CN106348446A - Corner adjustable type wastewater treatment biochemical reactor - Google Patents
Corner adjustable type wastewater treatment biochemical reactor Download PDFInfo
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- CN106348446A CN106348446A CN201610991542.9A CN201610991542A CN106348446A CN 106348446 A CN106348446 A CN 106348446A CN 201610991542 A CN201610991542 A CN 201610991542A CN 106348446 A CN106348446 A CN 106348446A
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- annular gallery
- wastewater treatment
- adjustable type
- water
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- 238000004065 wastewater treatment Methods 0.000 title claims abstract description 39
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 70
- 239000002351 wastewater Substances 0.000 claims abstract description 37
- 238000005842 biochemical reaction Methods 0.000 claims abstract description 15
- 238000005273 aeration Methods 0.000 claims description 55
- 206010002660 Anoxia Diseases 0.000 claims description 52
- 241000976983 Anoxia Species 0.000 claims description 52
- 206010021143 Hypoxia Diseases 0.000 claims description 52
- 230000007953 anoxia Effects 0.000 claims description 52
- 238000000034 method Methods 0.000 claims description 46
- 238000004062 sedimentation Methods 0.000 claims description 36
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 26
- 229910052760 oxygen Inorganic materials 0.000 claims description 26
- 239000001301 oxygen Substances 0.000 claims description 26
- 230000009935 nitrosation Effects 0.000 claims description 19
- 238000007034 nitrosation reaction Methods 0.000 claims description 19
- 239000010865 sewage Substances 0.000 claims description 18
- 238000005276 aerator Methods 0.000 claims description 16
- 239000000945 filler Substances 0.000 claims description 13
- 238000007254 oxidation reaction Methods 0.000 claims description 9
- 230000003647 oxidation Effects 0.000 claims description 8
- QGZKDVFQNNGYKY-UHFFFAOYSA-O Ammonium Chemical compound [NH4+] QGZKDVFQNNGYKY-UHFFFAOYSA-O 0.000 claims description 4
- 230000000977 initiatory effect Effects 0.000 claims description 4
- 239000000203 mixture Substances 0.000 claims description 3
- 230000002093 peripheral effect Effects 0.000 claims description 3
- 239000000725 suspension Substances 0.000 claims description 2
- 230000005540 biological transmission Effects 0.000 claims 1
- 239000007789 gas Substances 0.000 claims 1
- 230000000694 effects Effects 0.000 abstract description 10
- 238000013461 design Methods 0.000 abstract description 7
- 230000000813 microbial effect Effects 0.000 abstract description 4
- 230000008569 process Effects 0.000 description 27
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 20
- 229910052698 phosphorus Inorganic materials 0.000 description 20
- 239000011574 phosphorus Substances 0.000 description 20
- 238000012545 processing Methods 0.000 description 17
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 14
- 238000006243 chemical reaction Methods 0.000 description 11
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 10
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 8
- 230000008859 change Effects 0.000 description 8
- 239000010842 industrial wastewater Substances 0.000 description 8
- 238000010992 reflux Methods 0.000 description 7
- 230000006872 improvement Effects 0.000 description 6
- 229910052757 nitrogen Inorganic materials 0.000 description 6
- 229910021529 ammonia Inorganic materials 0.000 description 5
- 230000008901 benefit Effects 0.000 description 5
- 230000033228 biological regulation Effects 0.000 description 5
- 238000005516 engineering process Methods 0.000 description 5
- 230000014759 maintenance of location Effects 0.000 description 5
- 239000010802 sludge Substances 0.000 description 5
- 241001453382 Nitrosomonadales Species 0.000 description 4
- 230000004308 accommodation Effects 0.000 description 3
- 230000009286 beneficial effect Effects 0.000 description 3
- 230000004048 modification Effects 0.000 description 3
- 238000012986 modification Methods 0.000 description 3
- 238000006396 nitration reaction Methods 0.000 description 3
- 238000004080 punching Methods 0.000 description 3
- 238000000926 separation method Methods 0.000 description 3
- JVMRPSJZNHXORP-UHFFFAOYSA-N ON=O.ON=O.ON=O.N Chemical compound ON=O.ON=O.ON=O.N JVMRPSJZNHXORP-UHFFFAOYSA-N 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 238000002955 isolation Methods 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 238000001556 precipitation Methods 0.000 description 2
- CKUAXEQHGKSLHN-UHFFFAOYSA-N [C].[N] Chemical compound [C].[N] CKUAXEQHGKSLHN-UHFFFAOYSA-N 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 230000001651 autotrophic effect Effects 0.000 description 1
- 230000003851 biochemical process Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 230000008878 coupling Effects 0.000 description 1
- 238000010168 coupling process Methods 0.000 description 1
- 238000005859 coupling reaction Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000004615 ingredient Substances 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 230000001546 nitrifying effect Effects 0.000 description 1
- 238000005192 partition Methods 0.000 description 1
- 238000000247 postprecipitation Methods 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 238000012827 research and development Methods 0.000 description 1
- 238000005070 sampling Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
Classifications
-
- 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
- C02F3/30—Aerobic and anaerobic processes
- C02F3/301—Aerobic and anaerobic treatment in the same reactor
-
- 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
- C02F2203/00—Apparatus and plants for the biological treatment of water, waste water or sewage
- C02F2203/006—Apparatus and plants for the biological treatment of water, waste water or sewage details of construction, e.g. specially adapted seals, modules, connections
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/08—Chemical Oxygen Demand [COD]; Biological Oxygen Demand [BOD]
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/14—NH3-N
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Biodiversity & Conservation Biology (AREA)
- Microbiology (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
The invention discloses a corner adjustable type wastewater treatment biochemical reactor which is of annular gallery shape and comprises an anaerobic section (3), an anoxic section (5) and an aerobiotic section (7), wherein the anaerobic section (3) is connected with a water inlet pipe (1); the aerobiotic section (7) is connected with a water outlet pipe (8); a moveable separating plate (4) is arranged on the annular gallery; a slide rail (21) is arranged on an annular gallery wall; the moveable separating plate (4) is located on the slide rail (21); a driving device (20) is arranged at the center of the annular gallery; the moveable separating plate (4) is connected with the driving device (20) through a rotating arm (17); a water hole (22) is formed in the moveable separating plate (4). The corner adjustable type wastewater treatment biochemical reactor is reasonable in structure design; the relative staying time of each section can be flexibly adjusted according to the quality condition of the to-be-treated water; the microbial population is relative independent; the corresponding biochemical reaction environment is more stable; when different wastewater is treated, the efficient biochemical treatment can be kept; a settling pond is arranged at the center, so that the purifying effect is more excellent.
