CN109734186A - A kind of nanometer of microvesicle biochemical purification device and method - Google Patents
A kind of nanometer of microvesicle biochemical purification device and method Download PDFInfo
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- CN109734186A CN109734186A CN201910199100.4A CN201910199100A CN109734186A CN 109734186 A CN109734186 A CN 109734186A CN 201910199100 A CN201910199100 A CN 201910199100A CN 109734186 A CN109734186 A CN 109734186A
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- 238000000746 purification Methods 0.000 title claims abstract description 24
- 238000000034 method Methods 0.000 title claims abstract description 19
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 95
- 239000000945 filler Substances 0.000 claims abstract description 17
- 238000010992 reflux Methods 0.000 claims abstract description 7
- 238000007599 discharging Methods 0.000 claims abstract description 4
- 239000010865 sewage Substances 0.000 claims description 32
- 239000002351 wastewater Substances 0.000 claims description 21
- 201000010099 disease Diseases 0.000 claims description 18
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 claims description 18
- 239000004744 fabric Substances 0.000 claims description 9
- 238000000926 separation method Methods 0.000 claims description 9
- 241000235342 Saccharomycetes Species 0.000 claims description 7
- 244000063299 Bacillus subtilis Species 0.000 claims description 6
- 235000014469 Bacillus subtilis Nutrition 0.000 claims description 6
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 6
- 239000001301 oxygen Substances 0.000 claims description 6
- 229910052760 oxygen Inorganic materials 0.000 claims description 6
- 239000007921 spray Substances 0.000 claims description 5
- 210000003608 fece Anatomy 0.000 claims description 3
- 238000002347 injection Methods 0.000 claims description 3
- 239000007924 injection Substances 0.000 claims description 3
- 230000009471 action Effects 0.000 claims description 2
- 239000007789 gas Substances 0.000 claims description 2
- 241000194033 Enterococcus Species 0.000 claims 1
- 239000010802 sludge Substances 0.000 abstract description 11
- 230000008901 benefit Effects 0.000 abstract description 5
- 230000035484 reaction time Effects 0.000 abstract description 4
- 238000004065 wastewater treatment Methods 0.000 abstract description 3
- 230000000694 effects Effects 0.000 description 11
- 244000005700 microbiome Species 0.000 description 8
- 239000010410 layer Substances 0.000 description 5
- 230000008569 process Effects 0.000 description 5
- 241000194031 Enterococcus faecium Species 0.000 description 4
- 241000209094 Oryza Species 0.000 description 4
- 235000007164 Oryza sativa Nutrition 0.000 description 4
- 238000012423 maintenance Methods 0.000 description 4
- 239000000463 material Substances 0.000 description 4
- 235000009566 rice Nutrition 0.000 description 4
- 239000003344 environmental pollutant Substances 0.000 description 3
- 235000015097 nutrients Nutrition 0.000 description 3
- 231100000719 pollutant Toxicity 0.000 description 3
- 238000005204 segregation Methods 0.000 description 3
- 241000894006 Bacteria Species 0.000 description 2
- 239000002028 Biomass Substances 0.000 description 2
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 2
- 230000003851 biochemical process Effects 0.000 description 2
- 230000007812 deficiency Effects 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 230000010354 integration Effects 0.000 description 2
- 230000003993 interaction Effects 0.000 description 2
- 210000000936 intestine Anatomy 0.000 description 2
- 238000011068 loading method Methods 0.000 description 2
- 239000012528 membrane Substances 0.000 description 2
- 238000002156 mixing Methods 0.000 description 2
- 238000006213 oxygenation reaction Methods 0.000 description 2
- 238000007789 sealing Methods 0.000 description 2
- 239000002344 surface layer Substances 0.000 description 2
- 239000000725 suspension Substances 0.000 description 2
- 241000193830 Bacillus <bacterium> Species 0.000 description 1
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- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- 238000005273 aeration Methods 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
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- 238000005265 energy consumption Methods 0.000 description 1
- 238000012851 eutrophication Methods 0.000 description 1
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- JEGUKCSWCFPDGT-UHFFFAOYSA-N h2o hydrate Chemical compound O.O JEGUKCSWCFPDGT-UHFFFAOYSA-N 0.000 description 1
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- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
- Biological Treatment Of Waste Water (AREA)
Abstract
A kind of nanometer of microvesicle biochemical purification device, it is related to life wastewater treatment device and method, equipped with reactor tank, it through divides is anaerobic biological area, water distribution area, aerobic biochemical area and nanometer microvesicle Disengagement zone in reactor tank, micropore biological filler is equipped in aerobic biochemical area, discharging on micropore biological filler has biological flora；Nanometer microvesicle Disengagement zone top is equipped with dross refluxing opening and clear water output, is equipped with the clear water diversion pipe being connected to clear water output in nanometer microvesicle Disengagement zone；Equipped with microbubble generator and nanometer microbubble generator, aerobic biochemical area bottom is equipped with microvesicle release, it separates and is equipped with nanometer microvesicle release below the water outlet of diversion pipe, microbubble generator and nanometer microbubble generator are connected with microvesicle release and nanometer microvesicle release respectively.The advantages such as simple with structure, small in size, occupied area is few, reaction time is short, seldom generates sludge, long service life, and running expense is low.
