CN111573815A (en) * 2020-04-30 2020-08-25 浙江缘森生态环境科技有限公司 Advanced oxidation wastewater treatment device and method capable of achieving disinfection and sterilization
CN112704181A (en) * 2020-12-31 2021-04-27 瑞泽生物科技(苏州)有限公司 Vegetable and fruit pesticide degradation machine
CN112897756A (en) * 2021-02-01 2021-06-04 浙江省淡水水产研究所 Floating feed salvaging and sterilizing device in aquaculture pond
CN113428967A (en) * 2021-07-13 2021-09-24 中科合成油内蒙古有限公司 Multi-dimensional advanced oxidation organic wastewater advanced treatment method and system
CN114380385A (en) * 2022-01-21 2022-04-22 长沙市森蓝环境工程有限公司 Sewage treatment device and method
CN115043456A (en) * 2022-07-01 2022-09-13 安徽天柱绿色能源科技有限公司 Photocatalytic oxidation sewage treatment device and sewage treatment method thereof
CN115159666A (en) * 2022-07-26 2022-10-11 中钢集团武汉安全环保研究院有限公司 Black and odorous water body treatment device
CN115159666B (en) * 2022-07-26 2023-09-15 中钢集团武汉安全环保研究院有限公司 Black and odorous water body treatment device

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Application publication date: 20150902