CN110526390A - Sewage water intensification denitrification system and its control method - Google Patents
Sewage water intensification denitrification system and its control method Download PDFInfo
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- CN110526390A CN110526390A CN201910868313.1A CN201910868313A CN110526390A CN 110526390 A CN110526390 A CN 110526390A CN 201910868313 A CN201910868313 A CN 201910868313A CN 110526390 A CN110526390 A CN 110526390A
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- 239000010865 sewage Substances 0.000 title claims abstract description 106
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 44
- 229910001868 water Inorganic materials 0.000 title claims abstract description 42
- 238000000034 method Methods 0.000 title claims abstract description 16
- OKKJLVBELUTLKV-UHFFFAOYSA-N Methanol Chemical compound OC OKKJLVBELUTLKV-UHFFFAOYSA-N 0.000 claims abstract description 237
- 239000007788 liquid Substances 0.000 claims abstract description 108
- 239000003814 drug Substances 0.000 claims abstract description 79
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 45
- 229910052799 carbon Inorganic materials 0.000 claims abstract description 45
- 238000004064 recycling Methods 0.000 claims abstract description 20
- 238000002156 mixing Methods 0.000 claims abstract description 8
- 238000003756 stirring Methods 0.000 claims description 85
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 claims description 84
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims description 69
- 239000001569 carbon dioxide Substances 0.000 claims description 42
- 229910002092 carbon dioxide Inorganic materials 0.000 claims description 42
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 39
- 229910052757 nitrogen Inorganic materials 0.000 claims description 33
- 238000010521 absorption reaction Methods 0.000 claims description 31
- 230000001376 precipitating effect Effects 0.000 claims description 27
- 241000894006 Bacteria Species 0.000 claims description 11
- 238000001914 filtration Methods 0.000 claims description 10
- 239000002244 precipitate Substances 0.000 claims description 10
- 239000004576 sand Substances 0.000 claims description 9
- 239000013049 sediment Substances 0.000 claims description 9
- 239000004575 stone Substances 0.000 claims description 9
- UIIMBOGNXHQVGW-UHFFFAOYSA-M Sodium bicarbonate Chemical compound [Na+].OC([O-])=O UIIMBOGNXHQVGW-UHFFFAOYSA-M 0.000 claims description 6
- 239000007789 gas Substances 0.000 claims description 5
- 238000003466 welding Methods 0.000 claims description 5
- 239000003795 chemical substances by application Substances 0.000 claims description 4
- 238000004880 explosion Methods 0.000 claims description 4
- JCXJVPUVTGWSNB-UHFFFAOYSA-N nitrogen dioxide Inorganic materials O=[N]=O JCXJVPUVTGWSNB-UHFFFAOYSA-N 0.000 claims description 4
- 238000000746 purification Methods 0.000 claims description 4
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 claims description 3
- OMBRFUXPXNIUCZ-UHFFFAOYSA-N dioxidonitrogen(1+) Chemical compound O=[N+]=O OMBRFUXPXNIUCZ-UHFFFAOYSA-N 0.000 claims description 3
- VUZPPFZMUPKLLV-UHFFFAOYSA-N methane;hydrate Chemical compound C.O VUZPPFZMUPKLLV-UHFFFAOYSA-N 0.000 claims description 3
- 238000011017 operating method Methods 0.000 claims description 3
- QLNJFJADRCOGBJ-UHFFFAOYSA-N propionamide Chemical compound CCC(N)=O QLNJFJADRCOGBJ-UHFFFAOYSA-N 0.000 claims description 3
- 229940080818 propionamide Drugs 0.000 claims description 3
- 238000007789 sealing Methods 0.000 claims description 3
- 229910000030 sodium bicarbonate Inorganic materials 0.000 claims description 3
- 235000017557 sodium bicarbonate Nutrition 0.000 claims description 3
- 230000008859 change Effects 0.000 claims description 2
- 239000002245 particle Substances 0.000 claims description 2
- 230000000241 respiratory effect Effects 0.000 claims description 2
- 230000000694 effects Effects 0.000 abstract description 8
- 230000008901 benefit Effects 0.000 abstract description 4
- QJGQUHMNIGDVPM-UHFFFAOYSA-N nitrogen group Chemical group [N] QJGQUHMNIGDVPM-UHFFFAOYSA-N 0.000 description 4
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 3
- 239000005416 organic matter Substances 0.000 description 3
- 238000010586 diagram Methods 0.000 description 2
- 239000003344 environmental pollutant Substances 0.000 description 2
- 125000001477 organic nitrogen group Chemical group 0.000 description 2
- 231100000719 pollutant Toxicity 0.000 description 2
- 230000008569 process Effects 0.000 description 2
- 102000004169 proteins and genes Human genes 0.000 description 2
- 108090000623 proteins and genes Proteins 0.000 description 2
- 239000008213 purified water Substances 0.000 description 2
- 241000272814 Anser sp. Species 0.000 description 1
- 208000035473 Communicable disease Diseases 0.000 description 1
- 102000002322 Egg Proteins Human genes 0.000 description 1
- 108010000912 Egg Proteins Proteins 0.000 description 1
- 241000233855 Orchidaceae Species 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- 229920002472 Starch Polymers 0.000 description 1
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Chemical compound NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 description 1
- 241000700605 Viruses Species 0.000 description 1
- 150000001412 amines Chemical class 0.000 description 1
- 150000001413 amino acids Chemical class 0.000 description 1
- 230000005540 biological transmission Effects 0.000 description 1
- 229960000074 biopharmaceutical Drugs 0.000 description 1
- 210000000476 body water Anatomy 0.000 description 1
- 239000004202 carbamide Substances 0.000 description 1
- 235000014633 carbohydrates Nutrition 0.000 description 1
- 150000001720 carbohydrates Chemical class 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 201000010099 disease Diseases 0.000 description 1
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- DNJIEGIFACGWOD-UHFFFAOYSA-N ethanethiol Chemical compound CCS DNJIEGIFACGWOD-UHFFFAOYSA-N 0.000 description 1
- 238000012851 eutrophication Methods 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 208000015181 infectious disease Diseases 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 210000000936 intestine Anatomy 0.000 description 1
- GBMDVOWEEQVZKZ-UHFFFAOYSA-N methanol;hydrate Chemical compound O.OC GBMDVOWEEQVZKZ-UHFFFAOYSA-N 0.000 description 1
- 244000000010 microbial pathogen Species 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 235000016709 nutrition Nutrition 0.000 description 1
- 230000035764 nutrition Effects 0.000 description 1
- 210000000056 organ Anatomy 0.000 description 1
- 210000004681 ovum Anatomy 0.000 description 1
- 230000003071 parasitic effect Effects 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 230000007480 spreading Effects 0.000 description 1
- 235000019698 starch Nutrition 0.000 description 1
- 239000008107 starch Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000002352 surface water Substances 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/14—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
- B01D53/1456—Removing acid components
- B01D53/1475—Removing carbon dioxide
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/14—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
- B01D53/18—Absorbing units; Liquid distributors therefor
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/28—Anaerobic digestion processes
- C02F3/2806—Anaerobic processes using solid supports for microorganisms
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/001—Processes for the treatment of water whereby the filtration technique is of importance
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/283—Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5281—Installations for water purification using chemical agents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F2001/007—Processes including a sedimentation step
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/16—Nitrogen compounds, e.g. ammonia
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Life Sciences & Earth Sciences (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Analytical Chemistry (AREA)
- Microbiology (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Biodiversity & Conservation Biology (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
The present invention relates to a kind of sewage water intensification denitrification system and its control methods, affiliated technical field of sewage, including sewage feed pipe, horizontal methanol mixes liquid component and denitrification bio-filter case, sewage feed pipe and horizontal methanol mix liquid inter-module and are equipped with medicament settling tank, medicament settling tank and horizontal methanol mix liquid inter-module and are equipped with drawing liquid pump I, suction pump is equipped between medicament settling tank and sewage feed pipe, sewage inlet valve is equipped between suction pump and medicament settling tank, denitrification bio-filter case and horizontal methanol mix liquid inter-module and are equipped with drawing liquid pump II, drawing liquid pump II and horizontal methanol are equipped with mixed liquid outlet valve between mixing liquid component lower end, denitrification bio-filter case side is equipped with active carbon purifying pond case, drawing liquid pump III is equipped between active carbon purifying pond case and denitrification bio-filter case, sewage outlet valve is equipped between drawing liquid pump III and denitrification bio-filter case.Have the advantages that nitric efficiency high, effect stability and at low cost.Improve the reclamation rate and water quality quality of sewage recycling.
Description
Technical field
The present invention relates to technical field of sewage, and in particular to a kind of sewage water intensification denitrification system and its control method.
Background technique
Sanitary sewage is the waste water being discharged in resident's daily life, is mainly derived from residential architecture and public building, is such as lived
The toilet of the public places such as residence, organ, school, hospital, shop, factory, enterprise.Pollutant contained by sanitary sewage is mainly
Organic matter (such as protein, carbohydrate, fat, urea and ammonia nitrogen) and a large amount of pathogenic microorganisms (such as parasitic ovum and intestines
Road transmission virus etc.)；The organic matter being present in sanitary sewage is extremely unstable, is easy corruption and generates stench；Bacterium and cause of disease
Body using organic matter in sanitary sewage as nutrition mass propagation, can lead to infectious disease from spreading prevalence.Therefore, before sanitary sewage discharge
It must be handled.Total nitrogen (abbreviation TN) refers to that various forms in water are inorganic and the total amount of organic nitrogen, including NO3-, NO2 and
The organic nitrogens such as the inorganic nitrogens such as NH4+ and protein, amino acid and organic amine are calculated with the nitrogenous milligram number of every liter of water.Often it is used to table
Show the degree that water body is polluted by nutriment.When nitrogen, phosphorus substance are exceeded in surface water, microorganism mass propagation, planktonic organism life
Length is vigorous, eutrophic state occurs.
As water eutrophication is on the rise, sanitary sewage and industrial wastewater discharge standard are also increasingly stringenter,
GB8978-1996 has done clear stipulaties to the second pollutant maximum permissible concentration: the first discharge standard of ammonia nitrogen is < 15mg/
L.Emission industry for height containing ammonia nitrogen, in order to reach level-one pollution emission standard and requirements above, if still continuing to use traditional sewage
Denitrogenation processing mode, still have following major defect: economic cost investment height, complex process and denitrogenation efficiency are insufficient.It passes
The denitrogenation method of system such as A2/O, A/O etc., denitrogenation principle are all mainly anaerobic-aerobic or anoxic-aerobic process, are mainly passed through
The problems such as nitrification liquid to anoxic zone of flowing back carries out denitrogenation, but that there are nitric efficiencies is not high, effect is unstable and high energy consumption.
Summary of the invention
Nitric efficiency is not high, effect is unstable and deficiency at high cost present invention mainly solves existing in the prior art, and mentions
A kind of sewage water intensification denitrification system and its control method have been supplied, has had the advantages that high nitric efficiency, effect stability and at low cost.
Improve the reclamation rate and water quality quality of sewage recycling.
Above-mentioned technical problem of the invention is mainly to be addressed by following technical proposals:
A kind of sewage water intensification denitrification system, including sewage feed pipe, horizontal methanol mix liquid component and denitrification bio-filter case, institute
The horizontal methanol stated mixes liquid component upper end and is equipped with and the bolted methanol charging flange of the mixed liquid component phase flange form of horizontal methanol
Pipe, the sewage feed pipe mix liquid inter-module equipped with the medicament for mixing liquid component phase pipeline connection with horizontal methanol with horizontal methanol
Settling tank, the medicament settling tank and horizontal methanol mix liquid inter-module be equipped with fixed with medicament settling tank phase flanged joint and with
Horizontal methanol mixes the drawing liquid pump I of liquid component phase pipeline connection, is equipped between the medicament settling tank and sewage feed pipe and sewage
Feed pipe phase flange form bolted suction pump is equipped between the suction pump and medicament settling tank and mutually manages with medicament settling tank
The sewage inlet valve of road connection, the denitrification bio-filter case and horizontal methanol mix liquid inter-module and are equipped with and denitrification biology
Filter tank case phase flanged joint fix and with horizontal methanol mix liquid component phase pipeline connection drawing liquid pump II, the drawing liquid pump II with
Horizontal methanol is equipped with mixed liquid outlet valve between mixing liquid component lower end, and the denitrification bio-filter case side is equipped with raw with denitrification
The active carbon purifying pond case of object filter tank case phase pipeline connection is set between the active carbon purifying pond case and denitrification bio-filter case
Have and is fixed with active carbon purifying pond case phase flanged joint and the drawing liquid pump III with denitrification bio-filter case phase pipeline connection, it is described
Drawing liquid pump III with sewage outlet valve with denitrification bio-filter case phase pipeline connection is equipped between denitrification bio-filter case.
Preferably, the denitrification bio-filter case is equipped with and denitrification bio-filter case, phase pipeline connection
Carbon dioxide absorption case, the carbon dioxide absorption case are equipped with nitrogen and collect pressurized tank, and the nitrogen collects pressurized tank
It is equipped with nitrogen recycling blower between carbon dioxide absorption case, is set between the carbon dioxide absorption case and denitrification bio-filter case
There is Air fan.
Preferably, the carbon dioxide absorption case includes carbon dioxide absorption cabinet, the carbon dioxide absorption
Be equipped with sodium hydroxide solution in cabinet, be equipped with air inlet collecting pipe between the sodium hydroxide solution and Air fan, it is described into
Gas collecting pipe lower end is equipped with the porous type exhaust pipe of connection mutually integrated with air inlet collecting pipe, the sodium hydroxide solution top
Equipped with nitrogen recycling blower phase pipeline connection and the nitrogen recycling pipe that socket-connects with carbon dioxide absorption cabinet.
Preferably, it includes agitator tank that the horizontal methanol, which mixes liquid component, it is equipped with to extend in the agitator tank and stirs
It mixes tank and the Horizontal stirring axis with the sealing socket of agitator tank phase bearing-type, the Horizontal stirring axis is equipped with and Horizontal stirring axis
The helically stirring grillage of formula annular equidistantly distributed, described Horizontal stirring axis one end are equipped with and Horizontal stirring axis phase limit sleeve
The methanol connect mixes liquid and mixes motor, and the Horizontal stirring axis other end is equipped with the agitating shaft for mutually limiting socket with Horizontal stirring axis and limits
Position mounting base, the agitator tank upper end, which is equipped with, feeds flanged pipe with the bolted methanol of I phase flange form of drawing liquid pump, described
Methanol charging flanged pipe side, which is equipped with, to be connected with agitator tank and feeds the bolted sewage of flanged pipe phase flange form with methanol
Water inlet pipe I, the agitator tank lower end be equipped with the bolted mixed liquid outlet pipe of mixed liquid outlet valve phase flange form, described stirs
It mixes tank lower end and is equipped with the mixed liquid frame of the horizontal methanol welded with agitator tank phase inlaid type.
Preferably, the stirring grillage includes stirring mainboard, the stirring mainboard both ends are equipped with leads with stirring
Plate is perpendicular and is in the side plate of integrated inlay card, is equipped between both side plate and stirring mainboard is in the scraper plate of integrated vertical welding.
Preferably, the medicament settling tank includes medicament precipitating cabinet, dirt is equipped in the medicament settling tank body
Water, interior be equipped with of the medicament settling tank body extend to medicament precipitating cabinet upper end and are socketed with medicament precipitating cabinet phase bearing-type
Vertical stirring axle, the vertical stirring axle between sewage be equipped with vertical stirring axle be in integrated helical form equidistantly distributed
Stirring rod, the vertical stirring axle upper end be equipped with vertical stirring axle in it is integrated and with medicament precipitating cabinet phase flange form
Bolted medicament stirring motor, the medicament stirring motor side are equipped with the method for dosing medicine being connected with medicament precipitating cabinet
Orchid pipe and sewage pump pipe, and the sewage pumps pipe and extends to sewage lower part, and it is heavy that the medicament precipitating lower box is equipped with
Starch dump valve, the sediment dump valve are equipped with the sediment being connected with medicament precipitating cabinet between precipitating cabinet with medicament
Discharge pipe.
Preferably, the denitrification bio-filter case includes denitrification bio-filter case ontology, the denitrification
Several denitrifying bacterium filtering biologicals with denitrification bio-filter case ontology phase inlaid type grafting are equipped in the case ontology of biofilter
Film, the denitrification bio-filter case ontology top are equipped with the air inlet gas explosion for extending to denitrifying bacterium filtering biological film side
Pipe.
Preferably, the active carbon purifying pond case includes active carbon purifying pond case ontology, the active carbon purifying
Pond case ontology upper end is equipped with the water inlet pipe being connected with drawing liquid pump III, and the active carbon purifying pond case body lower part is equipped with and work
Property the outlet pipe that is connected of carbon purifying pond case ontology, the water outlet end surfaces are equipped with and the mutually sealed flanged joint of outlet pipe
Outlet valve is purified, pebble layer is equipped in the active carbon purifying pond case ontology, is equipped with sandstone below the pebble layer
Layer is equipped with active carbon layer between the sand stone layer and pebble layer.
Preferably, the control method of the sewage water intensification denitrification system, by following operating procedure:
Step 1: sewage is delivered in medicament settling tank from sewage feed pipe by suction pump and sewage inlet valve, by adding
Dephosphorization agent and poly- propionamide are added in medicament settling tank body by medicine flanged pipe, drive vertical stirring axle by medicament stirring motor
On stirring rod be sufficiently stirred, improve the speed of dephosphorization and precipitating, then pipe pumped by drawing liquid pump I and sewage, medicament sinks
Middle layer clear liquid sewage transport to horizontal methanol mixes in liquid component in the case of shallow lake.
Step 2: adding methanol by the sewage to agitator tank, liquid is mixed by methanol and is mixed on motor driven Horizontal stirring axis
Stirring grillage methanol is sufficiently dissolved in sewage, the sewage with methanol by drawing liquid pump II enter denitrification bio-filter
Case promotes the inorganic nitrogens such as nitrogen peroxide to react with methanol and generates nitrogen, carbon dioxide and water by denitrifying bacterium filtering biological film.
Step 3: entering in the case of active carbon purifying pond by denitrification treated sewage finally by drawing liquid pump III, adopt
It is purified water with the intrinsic pebble layer of active carbon purifying pond case, active carbon layer and sand stone layer from purification outlet valve discharge.
Preferably, the nitrogen and carbon dioxide that generate in denitrification bio-filter case pass through carbon dioxide absorption case, by
The intracorporal sodium hydroxide solution absorbing carbon dioxide of carbon dioxide absorption case generates soda and sodium bicarbonate precipitates particle, finally by
Nitrogen recycling blower and nitrogen collect pressurized tank for nitrogen recycling reuse.
The present invention can reach following effect:
The present invention provides a kind of sewage water intensification denitrification system and its control methods, compared with prior art, have denitrogenation effect
Rate height, effect stability and advantage at low cost.Improve the reclamation rate and water quality quality of sewage recycling.
Detailed description of the invention
Fig. 1 is structural schematic diagram of the invention.
Fig. 2 is the structure sectional view of medicament settling tank of the invention.
Fig. 3 is the structure sectional view that horizontal methanol of the invention mixes liquid component.
Fig. 4 is the structural schematic diagram of stirring grillage of the invention.
Fig. 5 is the structure sectional view of denitrification bio-filter case of the invention.
Fig. 6 is the structure sectional view of carbon dioxide absorption case of the invention.
Fig. 7 is the structure sectional view of active carbon purifying pond case of the invention.
In figure: sewage feed pipe 1, suction pump 2, sewage inlet valve 3, medicament settling tank 4, drawing liquid pump I 5, horizontal methanol are mixed
Liquid component 6, methanol charging flanged pipe 7, mixed liquid outlet valve 8, drawing liquid pump II 9, Air fan 10, denitrification bio-filter case 11,
Carbon dioxide absorption case 12, nitrogen recycling blower 13, nitrogen collection pressurized tank 14, drawing liquid pump III 15, active carbon purifying pond case 16,
Outlet valve 17, sewage outlet valve 18 are purified, horizontal methanol mixes liquid frame 19, sediment dump valve 20, and medicament precipitates cabinet 21, dosing
Flanged pipe 22, medicament stirring motor 23, vertical stirring axle 24, sewage pump pipe 25, stirring rod 26, sewage 27, sediment discharge
Pipe 28, methanol mix liquid and mix motor 29, agitator tank 30, and methanol feeds flanged pipe 31, and sewage water inlet pipe I 32 stirs grillage 33, horizontal
Agitating shaft 34 mixes liquid outlet pipe 35, and seat 36 is mounted in agitating shaft, and side plate 37 stirs mainboard 38, scraper plate 39, denitrification biology
Filter tank case ontology 40, air inlet gas explosion pipe 41, denitrifying bacterium filtering biological film 42, carbon dioxide absorption cabinet 43, air inlet collecting pipe
44, porous type exhaust pipe 45, nitrogen recycling pipe 46, sodium hydroxide solution 47, active carbon purifying pond case ontology 48, water inlet pipe 49,
Pebble layer 50, active carbon layer 51, sand stone layer 52, outlet pipe 53.
Specific embodiment
Below with reference to the embodiments and with reference to the accompanying drawing the technical solution to invention is described in further detail.
Embodiment: as shown in figs. 1-7, a kind of sewage water intensification denitrification system, including sewage feed pipe 1, horizontal methanol mix liquid
Component 6 and denitrification bio-filter case 11, horizontal methanol mix 6 upper end of liquid component and are equipped with and the mixed 6 phase flange of liquid component of horizontal methanol
The bolted methanol of formula feeds flanged pipe 7, is equipped between sewage feed pipe 1 and the mixed liquid component 6 of horizontal methanol mixed with horizontal methanol
The medicament settling tank 4 of 6 phase pipeline connection of liquid component, medicament settling tank 4 and horizontal methanol are equipped with and medicament precipitating between mixing liquid component 6
4 phase flanged joint of case fixes and mixes the drawing liquid pump I 5 of 6 phase pipeline connection of liquid component, medicament settling tank 4 and sewage with horizontal methanol
Between feed pipe 1 be equipped with the bolted suction pump 2 of 1 phase flange form of sewage feed pipe, set between suction pump 2 and medicament settling tank 4
There is the sewage inlet valve 3 with 4 phase pipeline connection of medicament settling tank, denitrification bio-filter case 11 and horizontal methanol mix liquid component 6
Between be equipped with fixed with 11 phase flanged joint of denitrification bio-filter case and with horizontal methanol mix 6 phase pipeline connection of liquid component drawing liquid
II 9 are pumped, drawing liquid pump II 9 and horizontal methanol are equipped with mixed liquid outlet valve 8,11 side of denitrification bio-filter case between mixing 6 lower end of liquid component
Side is equipped with the active carbon purifying pond case 16 with 11 phase pipeline connection of denitrification bio-filter case, active carbon purifying pond case 16 and anti-nitre
Change biofilter case 11 between be equipped with fixed with 16 phase flanged joint of active carbon purifying pond case and with 11 phase of denitrification bio-filter case
The drawing liquid pump III 15 of pipeline connection is equipped with and denitrification bio-filter case 11 between drawing liquid pump III 15 and denitrification bio-filter case 11
The sewage outlet valve 18 of phase pipeline connection.Denitrification bio-filter case 11 is equipped with to be connected with 11 phase pipeline of denitrification bio-filter case
Logical carbon dioxide absorption case 12, carbon dioxide absorption case 12 include carbon dioxide absorption cabinet 43, carbon dioxide absorption cabinet
It is equipped with sodium hydroxide solution 47 in 43, air inlet collecting pipe 44 is equipped between sodium hydroxide solution 47 and Air fan 10, air inlet is collected
44 lower end of pipe be equipped with the porous type exhaust pipe 45 of the mutually integrated connection of air inlet collecting pipe 44, be equipped with above sodium hydroxide solution 47
With the nitrogen recycling pipe 46 nitrogen recycling blower 13 phase pipeline connection and socket-connected with carbon dioxide absorption cabinet 43.Carbon dioxide
Respiratory box 12 is equipped with nitrogen and collects pressurized tank 14, and nitrogen is collected and returned between pressurized tank 14 and carbon dioxide absorption case 12 equipped with nitrogen
It calls prisoners in after letting them out for exercise machine 13, Air fan 10 is equipped between carbon dioxide absorption case 12 and denitrification bio-filter case 11.
It includes agitator tank 30 that horizontal methanol, which mixes liquid component 6, is equipped in agitator tank 30 and extends agitator tank 30 and and agitator tank
The Horizontal stirring axis 34 of 30 phase bearing-types sealing socket, Horizontal stirring axis 34 is equipped with helically formula is annular with Horizontal stirring axis 34
The stirring grillage 33 of equidistantly distributed, stirring grillage 33 include stirring mainboard 38, and stirring 38 both ends of mainboard are equipped with leads with stirring
Plate 38 is perpendicular and is in the side plate 37 of integrated inlay card, is equipped between both side plate 37 and stirring mainboard 38 is in integrated vertical welding
Scraper plate 39.34 one end of Horizontal stirring axis, which is equipped with, mixes motor 29 with the mixed liquid of methanol of 34 phase of Horizontal stirring axis limit socket, horizontal to stir
It mixes 34 other end of axis and is equipped with the agitating shaft limit installation seat 36 being socketed with the limit of 34 phase of Horizontal stirring axis, 30 upper end of agitator tank is equipped with
Flanged pipe 31 is fed with the bolted methanol of I 5 phase flange form of drawing liquid pump, methanol charging 31 side of flanged pipe is equipped with and agitator tank
30 be connected and with methanol feed the bolted sewage water inlet pipe I 32 of 7 phase flange form of flanged pipe, 30 lower end of agitator tank be equipped with
The mixed bolted mixed liquid outlet pipe 35 of 8 phase flange form of liquid outlet valve, 30 lower end of agitator tank are equipped with and 30 phase inlaid type of agitator tank
The horizontal methanol of welding mixes liquid frame 19.
Medicament settling tank 4 includes that medicament precipitates cabinet 21, and medicament precipitates and is equipped with sewage 27 in cabinet 21, and medicament precipitates cabinet
It is equipped in 21 and extends to medicament precipitating 21 upper end of cabinet and the vertical stirring axle 24 with medicament precipitating 21 phase bearing-type of cabinet socket,
It is equipped with the stirring rod 26 with vertical stirring axle 24 in integrated helical form equidistantly distributed between vertical stirring axle 24 and sewage 27, stands
24 upper end of formula agitating shaft be equipped with vertical stirring axle 24 in it is integrated and with medicament precipitate 21 phase flange form of cabinet it is bolted
Medicament stirring motor 23,23 side of medicament stirring motor are equipped with the dosing flanged pipe 22 being connected with medicament precipitating cabinet 21 and dirt
Water pumps pipe 25, and sewage pumps pipe 25 and extends to 27 lower part of sewage, and medicament precipitates 21 lower part of cabinet and is equipped with sediment dump valve 20,
Sediment dump valve 20 is equipped with the sediment discharge pipe 28 being connected with medicament precipitating cabinet 21 between precipitating cabinet 21 with medicament.
Denitrification bio-filter case 11 includes denitrification bio-filter case ontology 40, in denitrification bio-filter case ontology 40
Denitrifying bacterium filtering biological film 42 equipped with 12 pieces with the 40 phase inlaid type grafting of denitrification bio-filter case ontology, denitrification biology
The air inlet gas explosion pipe 41 for extending to 42 side of denitrifying bacterium filtering biological film is equipped with above filter tank case ontology 40.
Active carbon purifying pond case 16 includes active carbon purifying pond case ontology 48, and case ontology 48 upper end in active carbon purifying pond is equipped with
The water inlet pipe 49 being connected with drawing liquid pump III 15,48 lower part of active carbon purifying pond case ontology are equipped with and active carbon purifying pond case ontology
48 outlet pipes 53 being connected, 53 end face of outlet pipe are equipped with the purification outlet valve 17 with the mutually sealed flanged joint of outlet pipe 53,
It is equipped with pebble layer 50 in active carbon purifying pond case ontology 48, is equipped with sand stone layer 52, sand stone layer 52 and goose below pebble layer 50
Active carbon layer 51 is equipped between boulder bed 50.
The control method of sewage water intensification denitrification system, by following operating procedure:
Step 1: be delivered to sewage 27 in medicament settling tank 4 from sewage feed pipe 1 by suction pump 2 and sewage inlet valve 3,
Dephosphorization agent and poly- propionamide are added to medicament by dosing flanged pipe 22 to precipitate in cabinet 21, driven by medicament stirring motor 23
Stirring rod 26 on dynamic vertical stirring axle 24 is sufficiently stirred, and improves the speed of dephosphorization and precipitating, then pass through I 5 He of drawing liquid pump
Sewage pumps pipe 25 and mixes middle layer clear liquid sewage transport in medicament settling tank 4 to horizontal methanol in liquid component 6.
Step 2: add methanol by sewage 27 to agitator tank 30, liquid is mixed by methanol motor 29 is mixed driving horizontal stir
Methanol is sufficiently dissolved in sewage 27 by the stirring grillage 33 mixed on axis 34, and the sewage 27 with methanol is entered by drawing liquid pump II 9
Denitrification bio-filter case 11 promotes the inorganic nitrogens such as nitrogen peroxide to react generation with methanol by denitrifying bacterium filtering biological film 42
Nitrogen, carbon dioxide and water.The nitrogen and carbon dioxide generated in denitrification bio-filter case 11 passes through carbon dioxide absorption case
12, soda and sodium bicarbonate precipitating are generated by 47 absorbing carbon dioxide of sodium hydroxide solution in carbon dioxide absorption cabinet 43
Grain collects pressurized tank 14 for nitrogen recycling reuse finally by nitrogen recycling blower 13 and nitrogen.
Step 3: entering active carbon purifying pond case 16 finally by drawing liquid pump III 5 by denitrification treated sewage 27
It is interior, it is purified water using pebble layer 50, active carbon layer 51 and the sand stone layer 52 in active carbon purifying pond case ontology 48 from purification
Outlet valve 17 is discharged.
In conclusion the sewage water intensification denitrification system and its control method, have high nitric efficiency, effect stability and cost
Low advantage.Improve the reclamation rate and water quality quality of sewage recycling.
Above is only a specific embodiment of the present invention, but structure feature of the invention is not limited thereto, Ren Heben
Within the field of the present invention, made changes or modifications all cover within the scope of the patent of the present invention the technical staff in field.
Claims (10)
1. a kind of sewage water intensification denitrification system, it is characterised in that: including sewage feed pipe (1), horizontal methanol mix liquid component (6) and
Denitrification bio-filter case (11), the horizontal methanol mix liquid component (6) upper end and are equipped with and mixed liquid component (6) phase of horizontal methanol
Bolted methanol charging flanged pipe (7) of flange form, the sewage feed pipe (1) and horizontal methanol mix between liquid component (6)
Equipped with horizontal methanol mix liquid component (6) phase pipeline connection medicament settling tank (4), the medicament settling tank (4) with it is horizontal
It is equipped with to fix with medicament settling tank (4) phase flanged joint and mix liquid component (6) with horizontal methanol between methanol mixed liquid component (6) and mutually manage
The drawing liquid pump I (5) of road connection, the medicament settling tank (4) are equipped with and sewage feed pipe (1) phase between sewage feed pipe (1)
The bolted suction pump of flange form (2) is equipped with and medicament settling tank (4) between the suction pump (2) and medicament settling tank (4)
The sewage inlet valve (3) of phase pipeline connection, the denitrification bio-filter case (11) and horizontal methanol are set between mixing liquid component (6)
There is the drawing liquid fixed with denitrification bio-filter case (11) phase flanged joint and mix liquid component (6) phase pipeline connection with horizontal methanol
II (9) are pumped, the drawing liquid pump II (9) and horizontal methanol are equipped with mixed liquid outlet valve (8) between mixing liquid component (6) lower end, described
Denitrification bio-filter case (11) side is equipped with the active carbon purifying pond case with denitrification bio-filter case (11) phase pipeline connection
(16), it is equipped with and active carbon purifying pond case (16) between the active carbon purifying pond case (16) and denitrification bio-filter case (11)
Phase flanged joint is fixed and the drawing liquid pump III (15) with denitrification bio-filter case (11) phase pipeline connection, the drawing liquid pump III
(15) the sewage outlet valve with denitrification bio-filter case (11) phase pipeline connection is equipped between denitrification bio-filter case (11)
(18).
2. sewage water intensification denitrification system according to claim 1, it is characterised in that: the denitrification bio-filter case
(11) the carbon dioxide absorption case (12) with denitrification bio-filter case (11) phase pipeline connection, the carbon dioxide are equipped with
Respiratory box (12) is equipped with nitrogen and collects pressurized tank (14), and the nitrogen collects pressurized tank (14) and carbon dioxide absorption case
(12) nitrogen recycling blower (13) are equipped between, are set between the carbon dioxide absorption case (12) and denitrification bio-filter case (11)
There are Air fan (10).
3. sewage water intensification denitrification system according to claim 2, it is characterised in that: the carbon dioxide absorption case (12)
Including carbon dioxide absorption cabinet (43), sodium hydroxide solution (47) are equipped in the carbon dioxide absorption cabinet (43), institute
Air inlet collecting pipe (44) are equipped between the sodium hydroxide solution (47) stated and Air fan (10), under the air inlet collecting pipe (44)
End is equipped with the porous type exhaust pipe (45) of connection mutually integrated with air inlet collecting pipe (44), on the sodium hydroxide solution (47)
Side is equipped with and nitrogen recycling blower (13) phase pipeline connection and the nitrogen recycling pipe that socket-connects with carbon dioxide absorption cabinet (43)
(46).
4. sewage water intensification denitrification system according to claim 1, it is characterised in that: the horizontal methanol mixes liquid component
(6) include agitator tank (30), be equipped in the agitator tank (30) extend agitator tank (30) and with agitator tank (30) phase bearing
The Horizontal stirring axis (34) of formula sealing socket, the Horizontal stirring axis (34) are equipped with and Horizontal stirring axis (34) helically formula
The stirring grillage (33) of annular equidistantly distributed, described Horizontal stirring axis (34) one end are equipped with and mutually limit with Horizontal stirring axis (34)
The methanol of position socket mixes liquid and mixes motor (29), and Horizontal stirring axis (34) other end is equipped with and mutually limits with Horizontal stirring axis (34)
Seat (36) are mounted in the agitating shaft of position socket, and the agitator tank (30) upper end is equipped with and drawing liquid pump I (5) phase flange form bolt
The methanol of connection feeds flanged pipe (31), methanol charging flanged pipe (31) side be equipped be connected with agitator tank (30) and
The bolted sewage water inlet pipe I (32) of flanged pipe (7) phase flange form is fed with methanol, the agitator tank (30) lower end is equipped with
With the bolted mixed liquid outlet pipe (35) of mixed liquid outlet valve (8) phase flange form, the agitator tank (30) lower end is equipped with and stirs
The horizontal methanol for mixing the welding of tank (30) phase inlaid type mixes liquid frame (19).
5. sewage water intensification denitrification system according to claim 4, it is characterised in that: the stirring grillage (33) includes stirring
It mixes mainboard (38), described stirring mainboard (38) both ends are equipped with side that is perpendicular with stirring mainboard (38) and being in integrated inlay card
Plate (37), is equipped between both side plate (37) and stirring mainboard (38) is in the scraper plate (39) of integrated vertical welding.
6. sewage water intensification denitrification system according to claim 1, it is characterised in that: the medicament settling tank (4) includes
Medicament precipitates cabinet (21), is equipped with sewage (27) in medicament precipitating cabinet (21), the medicament precipitates cabinet (21)
Interior be equipped with extends to medicament precipitating cabinet (21) upper end and the vertical stirring axle with medicament precipitating cabinet (21) phase bearing-type socket
(24), it is equipped between the vertical stirring axle (24) and sewage (27) equidistant in integrated helical form with vertical stirring axle (24)
The stirring rod (26) of distribution, it is in integrated and and medicament that the vertical stirring axle (24) upper end, which is equipped with vertical stirring axle (24),
The bolted medicament stirring motor (23) of cabinet (21) phase flange form is precipitated, described medicament stirring motor (23) side is equipped with
The dosing flanged pipe (22) and sewage being connected with medicament precipitating cabinet (21) are pumped pipe (25), and the sewage pumps pipe (25)
Sewage (27) lower part is extended to, medicament precipitating cabinet (21) lower part is equipped with sediment dump valve (20), the precipitating
Object dump valve (20) is equipped with the sediment discharge pipe being connected with medicament precipitating cabinet (21) between precipitating cabinet (21) with medicament
(28).
7. sewage water intensification denitrification system according to claim 1, it is characterised in that: the denitrification bio-filter case
(11) include denitrification bio-filter case ontology (40), be equipped in the denitrification bio-filter case ontology (40) it is several with it is anti-
Nitrify the denitrifying bacterium filtering biological film (42) of biofilter case ontology (40) phase inlaid type grafting, the denitrification biological filter
The air inlet gas explosion pipe (41) for extending to denitrifying bacterium filtering biological film (42) side is equipped with above pond case ontology (40).
8. sewage water intensification denitrification system according to claim 1, it is characterised in that: the active carbon purifying pond case (16)
Including active carbon purifying pond case ontology (48), active carbon purifying pond case ontology (48) upper end is equipped with and drawing liquid pump III (15)
The water inlet pipe (49) being connected, active carbon purifying pond case ontology (48) lower part are equipped with and active carbon purifying pond case ontology
(48) outlet pipe (53) being connected, the outlet pipe (53) end face are equipped with and outlet pipe (53) mutually sealed flanged joint
It purifies outlet valve (17), is equipped with pebble layer (50) in the active carbon purifying pond case ontology (48), the pebble layer
(50) lower section is equipped with sand stone layer (52), is equipped with active carbon layer (51) between the sand stone layer (52) and pebble layer (50).
9. the control method of sewage water intensification denitrification system according to claim 1, it is characterised in that press following operating procedure:
It sinks step 1: sewage (27) is delivered to medicament from sewage feed pipe (1) by suction pump (2) and sewage inlet valve (3)
In shallow lake case (4), dephosphorization agent and poly- propionamide are added in medicament precipitating cabinet (21) by dosing flanged pipe (22), pass through medicine
Stirring rod (26) in agent stirring motor (23) driving vertical stirring axle (24) is sufficiently stirred, and the speed of dephosphorization and precipitating is improved
Degree, then pipe (25) is pumped for the interior middle layer clear liquid sewage transport of medicament settling tank (4) to horizontal by drawing liquid pump I (5) and sewage
Methanol mixes in liquid component (6)；
Step 2: add methanol by sewage (27) to agitator tank (30), by methanol mix liquid mix motor (29) drive it is horizontal
Methanol is sufficiently dissolved in sewage (27) by the stirring grillage (33) on agitating shaft (34), and the sewage (27) with methanol passes through drawing liquid
It pumps II (9) and enters denitrification bio-filter case (11), promote nitrogen peroxide etc. inorganic by denitrifying bacterium filtering biological film (42)
Nitrogen is reacted with methanol generates nitrogen, carbon dioxide and water；
Step 3: entering active carbon purifying pond case finally by drawing liquid pump III (5) by denitrification treated sewage (27)
(16) net using pebble layer (50), active carbon layer (51) and the sand stone layer (52) in active carbon purifying pond case ontology (48) in
Change water quality to be discharged from purification outlet valve (17).
10. the control method of sewage water intensification denitrification system according to claim 7, it is characterised in that: denitrification biological filter
The nitrogen and carbon dioxide generated in pond case (11) passes through carbon dioxide absorption case (12), by carbon dioxide absorption cabinet (43)
Sodium hydroxide solution (47) absorbing carbon dioxide generate soda and sodium bicarbonate and precipitate particle, finally by nitrogen recycling blower
(13) and nitrogen collects pressurized tank (14) for nitrogen recycling reuse.
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Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110961024A (en) * | 2019-12-24 | 2020-04-07 | 曹美军 | Agitating unit that food detected |
Citations (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1962487A (en) * | 2006-12-07 | 2007-05-16 | 同济大学 | Nitration denitrification integral type sewage denitrification biomembrane reactor |
| CN101423296A (en) * | 2008-11-21 | 2009-05-06 | 北京工业大学 | Hypoxic/anaerobic UASB-SBR landfill leachate shortcut biological denitrification method and apparatus |
| CN102653436A (en) * | 2012-06-01 | 2012-09-05 | 中冶华天南京工程技术有限公司 | Sewage reuse treatment system and process |
| CN106365384A (en) * | 2016-10-08 | 2017-02-01 | 上海未来企业股份有限公司 | Device and technology for removing total nitrogen |
| CN107265778A (en) * | 2017-08-02 | 2017-10-20 | 浙江西地环境科技有限公司 | Box hi-effect coagulation denitrification equipment |
| WO2018107740A1 (en) * | 2016-12-14 | 2018-06-21 | 江南大学 | Wastewater nitrogen and phosphorus removal device and application thereof |
| CN207805137U (en) * | 2017-12-31 | 2018-09-04 | 云南世诚环境技术有限公司 | A kind of filtering tank being conveniently replaceable filtrate |
| CN210795914U (en) * | 2019-09-16 | 2020-06-19 | 杭州金溢建设集团有限公司 | Sewage enhanced denitrification system |
-
2019
- 2019-09-16 CN CN201910868313.1A patent/CN110526390A/en active Pending
Patent Citations (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1962487A (en) * | 2006-12-07 | 2007-05-16 | 同济大学 | Nitration denitrification integral type sewage denitrification biomembrane reactor |
| CN101423296A (en) * | 2008-11-21 | 2009-05-06 | 北京工业大学 | Hypoxic/anaerobic UASB-SBR landfill leachate shortcut biological denitrification method and apparatus |
| CN102653436A (en) * | 2012-06-01 | 2012-09-05 | 中冶华天南京工程技术有限公司 | Sewage reuse treatment system and process |
| CN106365384A (en) * | 2016-10-08 | 2017-02-01 | 上海未来企业股份有限公司 | Device and technology for removing total nitrogen |
| WO2018107740A1 (en) * | 2016-12-14 | 2018-06-21 | 江南大学 | Wastewater nitrogen and phosphorus removal device and application thereof |
| CN107265778A (en) * | 2017-08-02 | 2017-10-20 | 浙江西地环境科技有限公司 | Box hi-effect coagulation denitrification equipment |
| CN207805137U (en) * | 2017-12-31 | 2018-09-04 | 云南世诚环境技术有限公司 | A kind of filtering tank being conveniently replaceable filtrate |
| CN210795914U (en) * | 2019-09-16 | 2020-06-19 | 杭州金溢建设集团有限公司 | Sewage enhanced denitrification system |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110961024A (en) * | 2019-12-24 | 2020-04-07 | 曹美军 | Agitating unit that food detected |
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Application publication date: 20191203 |