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 PDFInfo
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- 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
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- 239000007788 liquid Substances 0.000 title claims abstract description 82
- 239000002699 waste material Substances 0.000 title claims abstract description 64
- 238000007254 oxidation reaction Methods 0.000 title claims abstract description 30
- 230000003647 oxidation Effects 0.000 title claims abstract description 28
- 238000005516 engineering process Methods 0.000 title claims abstract description 27
- 150000001875 compounds Chemical class 0.000 title claims abstract description 19
- 238000006243 chemical reaction Methods 0.000 claims abstract description 81
- 230000003197 catalytic effect Effects 0.000 claims abstract description 44
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 claims abstract description 38
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 claims abstract description 29
- 239000003054 catalyst Substances 0.000 claims abstract description 20
- 238000006555 catalytic reaction Methods 0.000 claims abstract description 17
- 239000002912 waste gas Substances 0.000 claims abstract description 12
- 238000002156 mixing Methods 0.000 claims abstract description 11
- 238000006385 ozonation reaction Methods 0.000 claims abstract description 5
- 239000000945 filler Substances 0.000 claims abstract description 4
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- 238000011282 treatment Methods 0.000 claims description 28
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 23
- 239000007789 gas Substances 0.000 claims description 12
- 238000010438 heat treatment Methods 0.000 claims description 11
- 230000001105 regulatory effect Effects 0.000 claims description 7
- 238000011049 filling Methods 0.000 claims description 6
- 239000002184 metal Substances 0.000 claims 1
- 238000000034 method Methods 0.000 abstract description 21
- 239000002351 wastewater Substances 0.000 description 16
- -1 hydroxyl free radical Chemical class 0.000 description 11
- 239000000126 substance Substances 0.000 description 11
- 230000000694 effects Effects 0.000 description 10
- 238000004065 wastewater treatment Methods 0.000 description 10
- 230000008859 change Effects 0.000 description 9
- 238000006731 degradation reaction Methods 0.000 description 9
- 230000015556 catabolic process Effects 0.000 description 8
- 230000008569 process Effects 0.000 description 7
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- 238000000354 decomposition reaction Methods 0.000 description 6
- 239000005416 organic matter Substances 0.000 description 6
- 239000010842 industrial wastewater Substances 0.000 description 5
- 239000003344 environmental pollutant Substances 0.000 description 4
- 239000012530 fluid Substances 0.000 description 4
- 231100000719 pollutant Toxicity 0.000 description 4
- 150000003254 radicals Chemical class 0.000 description 4
- 239000000243 solution Substances 0.000 description 4
- 238000009303 advanced oxidation process reaction Methods 0.000 description 3
- 239000010953 base metal Substances 0.000 description 3
- 239000002173 cutting fluid Substances 0.000 description 3
- 238000005238 degreasing Methods 0.000 description 3
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- 239000000203 mixture Substances 0.000 description 3
- 239000002957 persistent organic pollutant Substances 0.000 description 3
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 230000008901 benefit Effects 0.000 description 2
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- 229910021506 iron(II) hydroxide Inorganic materials 0.000 description 2
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- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
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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
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.
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Cited By (2)
| 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 |
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2017
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Cited By (3)
| 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 |
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