Description
Technical field
The present invention relates to life wastewater treatment device and method, elaborating is that a kind of structure is simple, small in size, land occupation face
Product is few, and reaction time is short, seldom generates sludge, long service life, the low nanometer microvesicle biochemical purification dress of running expense
It sets and method.
Background technique
It is known that the pollution sources of China's rivers and lakes be mainly city planting ductwork extend less than small towns rural area life it is dirty
The method of waste water, the centralized processing of life stain disease does not meet the status in China rural area, and therefore, distributing integrated sewage disposal is set
It is standby to get more and more attention.Novel integrated sewage treating apparatus, efficient process are developed according to China, rural area, small towns realistic situation
City and cannot access the cities and towns of pipe network, rural area, outlying unit sewage have become trend.
In order to fundamentally prevent and treat the pollution of rivers and lakes, I is increased substantially national requirements discharge index, discharge control
Also will be increasingly tighter, traditional sewage treatment process is extremely difficult to the current standard of country's formulation, with water eutrophication
The appearance of situation and the raising of standard of drainage, sewage treatment not only for the purpose of removing COD, BOD, SS, ammonia nitrogen, phosphorus etc.
Removal also has become for emphasis, domestic and international existing distributing integrated sewage treating apparatus some only with single aerobic biochemical at
Science and engineering skill, denitrogenation dephosphorizing is undesirable, and some is higher using single aeration mode, energy consumption；Some uses AO mode device integration
Not high volume is larger, mostly divides at present using film biologic integration equipment MBR, and high equipment cost, especially film cost are still very
Valuableness, maintenance expense and running management are costly, and the integrated equipment for wastewater treatment of other forms is hard to reach existing discharge
The requirement of standard.
Summary of the invention
Present invention aim to address above-mentioned the deficiencies in the prior art, it is simple to provide a kind of structure, small in size, occupied area
Few, short processing time seldom generates sludge, long service life, the low nanometer microvesicle biochemical purification device and method of running expense.
The present invention solves technical solution used by above-mentioned the deficiencies in the prior art:
A kind of nanometer of microvesicle biochemical purification device is equipped with reactor tank, it is characterised in that through divides is anaerobism in reactor tank
Biochemical zone, water distribution area, aerobic biochemical area and nanometer microvesicle Disengagement zone, aerobic biochemical area are located at anaerobic biological area upside, water distribution area
Between nanometer microvesicle Disengagement zone, wastewater inlet is located at anaerobic biological area on the side of nanometer microvesicle Disengagement zone, anaerobic biological
The demarcation plate in area and water distribution section is equipped with water hole, and water distribution area and the demarcation plate in aerobic biochemical section are equipped with water distribution water conservancy diversion
Hole is equipped with micropore biological filler in aerobic biochemical area, and discharging on micropore biological filler has biological flora；Aerobic biochemical area and nanometer
The demarcation plate top of microvesicle Disengagement zone, which is equipped with, separated the mouth of a river, and nanometer microvesicle Disengagement zone is equipped with the separation connected with the mouth of a river was separated
Diversion pipe, nanometer microvesicle Disengagement zone top are equipped with dross refluxing opening and clear water output, are equipped in nanometer microvesicle Disengagement zone and clear water
The clear water diversion pipe of outlet；Equipped with microbubble generator and nanometer microbubble generator, aerobic biochemical area bottom is equipped with micro-
Release is steeped, separates and is equipped with nanometer microvesicle release below the water outlet of diversion pipe, microbubble generator and nanometer microvesicle occur
Device is connected with microvesicle release and nanometer microvesicle release respectively.
