CN106830283B - A kind of drinking water sterilization device of ceramic membrane coupling ozone catalytic - Google Patents

A kind of drinking water sterilization device of ceramic membrane coupling ozone catalytic Download PDF

Info

Publication number
CN106830283B
CN106830283B CN201710083072.0A CN201710083072A CN106830283B CN 106830283 B CN106830283 B CN 106830283B CN 201710083072 A CN201710083072 A CN 201710083072A CN 106830283 B CN106830283 B CN 106830283B
Authority
CN
China
Prior art keywords
ceramic membrane
catalyst
ozone
water
gas
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN201710083072.0A
Other languages
Chinese (zh)
Other versions
CN106830283A (en
Inventor
许柯
温舒涵
任洪强
耿金菊
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Nanjing University
Original Assignee
Nanjing University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Nanjing University filed Critical Nanjing University
Priority to CN201710083072.0A priority Critical patent/CN106830283B/en
Publication of CN106830283A publication Critical patent/CN106830283A/en
Application granted granted Critical
Publication of CN106830283B publication Critical patent/CN106830283B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/78Treatment of water, waste water, or sewage by oxidation with ozone
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D67/00Processes specially adapted for manufacturing semi-permeable membranes for separation processes or apparatus
    • B01D67/0039Inorganic membrane manufacture
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D69/00Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor
    • B01D69/10Supported membranes; Membrane supports
    • B01D69/105Support pretreatment
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D71/00Semi-permeable membranes for separation processes or apparatus characterised by the material; Manufacturing processes specially adapted therefor
    • B01D71/02Inorganic material
    • B01D71/024Oxides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/74Iron group metals
    • B01J23/75Cobalt
    • B01J35/59
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/50Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/725Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds

Abstract

The invention discloses a kind of drinking water sterilization devices of ceramic membrane coupling ozone catalytic, the device includes ozone generating-device, gas flowmeter, raw water vessel, fluid flowmeter, gas-liquid mixing pump, reaction vessel, catalyst couples ceramic membrane, reflux unit, discharging device, air pressure regulator, back purge system, gas-liquid mixing pump is used for the mixing of ozone and drinking water to be sterilized in the device of the invention, it can be improved the utilization rate of ozone, ozone oxidation is promoted using catalyst coupling ceramic membrane, improve disinfection efficiency, using reflux unit, discharging device, air pressure regulator, back purge system rationalizes overall structure more.