Description
Technical field
The present invention relates to a kind of biological treatment device is and in particular to a kind of corner adjustable type wastewater treatment biochemical reaction
Device.
Background technology
Traditional a/a/o technique is typical urban sewage treatment process, can solve the organic of sewage to a certain extent
Thing removes the problem with denitrogenation dephosphorizing.The hydraulic detention time of traditional a/a/o technique anaerobism section, anoxia section and aerobic section it
Than, that is, the ratio of each conversion zone volume, generally 1:1:3~4, Relative volumes are fixed, and controllability is poor, special for water quality treatment
Different industrial wastewater each conversion zone hydraulic detention time and process load and be difficult to adjust it is impossible to adapt to high salinity, high cod, highly concentrated
Degree hardly degraded organic substance, high nitrogen, some industrial wastewaters of high phosphorus, limit development and the application of such biochemical reactor.
Chinese patent cn201110157920.0 discloses a kind of " adjustable biochemical tank and its carry out the adjustable of water process
A/a/o technique ", although technique is changeable, fails fundamentally to change the actual volume of anaerobism section, anoxia section and aerobic section respectively
Size and relative hydraulic detention time ratio." five factors are adjustable, and sewage disposal fills Chinese patent cn200510132777.4
Put ", anaerobic pond, anoxic pond, the volume fraction of Aerobic Pond can adjust, however it is necessary that by anaerobic pond, anoxic pond and Aerobic Pond according to
Secondary arrangement, and it is linked to be rectangle great Chi, adjusted with moving partition, several conversion zone arrangement forms are single, be difficult to adjust,
It is of limited application.Chinese patent cn 103408143a discloses a kind of " lattice adjustable type anaerobic- anoxic- oxic biochemical reaction
Its regulation of device " is to be realized by the change of total number of divisions, and the accurate adjustment of " lattice " mode discontinuous.Chinese patent
The regulation that cn103755024a discloses " a kind of swinging adjustable type anaerobic- anoxic- oxic biochemical reactor " is confined to gallery
Front 2 parts, scope is mainly in anaerobism section and anoxia section, and the main part (outside gallery) of aerobic section can not be adjusted.
Therefore, necessary on the basis of existing technology, a kind of reasonable in design, compact conformation of research and development, be easy to adjust
Section, range of accommodation are wide, and technique is various, adapts to the corner adjustable type wastewater treatment biochemical reactor of change of water quality.
Content of the invention
Goal of the invention: the invention aims to solving the deficiencies in the prior art, provide a kind of reasonable in design, structure tight
Gather, can easily be accommodated, range of accommodation wide, technique is various, adapts to the corner adjustable type wastewater treatment biochemical reactor of change of water quality.
Technical scheme: in order to realize the purpose of the present invention, the technical solution used in the present invention is:
A kind of corner adjustable type wastewater treatment biochemical reactor, its ringwise gallery type, become reconciled including anaerobism section, anoxia section
Oxygen section, anaerobism section is connected with water inlet pipe, and aerobic section is connected with outlet pipe;Along waste water flow direction, in annular gallery setting 1~
5 pieces of mobile dividing plates, are provided with slide rail on annular gallery wall, and mobile dividing plate is located on slide rail;Annular gallery center is arranged
There is actuating device, mobile dividing plate is connected with actuating device by pivoted arm, and the described bottom of mobile dividing plate or top were provided with
Water orifice;
Described annular gallery bottom is provided with immobilized film device, and described immobilized film device includes aeration house steward, with
The aeration main that aeration house steward is connected, the aeration branch pipe being connected with aeration main, aeration branch pipe end is provided with aeration head, and aeration props up
Pipe is provided with control air valve;
The central area bottom position of described annular gallery is provided with sedimentation tank, sedimentation tank top and sedimentation tank outlet canal phase
Even, sedimentation tank outlet canal is connected with total outlet pipe, and sedimentation tank bottom is provided with sedimentation tank inhalant region, sedimentation tank Cun Ni area and scrapes mud
Machine;
Outlet pipe is connected with sedimentation tank inhalant region.
Preferably, above-described corner adjustable type wastewater treatment biochemical reactor, the annular of biochemical reactor
Gallery bottom is provided with underwater propeller in anaerobism section or anoxia section section start;In annular gallery along latter 1/2 of water (flow) direction
Set up separately and put immobilized film device, 1/2 part is provided with mobile aeration device before annular gallery is along water (flow) direction, described
Mobile aeration device includes aeration head, the pipeline being connected with aeration head, the aerator being connected with pipeline and be arranged on air blast owner
Valve on pipeline.
Preferably, above-described corner adjustable type wastewater treatment biochemical reactor, anaerobism section initiating terminal and heavy
Dian Chicunni is connected with mud return line between area;The end of anoxia section initiating terminal and aerobic section is connected with sewage backflow pipe;Dirty
Mud return duct and sewage backflow pipe are arranged along outside annular gallery.
Preferably, above-described corner adjustable type wastewater treatment biochemical reactor, annular gallery is provided with 2
Block moves dividing plate, is sequentially allocated as anaerobism section, anoxia section and aerobic section along water (flow) direction;Wherein anaerobism section, anoxia section and aerobic
The ratio of the annular gallery angle of Duan Suozhan is 1:1:3,1:1:3.5,1:1:4,1:1:8,1:1:10,3:2:7,4:2:7,3:1:8,
4:1:8,1:3:8 or 1:4:8.
Preferably, above-described corner adjustable type wastewater treatment biochemical reactor, annular gallery is provided with 5
Individual mobile dividing plate, annular gallery is provided with 5 mobile dividing plates, is sequentially allocated along water (flow) direction and becomes reconciled for anoxia section, anaerobism section
Oxygen section, wherein anoxia section are arranged for the nitrosation section of nitrosation biochemical reaction, and anaerobism section is arranged for Anammox
The Anammox section of biochemical reaction, it is made up of isometric 4 parts;Described nitrosation section, Anammox section are become reconciled
The ratio of the annular gallery angle shared by oxygen section is that (advantage using this ratio is for detesting by preposition for nitrosation section to 1:2:3 or 1:2:4
Anaerobic ammonium oxidation is prepared, and takes into full account that Anammox section has enough time of staying, is suitable for the culture of anaerobic ammonia oxidizing bacteria
With propagation.The present invention is screened by many experiments, and the convenience simultaneously taking into account engineer applied selectes this ratio);Anammox section
For anaerobic state, Anammox section adds lid so that dissolved oxygen value is lower in waste water, controls dissolved oxygen to be less than 1.0mg/l,
Cover the logical upper exhaustor of punching;Nitrosation section is provided with micro- aerator, controls dissolved oxygen in 0.5~1.5mg/l;Aerobic section sets
It is equipped with aerator, control dissolved oxygen to be more than 2.0mg/l.
Preferably, above-described corner adjustable type wastewater treatment biochemical reactor, described composition anaerobism ammonia
The water hole mouth of the mobile dividing plate of oxidation panel is alternately located in bottom and the top of mobile dividing plate successively, simultaneously two pieces of mobile dividing plates it
Between distance be controlled to 0.8~1.2 times of annular gallery width so that current carry out upper and lower baffling flowing;Anammox section
Between two pieces of mobile dividing plates, effective water section of crossing is provided with filler, can be conducive to the growth of Anaerobe film;Described filler is
Suspension ball filler;The water hole mouth on mobile dividing plate top is provided with grid, and the spherical filler stream that prevents from suspending goes out.
Preferably, above-described corner adjustable type wastewater treatment biochemical reactor, described sedimentation tank is spoke
Flow settling pond, using center water inlet, the method for operation of peripheral effluent.
Preferably, above-described corner adjustable type wastewater treatment biochemical reactor, mobile dividing plate passes through pivoted arm
It is connected with actuating device, pivoted arm is rotated by actuating device, drive mobile dividing plate to move up and down along slide rail and realize anaerobism
The distribution of section, anoxia section and aerobic section volume and adjustment.
Preferably, above-described corner adjustable type wastewater treatment biochemical reactor, described actuating device with
Mud scraper is connected.
The present invention can require according to the characteristic of concrete waste water, processing requirement and operation, flexible employing dividing plate
Anaerobism section, anoxia section and aerobic section are separated so as in microbial population relatively independent, corresponding biochemical reaction
Environment is relative to held stationary.Adjust the position of dividing plate by machinery, make each conversion zone account for different annular gallery angles;?
Annular gallery is wide, and under conditions of waiting depth, the ratio of the annular gallery angle shared by each conversion zone is exactly each conversion zone dischargeable capacity
Ratio, that is, the ratio of each conversion zone hydraulic detention time.
When processing sanitary sewage, consider to remove cod and denitrogenation dephosphorizing, shared by anaerobism section, anoxia section and aerobic section simultaneously
For 1:1:3,1:1:3.5 or 1:1:4 so forms the a/a/o denitrification dephosphorization technique of classics to angle ratio.When wastewater treatment needs to prolong
When aeration when, anaerobism section, anoxia section and angle shared by aerobic section are than for 1:1:8 or 1:1:10.The present invention is for process Industry Waste
Water is it is considered to extend anaerobism section relative retention time, the effect of reinforced anaerobic section biochemical treatment, anaerobism section, anoxia section and aerobic section
Shared angle is than for 3:2:7 or 4:2:7.The present invention, when processing high phosphorus waste water, needs emphatically to carry out dephosphorization to detest it is considered to extend
Oxygen section, aerobic section relative retention time, are beneficial to anaerobic phosphorus release and aerobic phosphorus absorption, anaerobism section, anoxia section and angle shared by aerobic section
Degree ratio is 3:1:8 or 4:1:8.The present invention provide corner adjustable type wastewater treatment biochemical reactor for process high-nitrogen waste water,
Consider emphatically during denitrogenation it is considered to shorten anaerobism section relative retention time, extend anoxia section, aerobic section relative retention time, with profit
In technique denitrogenation, anaerobism section, anoxia section and angle shared by aerobic section are than for 1:3:8 or 1:4:8.
When only setting a mobile dividing plate, anaerobism section can be cancelled, the ratio of angle shared by anoxia section and aerobic section for 1:2, is formed
Traditional a/o anoxia denitrification process;Or cancel anoxia section, the ratio of angle shared by anaerobism section and aerobic section for 1:2, forms traditional a-o and detests
Oxygen dephosphorization process.
The corner adjustable type wastewater treatment biochemical reactor that the present invention provides, wherein returned sludge are located at anaerobism section and initiate
Place, anoxia section nitrification liquid flows back in the section start of anoxia section, enters gallery by pump and pipeline.The present invention sets in gallery bottom
Put immobilized film device, by controlling Air Valve Control aeration rate, anaerobism section closes control air valve, and anoxia section, aerobic section are controlled by regulation
Controlling aeration rate, anoxia section keeps mixed liquor dissolved oxygen in 0.2~2.0mg/l to air valve, and aerobic section keeps mixed liquor dissolved oxygen
More than 2.0mg/l.
Annular gallery latter half due to biochemical reactor is mainly aerobic section, so only in annular gallery along current
The aerator of the rear 1/2 part setting fixation in direction;And in front 1/2 part, needing the local setting moving aeration of aeration
Device, this structure setting not only can reduce equipment investment, and it is convenient that operation runs, and Air Exposure effect is good.Moving aeration
Device by aeration head, pipeline and connects the valve of aerator main line and forms, and installs as needed, tears down and reconstruct, moves to needs
The place of aeration is installed again.Mobile aeration device typically along the outer side shifting of annular gallery, connection and reasonable arrangement, easy for installation.Anaerobism section,
Sludge reflux between anoxia section, aerobic section and sedimentation tank and return of waste water, by reflux pump and pipeline realization, reflux pump and pipe
Road is arranged along the line in the outside of annular gallery.
In addition to being adjusted to above-mentioned many sampling technologies moreover it is possible to be adjusted to anaerobism, anoxia, aerobe coupling or repeatedly between
Every the Various Complex technique processing.Can corner adjustable type wastewater treatment biochemical reactor arrange in annular gallery 5 movements every
Plate, is sequentially allocated as anoxia section (nitrosation section), anaerobism section (Anammox section) and aerobic section, so composition along water (flow) direction
The new technology of " nitrosation -- Anammox -- Aerobic Process for Treatment ", be primarily adapted for processing ammonia nitrogen is high and the low waste water of carbon-nitrogen ratio.Its
Middle Anammox section is made up of isometric 4 fractions, constitutes the water hole mouth of the mobile dividing plate of Anammox section, successively
It is alternately located in bottom and the top of dividing plate, between two dividing plates, distance controlling is 0.8~1.2 times of annular gallery width simultaneously, makes
Obtain current to carry out;Between two dividing plates of Anammox section, effective water section of crossing arranges filler, is conducive to the shape of Anaerobe film
Become and growth.Anammox section substantially defines the abr reactor of the improvement of filler, Anammox biochemical reaction
Occur in the main abr reactor in improvement.Anaerobic ammonia oxidizing bacteria can be cultivated in the abr reactor of improvement and be bred:
Baffling flowing up and down makes waste water and Anaerobe film contact-enhancing;It is reasonable to detest to obtain that Anammox section is added a cover
Oxygen condition so that in waste water do value lower;Cover the logical upper exhaustor of punching, be the biogas in order to exclude generation in time;Setting is filled out
Material, can extend the time of staying of anaerobic sludge, be conducive to the growth of Anaerobe.
The ratio of the nitrosation section of short distance, Anammox section and the annular gallery angle shared by aerobic section is 1:2:3 or 1:
2:4;Short distance nitration section arranges micro- aerator, controls dissolved oxygen in 0.5~1.5mg/l, Anammox section is anaerobic state,
Control dissolved oxygen to be less than 1.0mg/l, aerobic section arranges aerator, control dissolved oxygen to be more than 2.0mg/l.Short distance nitration section is main
Control and in waste water, generate nitrite nitrogen, and the nitrite nitrogen generating enters Anammox section, can carry out Anammox
Under microbial action, reacting with ammonia nitrogen in anaerobic condition, generating nitrogen, thus realizing denitrogenation.If add in reactor and
Culture is that the anaerobic ammonia oxidizing bacteria of whole process autotrophic then defines " Anammox canon technique ".If in short distance nitrosation
Section adds and cultivate is nitrosation strain, Anammox section add and cultivate be autotrophy anaerobic ammonia oxidizing bacteria, then
Define " Anammox oland technique ".Whole strict control do concentration, controls and for nitrifying process to rest on nitrosation rank
Section, completes half nh in waste water4 +- n changes into no2 -- n, more separately remaining nh4 +- n and no2 -- n reacts, and carry out is anaerobism ammonia
Oxidation reaction is such that it is able to realize high efficiency denitrogenation.It is suitable to process the relatively low high-nitrogen waste water of c/n.
The setting of polylith dividing plate and regulation, can form " Anammox canon+ is aerobic " or " Anammox oland work
Skill+aerobic " new technology, it is possible to resolve traditional a/a/o technique can not process the problem of the relatively low high-nitrogen waste water of c/n well.Anaerobism
Ammonia oxidation process is also the later Main Trends of The Development in denitrogenation dephosphorizing, and the present invention can combine Anammox well, becomes
There is the abr anaerobism workshop section of the improvement of filler.A/a/o technique can be overcome cannot to form Anammox workshop section or Anammox
The problem that effect is very faint, the advantage of being difficult to occupies anaerobic processes, achieves the unforeseeable technique effect of integrated artistic.
Mobile dividing plate is realized along the movement on gallery direction by railroad, and biochemical reactor annular center is provided with
Actuating device is connected with the mobile dividing plate equipped with slide rail rotating pivoted arm, pivoted arm, to realize distribution and the adjustment of each segment volumes.
Against water (flow) direction, adjust the mobile dividing plate of isolation aerobic section first, then dividing plate is fixed;Dismantle the company of pivoted arm and dividing plate
Connect, pivoted arm is connected with another piece of mobile dividing plate, another piece of mobile dividing plate is adjusted, fixes, so just can achieve a pivoted arm
Regulation to the mobile dividing plate of polylith, adjusting means configuration is reasonable, easy to adjust, efficiency high.
Beneficial effect: the present invention provide corner adjustable type wastewater treatment biochemical reactor compared to the prior art have with
Lower advantage:
1st, the corner adjustable type wastewater treatment biochemical reactor that the present invention provides, compact conformation is reasonable in design, can be according to treating
Each section of relative retention time of water quality treatment situation flexible, to carry out flexible isolation to each section using dividing plate so as in
Microbial population is relatively independent, and the environment of corresponding biochemical reaction is more steady.Thus, the biochemical reactor that the present invention provides exists
When processing different waste water, efficient biochemical all can be kept to process, make reactor obtain the treatment effect of stability and high efficiency on the whole.
2nd, the present invention provide corner adjustable type wastewater treatment biochemical reactor, adapt to different quality characteristic waste water or
The process demand of the waste water of change water quality, is widely used.Range of accommodation is wide, can relate to whole annular gallery, whole biochemical reaction
Each conversion zone of device.Adjustable handling process is diversified further simultaneously, and a/a/o technique can be overcome cannot to form anaerobism ammonia
The problem that oxidation section or Anammox effect are very faint, the advantage of being difficult to occupies anaerobic processes, " nitrosation is detested to adjust formation
Anaerobic ammonium oxidation is aerobic " combined treatment process, achieve unforeseeable new technique effect well.
3rd, the present invention provide corner adjustable type wastewater treatment biochemical reactor, main part pass through actuating device, pivoted arm,
Slide rail, mobile dividing plate are very convenient to adjust, and can achieve accurate adjustment, and work efficiency is higher.Mobile aeration device, mud return
Stream device and sewage backflow device, all arrange along the line by outside annular gallery, succinct, rationally, conveniently.
4th, the corner adjustable type wastewater treatment biochemical reactor that the present invention provides, using immobilized film device and moving aeration
Device, and it is provided with sedimentation tank in biochemical reactor central area bottom, sedimentation tank bottom is provided with sedimentation tank inhalant region, sedimentation tank
Cun Ni area and mud scraper etc., can make full use of the center of annular reactor so that structure more optimizes, and by " biochemical
Reaction-spoke stream precipitates " close-coupled processing, can preferably process waste water.
Brief description
The cross-sectional view of the biochemical reactor that Fig. 1 provides for the present invention.
The planar structure schematic diagram of the biochemical reactor that Fig. 2 provides for the present invention.
A kind of sectional plan structural representation of the biochemical reactor that Fig. 3 provides for the present invention.
A kind of outer shroud gallery that Fig. 4 provides for the present invention is along the stepwise schematic views of each conversion zone of water (flow) direction.
As illustrated, biochemical reactor ingredient is as follows: 1: water inlet pipe, 2: propeller, 3: anaerobism section, 4: mobile every
Plate, 5: anoxia section, 6: mobile aeration device, 7: aerobic section, 8: outlet pipe, 9: aeration house steward, 10: aeration main, 11: aeration props up
Pipe, 12: aeration head, 13: control air valve, 14: total outlet pipe, 15: mud return line, 16: sewage backflow pipe, 17: pivoted arm, 18: heavy
Shallow lake pond, 19: sedimentation tank outlet canal, 20: actuating device, 21: slide rail, 22: water hole mouth, 23: mud scraper, 24: sedimentation tank water inlet
Area, 25: sedimentation tank Cun Ni area, 26: filler.
Specific embodiment
Below in conjunction with the accompanying drawings and specific embodiment, it is further elucidated with the present invention it should be understood that these embodiments are merely to illustrate
The present invention rather than restriction the scope of the present invention, after having read the present invention, those skilled in the art are each to the present invention
The modification planting the equivalent form of value all falls within the application claims limited range.
Embodiment 1
As depicted in figs. 1 and 2, a kind of corner adjustable type wastewater treatment biochemical reactor, described reactor ringwise corridor
Road formula, is provided with 1 continuously wide contour water gallery excessively, is assigned as anaerobism section 3, anoxia section 5 and aerobic section 7, wherein edge
Waste water flow direction, arranges 2 pieces of mobile dividing plates 4 on initial gallery, arranges slide rail 21, biochemical reactor on annular gallery wall
Annular center is provided with actuating device 20 and is connected with the mobile dividing plate 4 on slide rail 21 rotating pivoted arm 17, pivoted arm 17, by moving
Dynamic dividing plate 4 is realizing distribution and the adjustment of each segment volumes.The bottom of mobile dividing plate 4 or top are provided with water hole mouth 22.
The precipitation of the corner adjustable type wastewater treatment biochemical reactor that the present invention provides, wherein biochemical reactor sedimentation tank is dirty
Mud backflow is located at anaerobism section initiating terminal, relies on mud return line 15 to flow back;The backflow of anoxia section nitrification liquid is located at the initial of anoxia section
End, relies on sewage backflow pipe 16 to flow back.The present invention fills along the rear 1/2 part setting immobilized film of water (flow) direction in annular gallery
Put, described immobilized film device includes aeration house steward 9, the aeration main 10 being connected with aeration house steward 9, with aeration main 10 phase
Aeration branch pipe 11 even, aeration branch pipe 11 end is provided with aeration head 12, and aeration branch pipe 11 is provided with control air valve 13.By controlling air valve
13 control aeration rates, anaerobism section closes control air valve, and anoxia section and aerobic section control aeration rate, anoxia by adjusting control air valve 13
Section keeps mixed liquor dissolved oxygen in 0.5~2.0mg/l, and aerobic section keeps mixed liquor dissolved oxygen to be more than 2.0mg/l.Needing aeration
Local setting mobile aeration device 6.
Mobile aeration device by aeration head, pipeline and connects the valve of aerator main line and forms, and installs as needed, tears open
The place changing, moving to the aeration of needs is installed again.Mobile aeration device typically along the outer side shifting of annular gallery, each conversion zone it
Between sludge reflux and return of waste water, realized by reflux pump and pipeline, reflux pump and pipeline are along the line in the outside of annular gallery
Arrangement.
The center setting sedimentation tank 18 of biochemical reactor is radical sedimentation basin, and waste water is after treatment by outlet pipe 8
Enter sedimentation tank 18, using center water inlet, the method for operation of peripheral effluent, intake water distribution by sedimentation tank inhalant region 24, sedimentation tank
Outlet canal 19 catchments, through total outlet pipe 14 water outlet.Sludge reflux is back to instead through mud return line 15 by sedimentation tank Cun Ni area 25
Answer the biochemical reaction section needed for device.Biochemical reactor annular center is provided with actuating device when not being adjusted, as precipitation
The actuating device of the mud scraper 23 in pond.
When processing sanitary sewage, before processing sanitary sewage water quality index: cod (COD) is 300~1000mg/
L, ammonia nitrogen is 30~50mg/l, and total phosphorus is 5~8mg/l, using above-described biochemical reactor, constitutes anaerobism section, anoxia section
With the ratio of the annular gallery angle shared by aerobic section (wide in annular gallery, under conditions of waiting depth, that is, each section distribution have
Imitate the ratio of volume or the ratio of each section of hydraulic detention time), it is 1:1:3,1:1:3.5 or 1:1:4.Using biochemical reaction of the present invention
After device process, the water quality index of sanitary sewage: cod is 50~80mg/l, ammonia nitrogen≤5.0mg/l, and total phosphorus≤1.0mg/l is (through this
After bright reactor for treatment, the water quality index of water outlet refers to the mensure numerical value of the water outlet after post precipitation unit, in following examples
It is all such).
Embodiment 2
Using the present invention provide reactor for treatment commonly industrial wastewater, described reactor cross water Corridor Design arrangement and
The separation mode of each biochemical reaction section, the operation control mode of reactor and aerator and parameter etc. are all with embodiment 1.With reality
Apply the difference being directed to process object unlike example 1, and adopt different anaerobism sections, anoxia section and aerobic section distribution volumetric ratio.
For the industrial wastewater processing difficult degradation, before processing industrial wastewater water quality index: cod is 1000~3000mg/l,
Ammonia nitrogen is about 30mg/l, and total phosphorus is about 5mg/l, using above-described swinging adjustable type anaerobic- anoxic- oxic biochemical reaction
Device, needs to extend anaerobism section relative to hydraulic detention time, the effect of reinforced anaerobic section biochemical treatment, anaerobism section, anoxia section are become reconciled
The ratio of the annular gallery angle shared by oxygen section is 3:2:7 or 4:2:7, using the water quality of biochemical reactor processed waste water of the present invention
Index: cod is 50~150mg/l, ammonia nitrogen≤5.0mg/l, total phosphorus≤1.0mg/l.
Embodiment 3
The reactor for treatment high phosphorus waste water being provided using the present invention, described reactor crosses water Corridor Design arrangement and each life
Change the separation mode of conversion zone, the operation control mode of reactor and aerator and parameter etc. are all with embodiment 1.With embodiment
It is directed to the difference of process object unlike 1, and adopt different anaerobism sections, anoxia section and aerobic section volumetric ratio.
For processing high phosphorus waste water, before processing industrial wastewater water quality index: cod (COD) is 400~1000mg/
L, ammonia nitrogen is about 10mg/l, and total phosphorus is about 20mg/l, biochemical using above-described swinging adjustable type anaerobic- anoxic- oxic
Reactor, needs to carry out dephosphorization, extends anaerobism section, aerobic section relative to hydraulic detention time, is beneficial to anaerobic phosphorus release and aerobic suction
Phosphorus, the ratio of anaerobism section, anoxia section and the annular gallery angle shared by aerobic section is 3:1:8 or 4:1:8, biochemical anti-using the present invention
The water quality index of device processed waste water: cod is answered to be 50~80mg/l, ammonia nitrogen≤5.0mg/l, total phosphorus≤1.0mg/l.
From example 1~3 it can be seen that reactor for treatment of the present invention is widely applicable, in the face of polytype water quality waste water all can be protected
The advantage holding efficient biochemical process.
Embodiment 4
Using corner adjustable type wastewater treatment biochemical reactor processing variation water quality waste water, described reactor crosses water gallery
Design arrangement and the separation mode of each biochemical reaction section, the operation control mode of reactor and aerator and parameter etc. are all with real
Apply example 1.It is directed to the change of waste water quality as different from Example 1, and adopt different anaerobism sections, anoxia section and aerobic section to divide
Join volumetric ratio, and timely adjusted.
Originally pending waste water quality is with embodiment 1, based on sanitary sewage, before processing sanitary sewage water quality index: cod
For 300~1000mg/l, ammonia nitrogen is 30~50mg/l, and total phosphorus is 5~8mg/l, is detested using above-described swinging adjustable type
Oxygen-anaerobic-aerobic biochemical reactor, the distribution volumetric ratio constituting anaerobism section, anoxia section and aerobic section is 1:1:3, using this
After open-birth reactor for treatment, the water quality index of sanitary sewage: cod is 50~80mg/l, ammonia nitrogen≤5.0mg/l, total phosphorus≤
1.0mg/l.
When above-mentioned wastewater treatment influent quality changes or fluctuates, (for example have a small amount of when the Industrial Zone built
Industrial wastewater enters sewage treatment plants and processes, or has industrial wastewater pipe leakage to enter city planting ductwork) waste water of before processing becomes
Turning to cod is 500~2000mg/l, ammonia nitrogen 25~50mg/l, total phosphorus 3~5mg/l, if anaerobism section, anoxia section and aerobic section
Distribution volumetric ratio remain in that to be than for 1:1:3, then be not suitable with present influent quality, longtime running can lead to biochemical treatment
Efficiency declines, and particularly the value of water outlet cod can raise, and leads to water outlet not up to standard.Now should be to anaerobism section, anoxia section and aerobic
Section distribution volumetric ratio is adjusted, and extends anaerobism section relative to hydraulic detention time, the effect of reinforced anaerobic section biochemical treatment, anaerobism
Section, anoxia section and aerobic section distribution volumetric ratio are 3:2:7 or 4:2:7.Through such adjustment, increase aerobic section aeration simultaneously
Amount, reactor adapts to present influent quality, the water quality index of waste water after adjustment post-reactor process: cod is 50~80mg/
L, ammonia nitrogen≤5.0mg/l, total phosphorus≤1.0mg/l, so that reactor of the present invention remains that high-performance bio is processed.
From example 4 it can be seen that reactor of the present invention adapts to the process of change waste water quality, there is flexible adjustment.
Embodiment 5
As Fig. 3 and Fig. 4, a kind of corner adjustable type wastewater treatment biochemical reactor, ringwise gallery type, it is provided with 1 company
Continuous wide contour water gallery excessively, is assigned as anoxia section (nitrosation section), anaerobism section (Anammox section) and aerobic section, its
Middle along waste water flow direction, on initial gallery arrange 5 pieces of mobile dividing plates 4, on gallery wall arrange railroad 21, movement every
Plate is realized along the movement on gallery direction by railroad, and biochemical reactor annular center is provided with actuating device 20 to revolve
Walk around arm 17, pivoted arm 17 is connected with the mobile dividing plate 4 on slide rail 21, thus movement moves dividing plate 4 to realize each point accordingly
The distribution of Duan Rongji and adjustment.Wherein Anammox section is made up of isometric 4 fractions, nitrosation section, Anammox
The ratio of section and the annular gallery angle shared by aerobic section is 1:2:3 or 1:2:4;Anammox section is anaerobic state, anaerobism ammonia
Oxidation panel adds lid so that do value is lower in waste water, controls dissolved oxygen to be less than 1.0mg/l, covers the logical upper exhaustor of punching;Sub-
Nitration section is provided with micro- aerator, controls dissolved oxygen in 0.5~1.5mg/l;Aerobic section is provided with aerator, controls dissolving
Oxygen is more than 2.0mg/l.Constitute the water hole mouth of the mobile dividing plate of Anammox section, be alternately located in the bottom of dividing plate and upper successively
Portion, between two dividing plates, distance controlling is 1.0 times of annular gallery width so that current carry out upper and lower baffling flowing simultaneously;Anaerobism
Between two dividing plates of ammoxidation section, effective water section of crossing arranges filler 26, is conducive to the growth of Anaerobe film.
Mobile aeration device and backflow etc. are arranged with example 1.Sedimentation tank is arranged with example 1.
When the relatively low high-nitrogen waste water of process c/n, before processing water quality index: cod (COD) is 300~500mg/
L, ammonia nitrogen is 500~1000mg/l, and total phosphorus is 5~8mg/l, using above-described biochemical reactor, constitutes nitrosation section, detests
The ratio of the annular gallery angle shared by anaerobic ammonium oxidation section and aerobic section is 1:2:3 or 1:2:4.At biochemical reactor of the present invention
Water quality index after reason: cod is 50~80mg/l, ammonia nitrogen≤20.0mg/l, total phosphorus≤1.0mg/l.
The above is only the preferred embodiment of the present invention it is noted that ordinary skill people for the art
For member, under the premise without departing from the principles of the invention, some improvements and modifications can also be made, these improvements and modifications also should
It is considered as protection scope of the present invention.
Claims (9)
1. a kind of corner adjustable type wastewater treatment biochemical reactor is it is characterised in that its ringwise gallery type, including anaerobism section
(3), anoxia section (5) and aerobic section (7), anaerobism section (3) is connected with water inlet pipe (1), and aerobic section (7) is connected with outlet pipe (8);Edge
Waste water flow direction, arranges 1~5 piece of mobile dividing plate (4) in annular gallery, is provided with slide rail (21) on annular gallery wall,
Mobile dividing plate (4) is located on slide rail (21);Annular gallery center is provided with actuating device (20), and mobile dividing plate (4) is passed through
Pivoted arm (17) is connected with actuating device (20), and the described bottom of mobile dividing plate (4) or top are provided with water hole mouth (22);
Described annular gallery bottom is provided with immobilized film device, and described immobilized film device includes aeration house steward (9), with exposure
The aeration main (10) that gas house steward (9) is connected, the aeration branch pipe (11) being connected with aeration main (10), aeration branch pipe (11) end
It is provided with aeration head (12), aeration branch pipe (11) is provided with control air valve (13);
The central area bottom position of described annular gallery is provided with sedimentation tank (18), sedimentation tank (18) top and sedimentation tank water outlet
Canal (19) is connected, and sedimentation tank outlet canal (19) is connected with total outlet pipe (14), and sedimentation tank (18) bottom is provided with sedimentation tank water inlet
Area (24), sedimentation tank Cun Ni area (25) and mud scraper (23);
Outlet pipe (8) is connected with sedimentation tank inhalant region (24).
2. corner adjustable type wastewater treatment biochemical reactor according to claim 1 it is characterised in that: biochemical reactor
Annular gallery bottom is provided with underwater propeller (2) in anaerobism section (3) or anoxia section (5) section start;In annular gallery along current
The rear 1/2 part setting immobilized film device in direction, before annular gallery is along water (flow) direction, 1/2 part is provided with mobile exposure
Device of air (6), described mobile aeration device (6) includes aeration head, pipeline and the valve connecting aerator main line.
3. corner adjustable type wastewater treatment biochemical reactor according to claim 1 it is characterised in that: anaerobism section (3) rise
It is connected with mud return line (15) between top and sedimentation tank Cun Ni area (25);Anoxia section (5) initiating terminal and the end of aerobic section (7)
End is connected with sewage backflow pipe (16);Mud return line (15) and sewage backflow pipe (16) are arranged along outside annular gallery.
4. corner adjustable type wastewater treatment biochemical reactor according to claim 1 it is characterised in that: set in annular gallery
It is equipped with 2 pieces of mobile dividing plates (4), be sequentially allocated as anaerobism section (3), anoxia section (5) and aerobic section (7) along water (flow) direction;Anaerobism section
(3), the ratio of anoxia section (5) and the annular gallery angle shared by aerobic section (7) is 1:1:3,1:1:3.5,1:1:4,1:1:8,1:
1:10,3:2:7,4:2:7,3:1:8,4:1:8,1:3:8 or 1:4:8.
5. corner adjustable type wastewater treatment biochemical reactor according to claim 1 it is characterised in that: set in annular gallery
It is equipped with 5 mobile dividing plates (4), be sequentially allocated as anoxia section (5), anaerobism section (3) and aerobic section (7) along water (flow) direction, wherein scarce
Oxygen section (5) is arranged for the nitrosation section of nitrosation biochemical reaction, and it is biochemical anti-that anaerobism section (3) is arranged for Anammox
The Anammox section answered, it is made up of isometric 4 parts;Described nitrosation section, Anammox section and aerobic section (7)
The ratio of shared annular gallery angle is 1:2:3 or 1:2:4;Anammox section is provided with lid so that useless oxygen in water
Value is lower, controls dissolved oxygen to be less than 1.0mg/l, lid is provided with exhaustor;Nitrosation section is provided with micro- aerator, controls
Dissolved oxygen is in 0.5~1.5mg/l;Aerobic section is provided with aerator, controls dissolved oxygen to be more than 2.0mg/l.
6. corner adjustable type wastewater treatment biochemical reactor according to claim 5 it is characterised in that: described composition is detested
The water hole mouth (22) of the mobile dividing plate (4) of anaerobic ammonium oxidation section is alternately located in bottom and the top of mobile dividing plate (4) successively, simultaneously
Between two pieces of mobile dividing plates (4), distance controlling is 0.8~1.2 times of annular gallery width so that current carry out upper and lower baffling stream
Dynamic;Between the mobile dividing plate (4) of two pieces of Anammox section, effective water section of crossing is provided with filler (26), is conducive to Anaerobe
The growth of film;Described filler (26) is suspension ball filler;The water hole mouth (22) on mobile dividing plate (4) top is provided with lattice
Grid, the spherical filler stream that prevents from suspending goes out.
7. corner adjustable type wastewater treatment biochemical reactor according to claim 1 it is characterised in that: described sedimentation tank
(18) it is radical sedimentation basin, using center water inlet, the method for operation of peripheral effluent.
8. corner adjustable type wastewater treatment biochemical reactor according to claim 1 it is characterised in that: mobile dividing plate (4)
It is connected with actuating device (20) by pivoted arm (17), pivoted arm (17) is rotated by actuating device (20), drive mobile dividing plate
(4) distribution and the adjustment of anaerobism section (3), anoxia section (5) and aerobic section (7) volume is realized along slide rail (21) movement.
9. corner adjustable type wastewater treatment biochemical reactor according to claim 1 it is characterised in that: described transmission dress
Put (20) to be connected with mud scraper (23).
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