The structure of heretofore described microvesicle release is: being equipped with water pipe, water pipe is equipped with apopore.
Heretofore described nanometer microvesicle release is spray head or fluffy head.Nanometer microvesicle release with separate diversion pipe
Water outlet is opposite to be located at below.
The water inlet of heretofore described microbubble generator and nanometer microbubble generator by the road with nanometer microvesicle
The lower part of Disengagement zone is connected.
Heretofore described dross refluxing opening is connected to wastewater inlet by the road or is connected with life stain disease collecting pit.
Micropore on heretofore described micropore biological filler successively becomes smaller from top to bottom aerobic biochemical is intracavitary.It is aerobic
It is biochemical it is intracavitary at least fill the different micropore biological filler of three layers of micropore, the micropore on micropore biological filler 0.1-10mm it
Between.
Heretofore described microbubble generator is used for the microbubble of biochemical part generation between 40-80 microns, excellent
Select 50-60 microns；Microbubble crosses the too small not easy to be filmed of vesicle, and the excessive rate of oxygen of microbubble is low, causes microorganism in sewage
Biochemical effects are poor, can not carry out subsequent nanometer microvesicle separating technology.
The microbubble that heretofore described nanometer microbubble generator generates is not more than 20 microns, preferably 10 microns with
Under.The smaller air-float segregation effect of microbubble diameter is better.
Heretofore described anaerobic biological is intracavitary to be equipped with guiding device.Guiding device is in the intracavitary setting of anaerobic biological
Deflector when sewage being made to flow through deflector, changes its flow direction, makes its mixing interaction.
Heretofore described biological flora includes enterococcus faecium, bacillus subtilis, acidophil, saccharomycete.Dung intestines ball
Bacterium, bacillus subtilis, acidophil, saccharomycete clump count ratio are 5:3-4:4-6:6-8.Mentioned microorganism is discharged and is filled out in biology
The present invention after nutrients is cultivated five to ten days, breeds flora large area is added after on material to be worked normally, instead of activity
Sludge.Other microorganisms for being conducive to sewage treatment can also be added in biological flora.
Access hole is equipped on the upside of heretofore described reactor tank, access hole is equipped with sealing cover.For loading and replacing
Material and maintenance.
A kind of nanometer of microvesicle biochemical purification method, it is characterised in that include the following steps:
1), with water pump that life stain disease is intracavitary by wastewater inlet injection anaerobic biological, under the action of intaking lift, life is dirty
Waste water is promoted from wastewater inlet between cloth water chamber, enters cloth water chamber by water hole after the intracavitary anaerobic biological of anaerobic biological；
2), the life stain disease in cloth water chamber enters aerobic biochemical area, micro- gas that microbubble generator generates through water distribution deflector hole
Bubble is discharged through microvesicle release to aerobic biochemical zone；
3), the sewage after the biochemical treatment of aerobic biochemical area is entered in nanometer microvesicle Disengagement zone by separating the mouth of a river, nanometer microvesicle
Micro SS in sewage is all floated to the top layer water surface by the nanometer microbubble that the nanometer microvesicle release in Disengagement zone releases, and is led to
It crosses dross and flows back into wastewater inlet or life stain disease collecting pit, circular treatment；Treated clear water is by clear water diversion pipe, clear
Water out discharge, completion processing.
When the invention works, sewage enters water distribution area through anaerobic biological area, and water distribution area is led the sewage after anaerobism through water distribution
Discharge orifice is promoted from aerobic biochemical area leading portion is uniformly biochemical backward, the microvesicle release discontinuity oxygenation of the bottom in aerobic biochemical area,
The sewage for making it into aerobic zone is sufficiently aerobic.By sufficiently it is aerobic after sewage enter a nanometer microvesicle Disengagement zone, nanometer microvesicle
Disengagement zone separates the suspended matter generated by aerobic biochemical area with nanometer microvesicle, completes sewage purification.
The present invention improves the utilization rate of oxygen and the active biomass of reactor in aerobic biochemical area using microvesicle；It is receiving
Using nanometer microvesicle in the trace suspension object air bearing generated in biochemical process to nanometer microvesicle Disengagement zone in rice microvesicle Disengagement zone
Sewage surface layer, wastewater inlet or life stain disease collecting pit are flowed back by dross, into circular treatment next time.The dress
Set take full advantage of nanometer microbubble technique accelerate in limited container separation, cooperate unique biological flora, instead of traditional work
Property sludge, does not generate sludge, effect that treated can achieve the effect that membrane process, replace traditional filter type, film substantially
Isolated purification device,.The present invention has structure simple, small in size, occupied area is few, and reaction time is short, does not generate dirt
Mud, long service life, the easy to operate, advantages such as running expense is low.
Detailed description of the invention
Fig. 1 is structural schematic diagram of the invention.
Specific embodiment
A kind of nanometer of microvesicle biochemical purification device is equipped with reactor tank, it is characterised in that is through divides in reactor tank
Anaerobic biological area 15, water distribution area 1, aerobic biochemical area 5 and nanometer microvesicle Disengagement zone 11, aerobic biochemical area 5 are located at anaerobic biological area
Between 15 upsides, water distribution area 1 and nanometer microvesicle Disengagement zone 11, water distribution area 1 is located at 15 upside of anaerobic biological area, and wastewater inlet 16 is set
In reactor tank of the anaerobic biological area 15 close to nanometer 11 side of microvesicle Disengagement zone, point in anaerobic biological area 15 and water distribution section 1
Partition is equipped with water hole 19, and the demarcation plate between water distribution area 1 and aerobic biochemical area 5 is equipped with water distribution deflector hole, aerobic biochemical area 5
Interior to be equipped with micropore biological filler 4, discharging on micropore biological filler 4 has biological flora；Biological flora includes enterococcus faecium, withered grass bud
Spore bacillus, acidophil, saccharomycete.Enterococcus faecium, bacillus subtilis, acidophil, saccharomycete clump count ratio are 5:3-4:4-6:
6-8, preferably 5:4:5:7；Before use, by mentioned microorganism discharge on micropore biological filler after addition nutrients cultivate five to
Ten days, make flora large area breed after the present invention can work normally, instead of activated sludge process.Biological flora can also be added
Be conducive to other microorganisms of sewage treatment.Separation above aerobic biochemical area and nanometer microvesicle Disengagement zone, micropore biological filler
Plate top, which is equipped with, separated the mouth of a river 6, and nanometer microvesicle Disengagement zone 11 is equipped with the separation diversion pipe 7 connected with the mouth of a river 6 was separated, separation
The water outlet of diversion pipe 7 is located at the lower part of nanometer microvesicle Disengagement zone 11, and the reactor tank on 11 top of nanometer microvesicle Disengagement zone is equipped with
With separate 6 sustained height of water hole or slightly above separate the dross refluxing opening 8 and clear water output 10 of water hole 6, nanometer microvesicle point
From be equipped in area 11 be connected to clear water output 10, lower end is located at the clear water diversion pipe 9 of nanometer microvesicle Disengagement zone middle part or lower part；If
There are microbubble generator 18 and nanometer microbubble generator 14, aerobic biochemical area bottom is laid with microvesicle release 2, and nanometer is micro-
It steeps and is equipped with nanometer microvesicle release 13 below the water outlet of the separation diversion pipe 7 of Disengagement zone lower part, microbubble generator 18 and receive
Rice microbubble generator 14 is connected with microvesicle release 2 and nanometer microvesicle release 13 respectively, the microvesicle release in the present embodiment
The structure of device 2 is: being equipped with water pipe, sets on water pipe and be evenly equipped with apopore, sets that there are two be connected with microvesicle release in reactor tank
Microvesicle interface, each microvesicle interface connect several microvesicle releases 2, more evenly for microvesicle release, also can be set three
Above microvesicle interface.Nanometer microvesicle release in the present embodiment is spray head or fluffy head, spray head or fluffy head with separate diversion pipe
Water outlet it is opposite be located at below, the nanometer microvesicle of spray head or the release of fluffy head can will be flowed out by separation diversion pipe water outlet
Water packet is good to the pollutant air-float segregation effect in it in it.It can be seen from the figure that the microbubble generator and receiving
The water inlet of rice microbubble generator is connected with the feed water inlet 12 of the lower part of nanometer microvesicle Disengagement zone by the road, and the two uses water
It is provided by the present invention treated clear water part, is supplied water without external.Guiding device is equipped in anaerobic biological chamber 15.Guiding device
It is when sewage flows through deflector 17, to change its flow direction in anaerobic biological intracavitary setting deflector 17, makes its mixing interaction.
The present invention be further improved, the dross refluxing opening 8 be connected to by the road with wastewater inlet or with life stain disease
Collecting pit is connected, and repeats biochemical purification.Micropore on the micropore biological filler aerobic biochemical it is intracavitary from top to bottom by
Layer becomes smaller；Aerobic biochemical is intracavitary at least to fill the different micropore biological filler of three layers of micropore, and the micropore on micropore biological filler exists
Between 0.1-10mm.
The microbubble that heretofore described microbubble generator generates is between 40-80 microns, and preferably 50-60 microns；
Microbubble crosses the too small not easy to be filmed of vesicle, and the excessive rate of oxygen of microbubble is low, causes microorganism poor to the biochemical effects in sewage, nothing
Method carries out subsequent nanometer microvesicle separating technology.The microbubble that the nanometer microbubble generator generates is not more than 20 microns,
It is preferred that 10 microns or less；The smaller air-float segregation effect of microbubble diameter is better.
Heretofore described biological flora includes enterococcus faecium, bacillus subtilis, acidophil, saccharomycete.Dung intestines ball
Bacterium, bacillus subtilis, acidophil, saccharomycete clump count ratio are 5:3-4:4-6:6-8.Mentioned microorganism is discharged and is filled out in biology
The present invention after nutrients is cultivated five to ten days, breeds flora large area is added after on material to be worked normally, instead of activity
Sludge.Other microorganisms for being conducive to sewage treatment can also be added in biological flora.Maintenance is equipped on the upside of the reactor tank
Mouth 3, access hole 3 are equipped with sealing cover；For loading and replacing material and maintenance.
A kind of nanometer of microvesicle biochemical purification method, it is characterised in that include the following steps:
1), with water pump that the life stain disease in wastewater disposal basin is intracavitary by wastewater inlet injection anaerobic biological, in the work of water inlet lift
Under, life stain disease is promoted from wastewater inlet between cloth water chamber, is entered after the intracavitary anaerobic biological of anaerobic biological by water hole
Cloth water chamber；
2), the life stain disease after the abundant anaerobism in anaerobic zone in cloth water chamber enters aerobic biochemical area through water distribution deflector hole, micro-
The microbubble that the generating apparatus that is soaked generates is discharged through microvesicle release to aerobic biochemical zone, and microbubble generator is interrupted sex work, is led to
Often release microvesicle 1-5 hours stops 0.5-3 hours；It is preferred that microbubble generator work 3 hours, it is 3 small to the release of aerobic biochemical zone
When microvesicle, sufficient dissolved oxygen (DO) is provided for it, stops two hours after three, facultative anaerobic biochemical, biological flora biochemical decomposition is given birth to
Pollutant (COD, BOD, SS ammonia nitrogen etc.) in stain disease living；It is intermittent discharged into sewage a large amount of microbubble with
Biological flora cooperation can quickly, thoroughly decompose the pollutant in life stain disease, seldom generate sludge.
3), the sewage after the biochemical treatment of aerobic biochemical area is entered in nanometer microvesicle Disengagement zone by separating the mouth of a river, nanometer
Micro SS in sewage is all floated to top layer water by the nanometer microbubble that the nanometer microvesicle release in microvesicle Disengagement zone releases
Face flows back into wastewater inlet or life stain disease collecting pit, circular treatment by dross；Treated clear water is by clear water water conservancy diversion
Pipe, clear water output discharge, completion processing.