Description

A kind of drinking water sterilization device of ceramic membrane coupling ozone catalytic
Technical field
The present invention relates to drinking water disinfection field of purification, in particular to mention the one of mark discharge for waterworks water quality The drinking water sterilization device of kind ceramic membrane coupling ozone catalytic.
Background technique
In recent years, China's water supply industry mentions mark and discharges always among schedule.Typical environment water and dirt in China Antibiotic, disinfection by-products, drug and personal care articles (PPCPs) in water treatment plant's waste discharge, incretion interferent and The exceeded report of the toxic Recalcitrant chemicals of other persistence emerges one after another, and greatly threatens aquatic ecological safety and human body is strong Health.The Committee of Experts, Chinese city sewage treatment concept factory is by erythromycin, sulfamethoxazole, Diclofenac, brufen, Luo Hong Mycin, 7 kinds of estrogen (poisonous effect equivalent) endangered with latency environment and the novel organic micro-pollutants that are difficult to degrade are classified as Science in Future in China water quality manages target, among concerned countries policy is also being bred.The common technology stream of China waterworks at present Journey is flocculation, sand coarse aggregate ratio, disinfection (chlorination, UV or ozone), and conventional processes remove dissolved organic matter, ammonia nitrogen, two worms etc. Ineffective, effluent quality has been unable to satisfy needs, and drinking water safety problem is extremely urgent, faces the need of technique upgrading It asks.
With the reduction of film product price and the maturation of membrane technology, application of the ultrafiltration membrane in drinking water treatment is increasingly Extensively, ultrafiltration membrane can effectively remove turbidity, particle and bacterium in water, and occupied area is small, high degree of automation.Common oxidation technology Micro-polluted raw is handled, and currently used ultrafiltration membrane is the organic polymer film for being unable to resistance to oxidation, therefore is split and answered using series connection For in each treatment process, ultrafiltration membrane to be often placed in process flow end, it is only capable of the barrier removed as microorganism, film skill at this time The advantage of art fails to embody.Compared with organic film, ceramic membrane energy resistance to oxidation, have high mechanical strength, membrane aperture narrow distribution range, The advantages that long service life, can couple use with oxidation technology.But it is film that membrane process, which applies to actual another biggest obstacle, Pollution is mainly shown as that filtration resistance increases and permeation flux reduces.
Ozonation technology is an environmentally friendly technology, can be H by some of the contaminants permineralization2O and CO2, so And its oxidisability has high selectivity.Catalytic ozonation belongs to high-level oxidation technology, is produced using catalyst Free hydroxyl, hardly degraded organic substance in enhancing degradation water are given birth to, carbon drop decoloring ability is significantly higher than simple ozone oxidation, has drop The features such as high-efficient, environmental-friendly is solved, cost is also below simple ozone oxidation.
Therefore, catalytic ozonation technology and Ceramic Membranes Separating Technique coupling will maximumlly be utilized into ceramic membrane and catalysis The effect of ozonisation, catalytic ozonation can be reacted with former Organic substance in water, changed organic constitution, be can solve ceramic membrane film Problem easily short by dirty, service life, while being also able to solve catalyst in catalytic ozonation technology and being difficult to the problem of recycling.
" multiple sterilizing filtration water purifier " disclosed in CN2586692, using the strong oxidation of ozone, oxidation is killed in water Various bacteria microorganism, removal organic matter, but its ozone utilization efficiency is low, and drinking mainly for the production of water dispenser Water." a kind of deep-purifying method for removing soluble pollutants in drinking water " disclosed in CN103274547A uses ceramic membrane mistake Filter, ozone oxidation organic matter macromolecular are after small molecule by molecular screen membrane advanced treating drinking water, but its ceramic membrane and ozone Reaction unit takes up a large area, and ozone utilization efficiency is low.
Summary of the invention
The technical problem to be solved by the present invention is to provide a kind of drinking water sterilization devices of ceramic membrane coupling ozone catalytic, go out Various bacteria microorganism, removal organic matter in water, and can be improved ozone utilization rate.
