[go: up one dir, main page]

CN207405000U - A kind of compound advanced oxidation technology handles the device of high COD waste liquids - Google Patents

A kind of compound advanced oxidation technology handles the device of high COD waste liquids Download PDF

Info

Publication number
CN207405000U
CN207405000U CN201721294754.8U CN201721294754U CN207405000U CN 207405000 U CN207405000 U CN 207405000U CN 201721294754 U CN201721294754 U CN 201721294754U CN 207405000 U CN207405000 U CN 207405000U
Authority
CN
China
Prior art keywords
hybrid reaction
reaction tank
photoreactors
inlet
catalytic reactor
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
CN201721294754.8U
Other languages
Chinese (zh)
Inventor
林鸿祥
杨昌友
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.)
Chengdu Environment Technology Co Ltd
Original Assignee
Chengdu Environment Technology Co Ltd
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 Chengdu Environment Technology Co Ltd filed Critical Chengdu Environment Technology Co Ltd
Priority to CN201721294754.8U priority Critical patent/CN207405000U/en
Application granted granted Critical
Publication of CN207405000U publication Critical patent/CN207405000U/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Treatment Of Water By Oxidation Or Reduction (AREA)
  • Physical Water Treatments (AREA)

Abstract

The utility model discloses a kind of device of the high COD waste liquids of compound advanced oxidation technology processing, including:Hydrogen peroxide catalyzed processing unit, including the first hybrid reaction tank and the tank connected first UV Photoreactors of the first hybrid reaction and the first catalytic reactor;Catalytic ozonation processing unit, it includes the second hybrid reaction tank, the 2nd UV Photoreactors and the second catalytic reactor with the second hybrid reaction tank, UV light sources are set inside the second catalytic reactor, filler particles shape catalyst B in the gap between UV light sources and reactor wall face;Ozone generator is connected respectively with the first ozone inlet and the second ozone inlet;Exhaust processor is connected respectively with the waste gas outlet at the top of the first blending tank and the second blending tank.Hydrogen peroxide and ozone catalytic reaction technology are combined by the method for treating waste liquid of the utility model, can fast decoupled organic pollution, efficiently thoroughly handle high COD waste liquids.