When the invention works, sewage enters water distribution area through anaerobic biological area, and water distribution area is led the sewage after anaerobism through water distribution
Discharge orifice is promoted from aerobic biochemical area leading portion is uniformly biochemical backward, the microvesicle release discontinuity oxygenation of the bottom in aerobic biochemical area,
The sewage for making it into aerobic zone is sufficiently aerobic.By sufficiently it is aerobic after sewage enter a nanometer microvesicle Disengagement zone, nanometer microvesicle
Disengagement zone separates the suspended matter generated by aerobic biochemical area with nanometer microvesicle, completes sewage purification.
The present invention improves the utilization rate of oxygen and the active biomass of reactor in aerobic biochemical area using microvesicle；It is receiving
Using nanometer microvesicle in the trace suspension object air bearing generated in biochemical process to nanometer microvesicle Disengagement zone in rice microvesicle Disengagement zone
Sewage surface layer, wastewater inlet or life stain disease collecting pit are flowed back by dross, into circular treatment next time.The dress
Set take full advantage of nanometer microbubble technique accelerate in limited container separation, cooperate unique biological flora, instead of traditional work
Property sludge, does not generate sludge, effect that treated can achieve the effect that membrane process, replace traditional filter type, film substantially
Isolated purification device,.The present invention has structure simple, small in size, occupied area is few, and reaction time is short, does not generate dirt
Mud, long service life, the easy to operate, advantages such as running expense is low.
Claims (10)
1. a kind of nanometer of microvesicle biochemical purification device, it is equipped with reactor tank, it is characterised in that through divides be to detest in reactor tank
Oxygen biochemical zone, water distribution area, aerobic biochemical area and nanometer microvesicle Disengagement zone, aerobic biochemical area are located at anaerobic biological area upside, water distribution
Between area and nanometer microvesicle Disengagement zone, wastewater inlet is located at anaerobic biological area on the side of nanometer microvesicle Disengagement zone, and anaerobism is raw
The demarcation plate for changing area and water distribution section is equipped with water hole, and water distribution area and the demarcation plate in aerobic biochemical section are equipped with water distribution water conservancy diversion
Hole is equipped with micropore biological filler in aerobic biochemical area, and discharging on micropore biological filler has biological flora；Aerobic biochemical area and nanometer
The demarcation plate top of microvesicle Disengagement zone, which is equipped with, separated the mouth of a river, and nanometer microvesicle Disengagement zone is equipped with the separation connected with the mouth of a river was separated
Diversion pipe, nanometer microvesicle Disengagement zone top are equipped with dross refluxing opening and clear water output, are equipped in nanometer microvesicle Disengagement zone and clear water
The clear water diversion pipe of outlet；Equipped with microbubble generator and nanometer microbubble generator, aerobic biochemical area bottom is equipped with micro-
Release is steeped, separates and is equipped with nanometer microvesicle release below the water outlet of diversion pipe, microbubble generator and nanometer microvesicle occur
Device is connected with microvesicle release and nanometer microvesicle release respectively.
2. according to claim 1 nanometer of microvesicle biochemical purification device, it is characterised in that the knot of the microvesicle release
Structure is: being equipped with water pipe, water pipe is equipped with apopore.
3. according to claim 1 nanometer of microvesicle biochemical purification device, it is characterised in that the nanometer microvesicle release
For spray head or fluffy head.
4. according to claim 1 nanometer of microvesicle biochemical purification device, it is characterised in that the microbubble generator and
The water inlet of nanometer microbubble generator is connected with the lower part of nanometer microvesicle Disengagement zone by the road.
5. according to claim 1 nanometer of microvesicle biochemical purification device, it is characterised in that the dross refluxing opening is through pipe
Road is connected to wastewater inlet or is connected with life stain disease collecting pit.
6. according to claim 1 nanometer of microvesicle biochemical purification device, it is characterised in that on the micropore biological filler
Micropore successively become smaller from top to bottom aerobic biochemical is intracavitary.
7. according to claim 1 nanometer of microvesicle biochemical purification device, it is characterised in that the microbubble generator is used
In the microbubble that biochemical part generates between 40-80 microns；The microbubble that the nanometer microbubble generator generates is little
In 20 microns.