Technical scheme is as follows:
A kind of drinking water sterilization device of ceramic membrane coupling ozone catalytic, including ozone generating-device, gas flowmeter, original Water container, fluid flowmeter, gas-liquid mixing pump, reaction vessel, catalyst couple ceramic membrane, reflux unit, discharging device, air pressure Regulating device, back purge system, the ozone generating-device, raw water vessel connect gas-liquid mixing pump by pipeline, described Catalyst coupling ceramic membrane is placed in reaction vessel interior, and the reflux unit, discharging device are placed on reaction vessel side wall, institute The air pressure regulator stated is placed in the upper cover position of reaction vessel.
Further, catalyst coupling ceramic membrane includes at least two ceramic membranes and catalyst, the ceramics Film loads cobalt oxide by infusion process, and the method by coating prepares catalyst coat in ceramic membrane surface, and building is three-dimensional more Grade catalytic carrier, it is more thorough to the catalysis oxidation of drinking water.
Further, the ceramic membrane is butterfly structure, with a thickness of 0.8-1.2mm, overall diameter 1.2-2cm, on film There is fenestra, fenestra aperture is 100-500nm, improves the disinfection efficiency of drinking water.
Further, the ceramic membrane the preparation method comprises the following steps:
(1) raw material are used are as follows: partial size is the TiO of 0.1-0.3um290-95 parts of powder, NH4HCO31-5 parts, asphalt mixtures modified by epoxy resin 0.5-5 parts of rouge, 0.5-5 parts of silica after mixing by raw material in high-temperature electric resistance furnace, adjust the temperature to 1200-1400 DEG C, 4-6h is fired, Temperature fall obtains supporter, spare;
(2) TiSO for being 0.4-0.8mol/L to concentration42Middle addition glycerol, makes glycerol concentration 0.1-0.4mol/L, makes Use H2SO4Or NH3·H2It is 5.5-8.5 that O, which adjusts pH value, is heated to 60-90 DEG C, and sodium phosphate is added, obtains film liquid, spare;
(3) film liquid made from step 2 is coated to the supporting body surface prepared to step 1, with a thickness of 10-100um, is placed in It on matter machine turntable, after revolving speed 2000-4000r/min, 1-5min, is placed in high-temperature electric resistance furnace, adjusts 400-500 DEG C of temperature, 5- After 10min, ceramic film is obtained, is repeated 3-5 times;
(4) step 3 gained ceramic film is placed in high-temperature electric resistance furnace, 1200-1400 DEG C of temperature of adjusting, after 4-6h, must be made pottery Porcelain film.
Further, the catalyst is Co-Ti composite oxides, improves ozone catalytic efficiency, makes Disinfection Effect more It is good.
Further, the Co-Ti composite oxides the preparation method comprises the following steps: being added 6 parts of titanium tetraisopropylates to 75 DEG C 100 parts of water in, 1-2 part concentrated nitric acids are added after being completely dissolved, 4-10 parts of cobalt nitrate hexahydrates, stirring 25- are added after 1-2h 35min obtains Co-Ti plural gel, in 50-70 environment after drying for 24 hours, calcines in Muffle furnace, controlled at 300-500 DEG C, after 3-5h, obtain Co-Ti composite oxides.
Further, the reflux unit includes return pipe, reflux pump, return line flow meter, will be that disinfection is complete Drinking water recycles again, and the discharging device includes pressure gauge, water outlet pump, and registration on pressure gauge is arranged, will by water outlet pump Water extraction after sterilizing in device, the air pressure regulator include gas gauge, air pump, and air pressure is flat in regulating device Weighing apparatus, back purge system include recoil flowmeter, backwash water tank, air compression box, and catalyst couples ceramic membrane in cleaning device.
Further, the raw water vessel and pipeline are connected by stainless steel pipes, internal passivated processing, Prevent corrosion of the substance to device in water.
Beneficial effects of the present invention: gas-liquid mixing pump is used to reduce ozone and drinking water than fusion, with appropriate in device The waste of ozone;Ozone is promoted to eliminate the mushroom in water using catalyst coupling ceramic membrane in catalytic process, to having Machine object is aoxidized, and disinfecting time is reduced;Catalyst, which couples, uses TiO used in ceramic membrane2For support body material, in light Organic matter is promoted to decompose according under conditions of, the preparation process of ceramic membrane is simple, at low cost;Co-Ti composite oxides are used to urge Agent is coated on ceramic membrane, improves the disinfection efficiency of drinking water, and significant effect;The principle of the invention is simple, low cost, High efficiency, low energy consumption and generates without other pollutants.