Description

A kind of compound advanced oxidation technology handles the device of high COD waste liquids
Technical field
The utility model is related to a kind of devices of the high COD waste liquids of compound advanced oxidation technology processing, belong to Wastewater Treatment Technology Art field.
Background technology
Traditional wastewater treatment method has Physical, chemical method and biological method.The treatment process of industrial wastewater is generally adopted It is combined with level-one materializing strategy (such as filtering, chemical coagulation, the precipitation method) with two stage biological processing (such as activated sludge process), ability Enough by wastewater treatment to discharge standard.It widely uses however as industrial development and speciality chemical, is produced in industrial processes Life has organism in product, byproduct or the derivative discarded object of inhibition or toxicity or containing the organic of high-concentration hardly-degradable Or inorganic pollution so that traditional wastewater processing unit is difficult to handle.Recently again because of electronic industry rapid rising, the waste water of generation Change of water quality is big, and conventional waste water treatment process is difficult to handle the treatment process, it is necessary to using other high financial cost at all.
Substance containing special chemical causes biological treatment difficulty decomposing pollutant in infant industry's waste water, and containing bio-toxicity or Biostatic.Therefore new waste water treatment process must have resistance to poison and removal biological inhibition sexual function, by toxicant It is decomposed into the biodegradable substance of small toxicity.Chemical oxidation treatment method and high-level oxidation technology are commonly used in processing waste water now Difficult decomposing pollutant.Its required equipment and place are small compared with biological treatment, and the reaction condition of method of chemical treatment is more loose, It is workable, it is easy to regulate and control its reaction rate and estimates removal efficiency.Therefore, waste water advanced oxidization treatment technology has been in recent years There is widely studied and application, many commercialized waste water advanced oxidization treatment technologies have been developed so far, such as Fenton methods, electrolysis Fenton oxidation, Photo-Fenton and photocatalytic oxidation etc..
At present, it is perfect not enough for the processing method containing high COD concentration and the big organic wastewater of toxicity, it is difficult to industry Change extensive processing waste water.Therefore exploitation high efficiency and low stain simultaneously can effectively reduce the treatment technology of above-mentioned industrial wastewater toxicity It is the important topic of current environment water pollution treatment technology development.Due to the high-COD waste water or waste liquid that are discharged in industrial production its Composition is complicated, with distillating method recycling wherein ingredient, so there are a large amount of high COD waste liquids by repeatedly distilling successor repeatedly in time, Cause follow-up difficulty.Traditional high-COD waste water or waste liquid must usually be reduced its bio-toxicity with dilution method with biological treatment and just obtained COD is removed with biological degradation method, but as extension rate increase will greatly improve wastewater flow rate wastewater treatment capacity is made to become larger, it is another Since metabolism difficulty increases, the COD value of waste discharge plays pendulum aspect.Toxicity organic wastewater is often with advanced oxygen at present Change method (Advanced Oxidation Processes, AOPs) carries out the fast degradation of pollutant and reduces toxicity, advanced oxygen The mechanism of action of change method is mostly similar, with have the hydroxyl free radical of Strong oxdiative ability homogeneously under heterogeneous conditions with organic matter Reaction since the hydroxyl free radical of tool Strong oxdiative ability is extremely unstable substance, is obtained by the reaction with organic matter during the reaction One electronics, therefore when obtaining the electronics of organic matter the structure of organic matter can be made to change or cause to be decomposed to form compared with small molecule The organic matter of amount.But the shortcomings that many existing advanced oxidation programs can not all overcome there are many, as efficiency is low and operates as This height, equipment cost are far above traditional chemical oxidation technology with operating cost and the processing cost of later stage sludge or discarded object, because This there is no method to be widely used in Industrial Wastewater Treatment, cause many special industrial wastewaters for whether using technique advance and retreat dimension Paddy.
Therefore, need to develop at present the Advanced Oxidation Technics in Dealing that can effectively drop high concentration COD waste liquid or waste water and its Corresponding disposal plant, and avoid generating follow-up waste sludge and waste liquid.
The content of the invention
One purpose of the utility model is to solve at least the above and/or defect, and provides and at least will be described later The advantages of.
The utility model is to solve advanced oxidation processes in the prior art to handle the existing place of high COD waste liquids there are one purpose Manage that efficiency is low, and organic pollution mineralising is not thorough, equipment cost and operating cost be of high cost and later stage sludge or discarded object The technical problems such as processing cost height.
In order to realize these purposes of the utility model and further advantage, the utility model provides a kind of compound advanced oxidation The device of the high COD waste liquids of process, including:
Hydrogen peroxide catalyzed processing unit, it is anti-including the first hybrid reaction tank, the first UV Photoreactors and the first catalysis Device is answered, the inlet and liquid outlet of the first UV Photoreactors are connected to the first hybrid reaction tank, and first catalysis is anti- The inlet of device and liquid outlet is answered to be connected to the first hybrid reaction tank, the first hybrid reaction tank is internally provided with heating Device, top set pH regulating devices, hydrogen peroxide to add in mouth and waste gas outlet, the inlet position of first catalytic reactor It puts and is additionally provided with the first ozone inlet;
Catalytic ozonation processing unit, it is anti-including the second hybrid reaction tank, the 2nd UV Photoreactors and the second catalysis Device is answered, the inlet of the second hybrid reaction tank is connected with the liquid outlet of the first hybrid reaction tank, the 2nd UV light reactions The inlet and liquid outlet of device are connected to the second hybrid reaction tank, and the inlet and liquid outlet of second catalytic reactor are equal The second hybrid reaction tank is connected to, the second hybrid reaction tank is internally provided with heating unit, and top sets pH to adjust dress It puts and waste gas outlet, the inlet front end of the 2nd UV Photoreactors sets the second ozone inlet, second catalysis is anti- It answers and UV light sources is set inside device, filler particles shape catalyst B in the gap between UV light sources and reactor wall face;
Ozone generator is connected respectively with the first ozone inlet and the second ozone inlet;
Exhaust processor is connected, the exhaust gas with the waste gas outlet at the top of the first blending tank and the second blending tank respectively The inside catalyst filling C of processor.
Preferably, first catalytic reactor includes the catalytic reaction slot of at least two serial or parallel connections, reactive tank Internal catalyst filling A is base metal mixed catalyst.
Preferably, the first UV Photoreactors include the UV light sources being arranged in reactor.
Preferably, between the first hybrid reaction tank and the first UV Photoreactors on connecting line and first mix it is anti- It answers and is respectively arranged with water pump on the connecting line between tank and the first catalytic reactor.
Preferably, between the second hybrid reaction tank and the 2nd UV Photoreactors on connecting line and second mix it is anti- It answers and is respectively arranged with water pump on the connecting line between tank and the second catalytic reactor.
Preferably, at least two second catalytic reactors connect in series or in parallel.
Preferably, the exhaust processor be tubular reactor, inside be additionally provided with heating unit.
Preferably, the exhaust processor further includes steam treatment device.
Compared with prior art, the utility model is beneficial in that:
One, by a variety of high-level oxidation technologies carry out it is compound, the high COD industrial wastewaters of efficient-decomposition are simultaneously conducive to subsequent bio Or materialization cell processing, the problem of which further improves Fenton technology middle and later periods sludge or discarded object, decompose Its COD decomposition efficiency is promoted to more than 90%, will not generate sludge or other solid waste, effectively by high COD organic liquid wastes Lifting waste water treatment effeciency.
Secondly, hydrogen peroxide catalyzed processing unit include 4 kinds generation hydroxyl radical free radical modes:(1) hydrogen peroxide light Decomposition reaction H2O2+ h ν → OH, (2) light Fenton's reaction Fe2++H2O2→Fe(OH)2++ OH, Fe (OH)2++hν→Fe2++ OH, (3) UV/O3Catalytic reaction, (4) UV/O3/H2O2Catalytic reaction.Therefore, the hydroxyl of higher concentration is assembled in reaction vessel Free radical, high concentration COD waste liquid carry out chain reaction decomposing organic pollutant with hydroxyl radical free radical, reach high efficiency removal COD Purpose.
Thirdly, high COD waste liquids by compound advanced oxidation technology processing after, be changed into small toxicity or it is avirulent can biology The substance of degradation is convenient for subsequent materializing strategy and biological treatment, and can handle various high COD waste liquids, uses model It encloses wide.
Description of the drawings
Compound advanced oxidation technology handles the apparatus structure signal of high COD waste liquids in Fig. 1, one embodiment of the utility model Figure.
Fig. 2, the high COD cutting fluids waste liquid treatment effect figure of certain factory.
Fig. 3, high COD degreasings water treatment effect figure.
Fig. 4, printing house's board-washing high-COD waste water treatment effect figure.
Figure label:
First hybrid reaction tank 1, the first UV Photoreactors 2, the first catalytic reactor 3, heating unit 11, pH regulating devices 12nd, hydrogen peroxide adds in mouth 13, waste gas outlet 14, the first ozone inlet 31, the second hybrid reaction tank 4, the 2nd UV light reactions Device 5, the second ozone inlet 51, the second catalytic reactor 6, heating unit 41, pH regulating devices 42, waste gas outlet 43, ozone Generator 7, exhaust processor 8, water pump 9.
Specific embodiment
The preferred embodiment of the utility model is illustrated below in conjunction with attached drawing, it should be understood that described herein excellent Embodiment is selected to be only used for describing and explaining the present invention, is not used to limit the utility model.
As depicted in figs. 1 and 2, the utility model provides the dress that a kind of compound advanced oxidation technology handles high COD waste liquids It puts, including:Hydrogen peroxide catalyzed processing unit, catalytic ozonation processing unit, ozone generator 7 and exhaust processor 8.
Wherein, hydrogen peroxide catalyzed processing unit includes the first hybrid reaction tank 1, the first UV Photoreactors 2 and first are urged Change reactor 3, the first hybrid reaction tank 1 is internally provided with for the heating unit 11 to waste liquid heated for controlling temperature, and top is set Adjust the pH regulating devices 12 of waste liquid acid-base value, hydrogen peroxide adds in mouth 13 and waste gas outlet 14.Mouth 13 is added in hydrogen peroxide Position is provided with to add in the medicine machine (not shown) of hydrogen peroxide.The inlet of the first UV Photoreactors 2 and go out Liquid mouth is connected to the first hybrid reaction tank 1 by pipeline and forms a fluid loop.In the first hybrid reaction tank 1 and the first UV Water pump 9 is set on the connecting line between the inlet of Photoreactor 2.First UV Photoreactors 2 include being arranged in reactor UV light sources.Mixed liquor in first hybrid reaction tank 1 is delivered in the first UV Photoreactors 2 and carries out ultraviolet light point by water pump 9 Organic pollution is solved, the mixed liquor after resolution process returns the first hybrid reaction tank 1.Water pump 9 is pumped into mixing again Liquid is reacted to the first UV Photoreactors 2, and water pump 9 both continuously can convey mixed liquor to the first UV Photoreactors 2, It can also set interval and intermittently convey mixed liquor.The inlet and liquid outlet of first catalytic reactor 3 are logical Piping is connected to the first hybrid reaction tank 1 and forms a fluid loop.In the first hybrid reaction tank 1 and the first catalytic reactor Water pump 9 is set on the connecting line between 3 inlet.Mixed liquor in first hybrid reaction tank 1 is delivered to first by water pump 9 In catalytic reactor 3, the mixed liquor after catalytic degradation processing returns the first hybrid reaction tank 1.Water pump 9 is pumped into again Mixed liquor is reacted to the first catalytic reactor 3.Water pump 9 both can continuously convey mixed to the first catalytic reactor 3 Liquid is closed, can also set interval and intermittently convey mixed liquor.First catalytic reactor 3 includes at least two series connection Or catalytic reaction slot in parallel, reactive tank inside catalyst filling A, is base metal mixed catalyst.The catalyst A energy Enough catalyzing hydrogen peroxides generate hydroxyl radical free radical, hydroxyl radical free radical oxygenolysis organic pollution.First catalytic reactor 3 into Liquid mouth position is additionally provided with the first ozone inlet 31, ozone gas is injected in the first catalytic reactor 3, ozone has in itself Strong oxidizing property can be with decomposing organic pollutant, while the generation hydroxyl radical free radical decomposition that can also act synergistically with catalyst A is organic Object.
Catalytic ozonation processing unit includes the second hybrid reaction tank 4, the 2nd UV Photoreactors 5 and the second catalytic reaction Device 6.The heating unit 41 for being internally provided with to heat waste liquid of second hybrid reaction tank 4, top set to adjust waste liquid The pH regulating devices 42 of acid-base value and waste gas outlet 43.The inlet and the first hybrid reaction tank 1 of the second hybrid reaction tank 4 Liquid outlet connection, with receive from the first hybrid reaction tank 1 come out the waste liquid by preliminary treatment.The 2nd UV light reactions The inlet and liquid outlet of device 5 are connected to the second hybrid reaction tank 4 by pipeline and form a fluid loop, and the second mixing is anti- Answer on the connecting line between the inlet of 4 and the 2nd UV Photoreactors 5 of tank setting water pump 9, water pump 9 is by the second hybrid reaction tank Pending waste liquid in 4 is delivered to the 2nd UV Photoreactors 5, then sends the waste liquid after light reaction back to second hybrid reaction tank 4.The inlet front end of the 2nd UV Photoreactors sets the second ozone inlet 51, the ozone in the 2nd UV Photoreactors 5 Gas is acted on ultraviolet cooperating, generates hydroxyl radical free radical, oxidative degradation organic pollution.The feed liquor of second catalytic reactor 6 Mouth and liquid outlet are connected to the second hybrid reaction tank 4 by pipeline and form a fluid loop.Second hybrid reaction tank 4 and Water pump 9 is set on the connecting line between the inlet of two catalytic reactors 6, and water pump 9 will be waited to locate in the second hybrid reaction tank 4 Reason waste liquid is delivered to the second catalytic reactor 6, then sends the waste liquid after light reaction back to second hybrid reaction tank 4.Described second urges Change and UV light sources are set inside reactor 6, filler particles shape catalyst B in the gap between UV light sources and reactor wall face; When specifically used, multiple second catalytic reactors 6 can be connected in series or in parallel as needed.Catalyst and spy The ultraviolet light of standing wave length is combined and plays synergistic effect, and the effect of oxidative degradation pollutant is better than exclusive use catalyst and ultraviolet The adduction of the degradation effect of light.
Ozone generator 7 is connected respectively with the first ozone inlet and the second ozone inlet, by the ozone gas of generation It is delivered to the first catalytic reactor 3 and the 2nd UV Photoreactors 5.
Exhaust processor 8 connects respectively with the waste gas outlet 43 at the top of 14 and second blending tank of the waste gas outlet of the first blending tank It connects, the inside catalyst filling C of exhaust processor.Exhaust processor is tubular reactor, inside be additionally provided with heating unit (not shown).It may further be preferable that the exhaust processor 8 further includes steam treatment equipment (not shown), for handling The a small amount of water vapour taken out of by exhaust gas.
Catalyst A, catalyst B and the catalyst C used in the present apparatus is different types of base metal mixed catalytic Agent.
The method that high COD waste liquids are handled using above device, is included the following steps:
S1, the waste liquid after separation of solid and liquid removes waste residue is adjusted into pH value as 3.0-7.0, hydrogen peroxide is in pH value 3.0-7.0 oxidation effectiveness is optimal in the range of.
S2, the waste liquid after adjusting pH is transferred to the first hybrid reaction tank 1, adds in hydrogen peroxide, be uniformly mixed, mixed Liquid is closed, water pump 9 is opened and part mixed liquor is pumped into the first UV Photoreactors 2, it is anti-that another part mixed liquor is sent into the first catalysis Device 3 is answered, while opens ozone generator 7, by the first UV Photoreactors 2 and the first catalytic reactor 3 treated mixed liquor The first hybrid reaction tank 1 is returned to, so cycles continuous processing waste liquid, obtains the waste liquid of organic pollution preliminary oxidation decomposition. In this step, the mode of 4 kinds of generation hydroxyl radical free radicals is included:(1) hydrogen peroxide photolysis reactions H2O2+ h ν → OH, (2) light Fenton's reaction Fe2++H2O2→Fe(OH)2++ OH, Fe (OH)2++hν→Fe2++ OH, (3) UV/O3Catalytic reaction, (4) UV/O3/H2O2Catalytic reaction.Therefore, the hydroxyl radical free radical of higher concentration, high concentration COD waste liquid and hydroxyl are assembled in reaction vessel Free radical carries out chain reaction decomposing organic pollutant, achievees the purpose that high efficiency removes COD.
S3, it is transferred to second after the waste liquid after preliminary exposition is adjusted pH to 6.0-12.0 in the first hybrid reaction tank 1 Hybrid reaction tank 4, is then turned on water pump 9 and part waste liquid is pumped into the 2nd UV Photoreactors 5, and another part waste liquid is pumped into second Catalytic reactor 6, by the 2nd UV Photoreactors 5 and the second catalytic reactor 6, treated that waste liquid is returned to the second mixing is anti- Tank 4 is answered, continuous processing waste liquid is so cycled, obtains the waste liquid of the thorough mineralising of organic matter.In this step, including 3 kinds of generation hydroxyls The mode of base free radical:(1)O3+H2O+hν→OH·+O2, 2.UV/O3 catalytic reactions, 3.UV/O3/H2O catalytic reactions.Therefore, The hydroxyl radical free radical of aggregation higher concentration, high concentration COD waste liquid carry out chain reaction decomposition with hydroxyl radical free radical in reaction vessel Organic pollution achievees the purpose that high efficiency removes COD.
The exhaust gas that S4, the first hybrid reaction tank and the second hybrid reaction tank generate enters exhaust processor and carries out catalysis point Solution, is finally emitted into air.The exhaust gas is mainly to have neither part nor lot in the extra ozone gas of reaction, the first hybrid reaction tank and the The a small amount of pernicious gas and waste liquid evaporated when two hybrid reaction tanks heat in waste liquid generated during degradation reaction Pernicious gas.
The concrete application embodiment of high COD waste liquids is handled using above-mentioned compound advanced oxidation technology:
(1) the high COD cutting fluids waste liquid of certain factory is handled, treatment effect is shown in Fig. 2.As can be seen that in initial treatment 4h, As processing time extends, total organic carbon (TOC) concentration in waste liquid is of a straight line type rapid decrease, and the TOC concentration of waste liquid is from first Beginning, 19000mg/L was reduced to 2000mg/L or so;As processing time extends after 4h, TOC concentration slowly reduces, until processing 16h, TOC concentration are close to zero.Thus illustrating, the Best Times of the degradation treatment cutting fluid waste liquid are initial 4h, after 4h, place Reason efficiency slows down.
(2) high COD degreasings waste water is handled, treatment effect is shown in Fig. 3.As can be seen that in initial 2h, with processing time Extend, COD concentration is of a straight line type rapid decrease in waste liquid, and the COD concentration of waste liquid is reduced to from initial 26000mg/L or so 2000mg/L or so;As processing time extends after 2h, COD concentration slowly reduces.Thus illustrate, the degradation treatment degreasing is given up The Best Times of water are initial 2h, after 2h, without apparent treatment effect.
(3) printing house's board-washing high-COD waste water is handled, the result is shown in Fig. 4.As can be seen that in initial 2h, during with processing Between extend, COD concentration is of a straight line type rapid decrease in waste liquid, and the COD concentration of waste liquid is reduced to from initial 8000mg/L or so 500mg/L or so;As processing time extends after 2h, COD concentration slowly reduces.Thus illustrate, the degradation treatment printing house The Best Times of waste water are initial 2h, after 2h, treatment effect unobvious.
Therefore, the compound advanced oxidation processing technique of the utility model can handle various high COD waste liquids, and COD decomposes effect Rate significantly improves, and will not generate sludge or other solid waste, effectively promotes high-COD waste water treatment effeciency, the scope of application Extensively.
The above descriptions are merely preferred embodiments of the present invention, and not the utility model is made in any form Limitation, although the utility model has been disclosed with preferred embodiment as above, be not limited to the utility model, it is any ripe Professional and technical personnel is known, is not being departed from the range of technical solutions of the utility model, when in the technology using the disclosure above Hold the equivalent embodiment made a little change or be modified to equivalent variations, as long as being without departing from technical solutions of the utility model Hold, any simple modification, equivalent change and modification that foundation the technical essence of the utility model makees above example, still Belong in the range of technical solutions of the utility model.

Claims (8)

1. a kind of compound advanced oxidation technology handles the device of high COD waste liquids, which is characterized in that including:
Hydrogen peroxide catalyzed processing unit, including the first hybrid reaction tank, the first UV Photoreactors and the first catalytic reactor, The inlet and liquid outlet of the first UV Photoreactors are connected to the first hybrid reaction tank, first catalytic reactor Inlet and liquid outlet are connected to the first hybrid reaction tank, and the first hybrid reaction tank is internally provided with heating unit, Top sets pH regulating devices, hydrogen peroxide to add in mouth and waste gas outlet, and the inlet position of first catalytic reactor is also It is provided with the first ozone inlet;
Catalytic ozonation processing unit, including the second hybrid reaction tank, the 2nd UV Photoreactors and the second catalytic reactor, The inlet of the second hybrid reaction tank is connected with the liquid outlet of the first hybrid reaction tank, the 2nd UV Photoreactors into Liquid mouth and liquid outlet are connected to the second hybrid reaction tank, and the inlet and liquid outlet of second catalytic reactor are connected to Second hybrid reaction tank, the second hybrid reaction tank are internally provided with heating unit, and top sets pH regulating devices and gives up Gas exports, the second ozone inlet of inlet front end setting of the 2nd UV Photoreactors, in second catalytic reactor Portion sets UV light sources, filler particles shape catalyst B in the gap between UV light sources and reactor wall face;
Ozone generator is connected respectively with the first ozone inlet and the second ozone inlet;
Exhaust processor is connected, the exhaust-gas treatment with the waste gas outlet at the top of the first blending tank and the second blending tank respectively The inside catalyst filling C of device.
2. compound advanced oxidation technology as described in claim 1 handles the device of high COD waste liquids, which is characterized in that described the One catalytic reactor includes the catalytic reaction slot of at least two serial or parallel connections, and reactive tank inside catalyst filling A, is non-expensive Metal mixed catalyst.
3. compound advanced oxidation technology as claimed in claim 2 handles the device of high COD waste liquids, which is characterized in that described the One UV Photoreactors include the UV light sources being arranged in reactor.
4. compound advanced oxidation technology as claimed in claim 3 handles the device of high COD waste liquids, which is characterized in that first Between hybrid reaction tank and the first UV Photoreactors on connecting line and the first hybrid reaction tank and the first catalytic reactor it Between connecting line on be respectively arranged with water pump.
5. compound advanced oxidation technology as claimed in claim 4 handles the device of high COD waste liquids, which is characterized in that second Between hybrid reaction tank and the 2nd UV Photoreactors on connecting line and the second hybrid reaction tank and the second catalytic reactor it Between connecting line on be respectively arranged with water pump.
6. compound advanced oxidation technology as claimed in claim 5 handles the device of high COD waste liquids, which is characterized in that at least two A second catalytic reactor connects in series or in parallel.
7. compound advanced oxidation technology as described in claim 1 handles the device of high COD waste liquids, which is characterized in that described useless Treatment apparatus is tubular reactor, inside be additionally provided with heating unit.
8. compound advanced oxidation technology as claimed in claim 7 handles the device of high COD waste liquids, which is characterized in that described useless Treatment apparatus further includes steam treatment device.
CN201721294754.8U 2017-10-10 2017-10-10 A kind of compound advanced oxidation technology handles the device of high COD waste liquids Active CN207405000U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201721294754.8U CN207405000U (en) 2017-10-10 2017-10-10 A kind of compound advanced oxidation technology handles the device of high COD waste liquids

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201721294754.8U CN207405000U (en) 2017-10-10 2017-10-10 A kind of compound advanced oxidation technology handles the device of high COD waste liquids

Publications (1)

Publication Number Publication Date
CN207405000U true CN207405000U (en) 2018-05-25

Family

ID=62407378

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201721294754.8U Active CN207405000U (en) 2017-10-10 2017-10-10 A kind of compound advanced oxidation technology handles the device of high COD waste liquids

Country Status (1)

Country Link
CN (1) CN207405000U (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111533378A (en) * 2020-05-11 2020-08-14 上海市政工程设计研究总院(集团)有限公司 Combined purification method suitable for pathogen control of discharge port
CN112023690A (en) * 2020-08-26 2020-12-04 福建龙净环保股份有限公司 VOCs waste gas treatment system and VOCs waste gas treatment method

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111533378A (en) * 2020-05-11 2020-08-14 上海市政工程设计研究总院(集团)有限公司 Combined purification method suitable for pathogen control of discharge port
CN112023690A (en) * 2020-08-26 2020-12-04 福建龙净环保股份有限公司 VOCs waste gas treatment system and VOCs waste gas treatment method
CN112023690B (en) * 2020-08-26 2022-07-12 福建龙净环保股份有限公司 VOCs waste gas treatment system and VOCs waste gas treatment method

Similar Documents

Publication Publication Date Title
CN101734817B (en) Method for treating organic chemical waste water
Zhang et al. Treatment of ammonia‑nitrogen wastewater by the ultrasonic strengthened break point chlorination method
CN105621740B (en) A kind of ferrikinetics and the Fenton oxidation method and its device of sludge zero discharge
CN105776738B (en) Method and device for pretreatment of organic wastewater
CN107500456A (en) A kind of compound advanced oxidation technology handles the device and method of high COD waste liquids
CN204958499U (en) Novel advanced oxidation - ozone catalytic oxidation AOP waste water treatment device
CN105800739A (en) 3D-EO three-dimensional peroxidation electrochemical device and application thereof
CN101148287B (en) Enhanced oxidation process and device for treating organic poison wastewater
CN104193058B (en) A kind of gold mine cyanide wastewater comprehensive processing method
CN109264845A (en) A kind of device and method of reverse osmosis concentrated water organic matter and ammonia nitrogen removal simultaneously
CN207405000U (en) A kind of compound advanced oxidation technology handles the device of high COD waste liquids
US9604862B2 (en) Oxidation method, nozzle and system for treating waste water
CN115140878A (en) System and method for producing hydrogen peroxide with low energy consumption and removing perfluorinated compounds in water in situ
CN206915904U (en) A kind of wastewater treatment equipment
CN106082559A (en) A kind of integrated waste-water treater of efficient energy-saving
CN218320969U (en) Collaborative ozone catalytic oxidation system
CN206204101U (en) A kind of integrated waste-water treater of efficient energy-saving
CN118591513A (en) Method and system for water treatment using improved advanced oxidation technology
JPH0938672A (en) Pressurization type lower injection system multistage ozone contact vessel
CN218491598U (en) Copper-containing etching waste liquid and tower spraying absorption liquid co-processing device
CN207210049U (en) Catalytic wet oxidation administers the device of hydrochloric organic wastewater
CN207511907U (en) Efficiently catalyzing and oxidizing reaction unit
CN111689570A (en) Method for treating sewage by using ozone micro-nano bubbles
CN206014494U (en) A kind of device for disposing mother solution in Chemical Manufacture
CN111977739A (en) COD degradation reactor for high-concentration organic wastewater

Legal Events

Date Code Title Description
GR01 Patent grant
GR01 Patent grant