8. according to claim 1 nanometer of microvesicle biochemical purification device, it is characterised in that the anaerobic biological is intracavitary to be set
There is guiding device.
9. according to claim 1 nanometer of microvesicle biochemical purification device, it is characterised in that the biological flora includes dung
Enterococcus, bacillus subtilis, acidophil, saccharomycete.
10. a kind of nanometer of microvesicle biochemical purification method, it is characterised in that include the following steps:
1), with water pump that life stain disease is intracavitary by wastewater inlet injection anaerobic biological, under the action of intaking lift, life is dirty
Waste water is promoted from wastewater inlet between cloth water chamber, enters cloth water chamber by water hole after the intracavitary anaerobic biological of anaerobic biological；
2), the life stain disease in cloth water chamber enters aerobic biochemical area, micro- gas that microbubble generator generates through water distribution deflector hole
Bubble is discharged through microvesicle release to aerobic biochemical zone；
3), the sewage after the biochemical treatment of aerobic biochemical area is entered in nanometer microvesicle Disengagement zone by separating the mouth of a river, nanometer microvesicle
Micro SS in sewage is all floated to the top layer water surface by the nanometer microbubble that the nanometer microvesicle release in Disengagement zone releases, and is led to
It crosses dross and flows back into wastewater inlet or life stain disease collecting pit, circular treatment；Treated clear water is by clear water diversion pipe, clear
Water out discharge, completion processing.
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Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2007175606A (en) * | 2005-12-27 | 2007-07-12 | Meidensha Corp | Microbubble supply method, and its apparatus and system |
| CN202124539U (en) * | 2011-06-20 | 2012-01-25 | 扬州龙锦涂装环保设备有限公司 | Underground integrated domestic sewage treatment device |
| CN204185345U (en) * | 2014-11-07 | 2015-03-04 | 青岛力科环保工程有限公司 | A kind of bacteria filter device |
| CN204417216U (en) * | 2015-01-31 | 2015-06-24 | 山东恩特水处理科技有限公司 | Integration air-dissolved microbial film water treating equipment |
| CN104888636A (en) * | 2015-05-28 | 2015-09-09 | 中国石油化工股份有限公司 | Micro-nano bubble generation device and sewage purification system |
| CN207227211U (en) * | 2016-08-19 | 2018-04-13 | 华安奥特（北京）科技股份有限公司 | A kind of micro-nano bubble processing unit of the chlorine dioxide of dyeing waste water |
| CN209974412U (en) * | 2019-03-15 | 2020-01-21 | 威海格润环保科技股份有限公司 | Biochemical purifier of nanometer microbubble |
-
2019
- 2019-03-15 CN CN201910199100.4A patent/CN109734186A/en active Pending
Patent Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2007175606A (en) * | 2005-12-27 | 2007-07-12 | Meidensha Corp | Microbubble supply method, and its apparatus and system |
| CN202124539U (en) * | 2011-06-20 | 2012-01-25 | 扬州龙锦涂装环保设备有限公司 | Underground integrated domestic sewage treatment device |
| CN204185345U (en) * | 2014-11-07 | 2015-03-04 | 青岛力科环保工程有限公司 | A kind of bacteria filter device |
| CN204417216U (en) * | 2015-01-31 | 2015-06-24 | 山东恩特水处理科技有限公司 | Integration air-dissolved microbial film water treating equipment |
| CN104888636A (en) * | 2015-05-28 | 2015-09-09 | 中国石油化工股份有限公司 | Micro-nano bubble generation device and sewage purification system |
| CN207227211U (en) * | 2016-08-19 | 2018-04-13 | 华安奥特（北京）科技股份有限公司 | A kind of micro-nano bubble processing unit of the chlorine dioxide of dyeing waste water |
| CN209974412U (en) * | 2019-03-15 | 2020-01-21 | 威海格润环保科技股份有限公司 | Biochemical purifier of nanometer microbubble |
Non-Patent Citations (1)
| Title |
|---|
| 王凯军: "城市黑臭水体治理实用技术及案例分析", 化学工业出版社, pages: 194 * |
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