Detailed description of the invention
Fig. 1 is the drinking water sterilization device structural schematic diagram that a kind of ceramic membrane of the invention couples ozone catalytic.
Wherein, 1- ozone generating-device, 2- gas flowmeter, 3- raw water vessel, 4- fluid flowmeter, 5- gas-liquid mixed Pump, 6- reaction vessel, 7- catalyst coupling ceramic membrane, 8- reflux unit, 9- discharging device, 10- air pressure regulator, 11- are anti- Flusher.
Specific embodiment
With reference to embodiment come to the present invention be further described in detail:
As shown in Figure 1, a kind of drinking water sterilization device of ceramic membrane coupling ozone catalytic, which is characterized in that including ozone Generating device 1, gas flowmeter 2, raw water vessel 3, fluid flowmeter 4, gas-liquid mixing pump 5, reaction vessel 6, catalyst coupling Ceramic membrane 7, reflux unit 8, discharging device 9, air pressure regulator 10, back purge system 11, ozone generating-device 1, raw water are held Device 3 connects gas-liquid mixing pump 7 by pipeline, and catalyst coupling ceramic membrane 7 is placed in inside reaction vessel 6, reflux unit 8, water outlet Device 9 is placed on 6 side wall of reaction vessel, and air pressure regulator 10 is placed in the upper cover position of reaction vessel 6.
Raw water vessel 3 and pipeline are connected by stainless steel pipes, internal passivated processing.
Catalyst couples ceramic membrane 7: including at least two ceramic membranes and catalyst, ceramic membrane is loaded by infusion process and is aoxidized Cobalt, and the method by coating prepares catalyst coat in ceramic membrane surface, constructs three-dimensional multistage catalytic carrier.Ceramic membrane is butterfly Shape structure, with a thickness of 0.8-1.2mm, overall diameter 1.2-2cm has fenestra on film, and fenestra aperture is 100-500nm.Catalyst For Co-Ti composite oxides, Co-Ti composite oxides the preparation method comprises the following steps: being added 6 parts of titanium tetraisopropylates to the 100 of 75 DEG C In part water, 1-2 parts of concentrated nitric acids are added after being completely dissolved, 4-10 parts of cobalt nitrate hexahydrates are added after 1-2h, stirs 25-35min, obtains Co-Ti plural gel, in 50-70 environment it is dry for 24 hours after, calcined in Muffle furnace, controlled at 300-500 DEG C, 3-5h Afterwards, Co-Ti composite oxides are obtained.
Ceramic membrane the preparation method comprises the following steps:
(1) raw material are used are as follows: partial size is the TiO of 0.1-0.3um290-95 parts of powder, NH4HCO31-5 parts, asphalt mixtures modified by epoxy resin 0.5-5 parts of rouge, 0.5-5 parts of silica after mixing by raw material in high-temperature electric resistance furnace, adjust the temperature to 1200-1400 DEG C, 4-6h is fired, Temperature fall obtains supporter, spare;
(2) TiSO for being 0.4-0.8mol/L to concentration42Middle addition glycerol, makes glycerol concentration 0.1-0.4mol/L, makes Use H2SO4Or NH3·H2It is 5.5-8.5 that O, which adjusts pH value, is heated to 60-90 DEG C, and sodium phosphate is added, obtains film liquid, spare;
(3) film liquid made from step 2 is coated to the supporting body surface prepared to step 1, with a thickness of 10-100um, is placed in It on matter machine turntable, after revolving speed 2000-4000r/min, 1-5min, is placed in high-temperature electric resistance furnace, adjusts 400-500 DEG C of temperature, 5- After 10min, ceramic film is obtained, is repeated 3-5 times;
(4) step 3 gained ceramic film is placed in high-temperature electric resistance furnace, 1200-1400 DEG C of temperature of adjusting, after 4-6h, must be made pottery Porcelain film.
Reflux unit 8: including return pipe, reflux pump, return line flow meter.
Discharging device 9: including pressure gauge, water outlet pump.
Air pressure regulator 10: including gas gauge, air pump, back purge system 15 includes recoil flowmeter, backwash Water tank, air compression box.
Finally, it should be noted that the above embodiments are merely illustrative of the technical solutions of the present invention, rather than its limitations;Although Present invention has been described in detail with reference to the aforementioned embodiments, those skilled in the art should understand that: it still may be used To modify to technical solution documented by previous embodiment or equivalent replacement of some of the technical features;And These are modified or replaceed, the spirit and model of technical solution of the embodiment of the present invention that it does not separate the essence of the corresponding technical solution It encloses.

Claims (1)

1. a kind of drinking water sterilization device of ceramic membrane coupling ozone catalytic, which is characterized in that including ozone generating-device (1), Gas flowmeter (2), raw water vessel (3), fluid flowmeter (4), gas-liquid mixing pump (5), reaction vessel (6), catalyst coupling Ceramic membrane (7), reflux unit (8), discharging device (9), air pressure regulator (10), back purge system (11), the ozone Generating device (1), raw water vessel (3) connect gas-liquid mixing pump (5) by pipeline, and catalyst coupling ceramic membrane (7) is set In reaction vessel (6) inside, the reflux unit (8), discharging device (9) are placed on reaction vessel (6) side wall, the gas Pressure regulating device (10) is placed in the upper cover position of reaction vessel (6), and the back purge system (11) is connected to reaction vessel (6) Bottom end;Catalyst coupling ceramic membrane (7) includes at least two ceramic membranes and catalyst, and the ceramic membrane passes through leaching Stain method loads cobalt oxide, and the method by coating prepares catalyst coat in ceramic membrane surface, constructs three-dimensional multistage catalytic and carries Body;The ceramic membrane is butterfly structure, and with a thickness of 0.8-1.2mm, overall diameter 1.2-2cm has fenestra, fenestra aperture on film For 100-500nm;The ceramic membrane the preparation method comprises the following steps:
(1) raw material are used are as follows: the TiO that partial size is 0.1-0.3 μm290-95 parts of powder, NH4HCO31-5 parts, epoxy resin 0.5-5 parts, 0.5-5 parts of silica, after mixing by raw material, in high-temperature electric resistance furnace, adjust the temperature to 1200-1400 DEG C, 4-6h is fired, Temperature fall obtains supporter, spare;
(2) Ti (SO for being 0.4-0.8mol/L to concentration4)2Middle addition glycerol makes glycerol concentration 0.1-0.4mol/L, uses H2SO4Or NH3·H2It is 5.5-8.5 that O, which adjusts p H value, is heated to 60-90 DEG C, and sodium phosphate is added, obtains film liquid, spare;
(3) supporting body surface for coating film liquid made from step (2) to step (1) preparation is placed in a thickness of 10-100 μm It on homogenizer turntable, after revolving speed 2000-4000r/min, 1-5min, is placed in high-temperature electric resistance furnace, adjusts 400-500 DEG C of temperature, After 5-10min, ceramic film is obtained, is repeated 3-5 times;
(4) ceramic film obtained by step (3) is placed in high-temperature electric resistance furnace, 1200-1400 DEG C of temperature of adjusting, after 4-6h, is obtained ceramic Film;
The catalyst is Co-Ti composite oxides;The Co-Ti composite oxides the preparation method comprises the following steps: different by 6 part four Titanium propanolate is added into 75 DEG C of 100 parts of water, and 1-2 parts of concentrated nitric acids are added after being completely dissolved, six water nitre of 4-10 part is added after 1-2h Sour cobalt stirs 25-35min, obtains Co-Ti plural gel, in 50-70 environment after drying for 24 hours, calcines in Muffle furnace, controls Temperature is 300-500 DEG C, after 3-5h, obtains Co-Ti composite oxides;
The reflux unit (8) includes return pipe, reflux pump, return line flow meter, and the discharging device (9) includes pressure Meter, water outlet pump, the air pressure regulator (10) include gas gauge, air pump, and back purge system (11) includes recoil stream Meter, backwash water tank, air compression box;
The raw water vessel (3) and pipeline are connected by stainless steel pipes, internal passivated processing.
CN201710083072.0A 2017-02-16 2017-02-16 A kind of drinking water sterilization device of ceramic membrane coupling ozone catalytic Active CN106830283B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710083072.0A CN106830283B (en) 2017-02-16 2017-02-16 A kind of drinking water sterilization device of ceramic membrane coupling ozone catalytic

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710083072.0A CN106830283B (en) 2017-02-16 2017-02-16 A kind of drinking water sterilization device of ceramic membrane coupling ozone catalytic

Publications (2)

Publication Number Publication Date
CN106830283A CN106830283A (en) 2017-06-13
CN106830283B true CN106830283B (en) 2019-10-01

Family

ID=59128218

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710083072.0A Active CN106830283B (en) 2017-02-16 2017-02-16 A kind of drinking water sterilization device of ceramic membrane coupling ozone catalytic

Country Status (1)

Country Link
CN (1) CN106830283B (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109775892A (en) * 2019-03-11 2019-05-21 山东建筑大学 A kind of low energy consumption gravity stream catalytic membrane integral water purifying device and its operation method
CN113443697B (en) * 2021-07-09 2022-10-25 哈尔滨工业大学 Continuous flow device for catalyzing ozone oxidation by multistage membrane module
CN113548758A (en) * 2021-09-22 2021-10-26 山东泰禾环保科技股份有限公司 Method and device for treating drinking water by using ceramic membrane and combined nanofiltration membrane
CN115709069A (en) * 2022-11-11 2023-02-24 淮阴师范学院 Attapulgite-based catalytic membrane, preparation method and application thereof in treatment of sulfamethoxazole-containing water body

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101590403A (en) * 2009-06-11 2009-12-02 上海交通大学 Multifunctional coupling catalyst and preparation method thereof
CN104803512A (en) * 2015-04-21 2015-07-29 大连理工大学 Ozone catalytic oxidation and self-cleaning ceramic membrane combined water treatment method and device
CN105597553A (en) * 2016-03-17 2016-05-25 江苏久吾高科技股份有限公司 Preparation method of ceramic membrane used in membrane absorption process

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101590403A (en) * 2009-06-11 2009-12-02 上海交通大学 Multifunctional coupling catalyst and preparation method thereof
CN104803512A (en) * 2015-04-21 2015-07-29 大连理工大学 Ozone catalytic oxidation and self-cleaning ceramic membrane combined water treatment method and device
CN105597553A (en) * 2016-03-17 2016-05-25 江苏久吾高科技股份有限公司 Preparation method of ceramic membrane used in membrane absorption process

Also Published As

Publication number Publication date
CN106830283A (en) 2017-06-13

Similar Documents

Publication Publication Date Title
CN106830283B (en) A kind of drinking water sterilization device of ceramic membrane coupling ozone catalytic
CN1290774C (en) Continual immersion type processing unit of photocatalysis membrane for removing natural organic matter in water
CN202924850U (en) Advanced wastewater oxidation system
CN102180556A (en) Adsorption regeneration-photocatalysis advanced oxidation water treatment equipment
CN105481154A (en) Ultrafiltration membrane reclaimed water treatment device integrating catalytic oxidation and supported catalyst
CN107963773A (en) Industrial sewage processing unit with waste gas purification function
CN105461045A (en) Ultrafiltration membrane assembly integrating catalytic oxidation and carrying catalyst
CN101085685A (en) Landscape water treatment technology
CN202152309U (en) Complete set of modularized small-scale device for treatment of high-concentration organic wastewater
CN101343128A (en) Movable combined water correction plant
CN201737737U (en) Airflow driving inner circulation photocatalysis cylindrical water treatment device
CN207792867U (en) A kind of ozone ceramics dual-membrane process water treatment facilities
CN101659503A (en) Membrane bioreaction-nanometer fixed state light-catalyzed reaction device
CN101955301B (en) Method and equipment for treating micropollution raw water based on biological bamboo charcoal contact oxidation method
CN112520923A (en) Wastewater treatment method for urea-formaldehyde resin and phenolic resin production enterprises
CN103754982A (en) Photocatalytic water-treatment sterilizing equipment
CN206553335U (en) A kind of new photooxidation catalyzing deodorizing wastewater treatment equipment
CN201288101Y (en) Water treating device for softening, clarifying and filtering lime
CN102616915B (en) Device and method for comprehensively treating water body
CN101811750B (en) Magnetic assist-photolysis composite water purifier and application thereof
CN107487808A (en) A kind of photo-catalyst device
CN109970251A (en) A kind of multistage water treatment system of catalytic ozonation
CN105110501A (en) Multi-term advanced nanometer catalytic wastewater treatment device
CN209662969U (en) Full-automatic exhaust treatment system
CN205222856U (en) Multiple high grade nano catalytic waste water treating device

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant