CN110498568A - A kind of sewage simultaneous phosphorus and nitrogen removal integrated apparatus and method - Google Patents
A kind of sewage simultaneous phosphorus and nitrogen removal integrated apparatus and method Download PDFInfo
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- CN110498568A CN110498568A CN201910809590.5A CN201910809590A CN110498568A CN 110498568 A CN110498568 A CN 110498568A CN 201910809590 A CN201910809590 A CN 201910809590A CN 110498568 A CN110498568 A CN 110498568A
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- sewage
- water
- sedimentation basin
- contact oxidation
- pond
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- 239000010865 sewage Substances 0.000 title claims abstract description 53
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 title claims abstract description 46
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 title claims abstract description 23
- 229910052757 nitrogen Inorganic materials 0.000 title claims abstract description 23
- 229910052698 phosphorus Inorganic materials 0.000 title claims abstract description 23
- 239000011574 phosphorus Substances 0.000 title claims abstract description 23
- 238000000034 method Methods 0.000 title claims abstract description 15
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 58
- 238000004062 sedimentation Methods 0.000 claims abstract description 40
- 230000001954 sterilising effect Effects 0.000 claims abstract description 33
- 238000004659 sterilization and disinfection Methods 0.000 claims abstract description 33
- 238000001914 filtration Methods 0.000 claims abstract description 32
- 230000003647 oxidation Effects 0.000 claims abstract description 30
- 238000007254 oxidation reaction Methods 0.000 claims abstract description 30
- 239000000945 filler Substances 0.000 claims abstract description 25
- 230000005484 gravity Effects 0.000 claims abstract description 7
- 239000004744 fabric Substances 0.000 claims abstract description 3
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 26
- 238000006243 chemical reaction Methods 0.000 claims description 13
- 229910052742 iron Inorganic materials 0.000 claims description 13
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 claims description 6
- 239000000460 chlorine Substances 0.000 claims description 6
- 229910052801 chlorine Inorganic materials 0.000 claims description 6
- 238000012545 processing Methods 0.000 claims description 6
- 238000009434 installation Methods 0.000 claims description 5
- 239000004576 sand Substances 0.000 claims description 3
- 239000012141 concentrate Substances 0.000 claims description 2
- 238000010992 reflux Methods 0.000 claims description 2
- 239000002574 poison Substances 0.000 claims 1
- 231100000614 poison Toxicity 0.000 claims 1
- 239000010802 sludge Substances 0.000 abstract description 4
- 230000009467 reduction Effects 0.000 abstract description 2
- 238000012423 maintenance Methods 0.000 description 4
- 230000001376 precipitating effect Effects 0.000 description 4
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 3
- 230000008859 change Effects 0.000 description 3
- 238000005265 energy consumption Methods 0.000 description 3
- 239000001301 oxygen Substances 0.000 description 3
- 229910052760 oxygen Inorganic materials 0.000 description 3
- 230000008569 process Effects 0.000 description 3
- 230000005611 electricity Effects 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000001737 promoting effect Effects 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 238000004065 wastewater treatment Methods 0.000 description 2
- 208000031872 Body Remains Diseases 0.000 description 1
- 206010033799 Paralysis Diseases 0.000 description 1
- 230000009471 action Effects 0.000 description 1
- 238000011001 backwashing Methods 0.000 description 1
- 238000005842 biochemical reaction Methods 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000011152 fibreglass Substances 0.000 description 1
- 230000002070 germicidal effect Effects 0.000 description 1
- 230000010354 integration Effects 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 239000004033 plastic Substances 0.000 description 1
- 229920003023 plastic Polymers 0.000 description 1
- 238000007747 plating Methods 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 239000002344 surface layer Substances 0.000 description 1
- 238000012546 transfer Methods 0.000 description 1
- 239000002351 wastewater 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
- 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
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
- C02F1/32—Treatment of water, waste water, or sewage by irradiation with ultraviolet light
-
- 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
- C02F1/50—Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment
-
- 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
-
- 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
- C02F1/58—Treatment of water, waste water, or sewage by removing specified dissolved compounds
-
- 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
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/76—Treatment of water, waste water, or sewage by oxidation with halogens or compounds of halogens
-
- 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
- C02F2101/105—Phosphorus compounds
-
- 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
-
- 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
- C02F2301/00—General aspects of water treatment
- C02F2301/04—Flow arrangements
- C02F2301/046—Recirculation with an external loop
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/04—Disinfection
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/14—Maintenance of water treatment installations
-
- 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
- C02F3/302—Nitrification and denitrification treatment
- C02F3/305—Nitrification and denitrification treatment characterised by the denitrification
Landscapes
- Life Sciences & Earth Sciences (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 kind of sewage simultaneous phosphorus and nitrogen removal integrated apparatus and methods, belong to sewage treatment field, including bracket and rack-mount Anaerobic Contact oxidation pond, trickling biofilter, sedimentation basin, intermediate promotion pond, filtering dephosphorization tank and sterilization pool;Trickling biofilter is located at the top of Anaerobic Contact oxidation pond, sedimentation basin, trickling biofilter includes the water distribution system set gradually from top to bottom, filler module and outlet system, Anaerobic Contact oxidation pond is connect by inlet pipeline with water distribution system, elevator pump, the connection Anaerobic Contact oxidation pond and sedimentation basin of outlet system gravity flow are installed on inlet pipeline;Sedimentation basin, intermediate promotion pond, filtering dephosphorization tank, sterilization pool are sequentially connected according to drainage flow direction.It is the configuration of the present invention is simple, easy to use, denitrogenation and dephosphorization can either be carried out with cloth, also have the advantages that reduction sludge yield.
Description
Technical field
The present invention relates to sewage treatment field, in particular to a kind of sewage simultaneous phosphorus and nitrogen removal integrated apparatus and method.
Background technique
Currently, the sanitary sewage integrated equipment for wastewater treatment of small tonnage energy consumption when handling sanitary sewage is higher, and power is set
Standby maintenance is more frequent.For large-scale wastewater treatment plant, during small-sized sanitary sewage disposal station operation management, because adding
The investment of labour cost caused by medicine and maintenance of equipment are frequent is too high, eventually leads to most small-sized sanitary sewage disposal stations or unmanned pipe
It manages or paralyses and be unable to operate normally.
Simultaneously as general integrated domestic sewage treatment device lacks spoil disposal function, sewage treatment integration is caused to set
Lack dephosphorization ability after standby longtime running.
Notification number is that the Chinese invention patent of CN102190374A discloses a kind of trickling biofilter, and the trickling biofilter is by intaking
Pipeline, water distribution system, filler module and outlet system are constituted, and inlet pipeline and water distribution system are located at top, and water inlet is uniformly divided
Cloth is into filler module, and along vertically to setting, top filler module is supported filler module with lower part filler module, without independent
Support frame is set, and outlet system is located at lowest part, collection, reflux and emission treatment water.
Wherein, filler module is that rigid plastics, glass reinforced plastic or light-weight metal plate are fabricated to network, the filler module
Along vertically corrugated to being designed to, extension flow path.Filler module is supported by lower part filler module, without being separately provided
Support frame facilitates installation;Filler module can be composed of corrugated plating and connecting rod or single injection-molded, for various concentration
Waste water, selects different length connecting rod or ripple plate spacing, i.e., changeable filler module gap prevents big partial size substance in sewage
It is sized and is trapped in packed bed, sewage is degraded in drip process by the biochemical action of the biomembrane of filler surface layer attachment, is taken off
The microbial film fallen can pass through network packed bed, fundamentally packed bed be prevented to block, and avoid backwash,
Simplify sewage treatment and runs operating process.
Above-mentioned trickling biofilter structure is simple, easy for installation, naturally oxygen supply, low energy consumption, and sludge yield is few, is applicable in very much
It is used in the domestic sewage treatment device of small tonnage.
Summary of the invention
Structure is complicated for domestic sewage treatment device of the existing technology, be not easy to maintenance and sludge quantity is big asks
Topic, the purpose of the present invention is to provide a kind of sewage simultaneous phosphorus and nitrogen removal integrated apparatus.
To achieve the above object, the technical solution of the present invention is as follows:
A kind of sewage simultaneous phosphorus and nitrogen removal integrated apparatus, the Anaerobic Contact oxygen including bracket and installation on the bracket
Change pond, trickling biofilter, sedimentation basin, intermediate promotion pond, filtering dephosphorization tank and sterilization pool;The trickling biofilter is located at the anaerobism and connects
The top of oxidation pond, the sedimentation basin is touched, the trickling biofilter includes the water distribution system set gradually from top to bottom, filler module
And outlet system, the Anaerobic Contact oxidation pond are connect with the water distribution system by inlet pipeline, are pacified on the inlet pipeline
Equipped with elevator pump, the connection Anaerobic Contact oxidation pond and the sedimentation basin of the outlet system gravity flow;The sedimentation basin, institute
State it is intermediate promote pond, the filtering dephosphorization tank, the sterilization pool are sequentially connected according to drainage flow direction.
Preferably, the filtering dephosphorization tank includes tank body, and the tank body is equipped with inlet and outlet, is set in the tank body
It is equipped with iron content filtering dephosphorization filler, the iron content filtering dephosphorization filler is iron ore or iron sand.
Further, backwash interface is additionally provided on the tank body.
Preferably, chlorine tablets and/or ultraviolet disinfection lamp are provided in the sterilization pool.
Preferably, the lower part of the sedimentation basin is provided with sewage draining exit, and the sewage outfalls setting has blowdown valve.
Further, control cabinet, the control cabinet and the elevator pump, blowdown valve electricity are also equipped on the bracket
Connection.
The invention also discloses a kind of sewage simultaneous phosphorus and nitrogen removal methods, comprising the following steps:
Sewage lifting to Anaerobic Contact oxidation pond is carried out anaerobic hydrolysis-acidification reaction by step 1;
Step 2 carries out the water promotion for passing through anaerobic hydrolysis-acidification reaction in Anaerobic Contact oxidation pond to trickling biofilter
Oxygen reaction;
The water a part for passing through aerobic reaction in trickling biofilter is flowed back into the anti-nitre of Anaerobic Contact oxidation pond progress by step 3
Change denitrogenation processing, another part flows into sedimentation basin and settled;
Step 4, by the water promotion by sedimentation basin sedimentation, to filtering, dephosphorization tank is filtered and dephosphorization is handled;
Step 5, by filtering and dephosphorization, treated that water enters obtains clean water after sterilization pool carries out sterilizing.
Preferably, in step 3, it is to flow into the water of sedimentation basin that trickling biofilter, which flows back into the water of Anaerobic Contact oxidation pond,
Twice.
Preferably, in step 4, further include intermediate promotion pond, first flow into the centre by the water that settling tank settles and mention
Chi Jizhong is risen, then is thus lifted to the filtering dephosphorization tank.
Preferably, in steps of 5, the sterilizing includes one of chlorine tablets sterilization, ultraviolet sterilization or several
Combination.
By adopting the above technical scheme, due to the use of trickling biofilter, on the one hand make the reduction of sludge yield, another party side
What face also made aerobic reaction becomes simpler for oxide structure, facilitates operation, facilitates and carries out nitrification and denitrification reaction;Due to
The setting for filtering dephosphorization tank, so that dephosphorization ability is improved.The present invention solves the high energy of small-sized domestic sewage of villages and small towns processing
The problem of consumption, complex management, fluctuation of service, equipment operation energy consumption is lower, and operational management is simple, and personnel's Meteorological is low, if
Standby maintenance cost is low, and equipment land occupation is few, every pollution factor in effectively stable processing sewage.
Detailed description of the invention
Fig. 1 is the top view of sewage simultaneous phosphorus and nitrogen removal integrated apparatus of the present invention;
Fig. 2 is the main view of sewage simultaneous phosphorus and nitrogen removal integrated apparatus of the present invention;
Fig. 3 is sewage simultaneous phosphorus and nitrogen removal method flow diagram of the present invention.
In figure: 1- bracket, 2- Anaerobic Contact oxidation pond, 3- trickling biofilter, 4- sedimentation basin, the centre 5- promote pond, 6- filtering
Dephosphorization tank, 7- sterilization pool, 8- control cabinet, 9- elevator pump, 10- ultraviolet disinfection lamp, 11- water-distribution nozzle.
Specific embodiment
Specific embodiments of the present invention will be further explained with reference to the accompanying drawing.It should be noted that for
The explanation of these embodiments is used to help understand the present invention, but and does not constitute a limitation of the invention.In addition, disclosed below
The each embodiment of the present invention involved in technical characteristic can be combined with each other as long as they do not conflict with each other.
As shown in Figures 1 and 2, a kind of sewage simultaneous phosphorus and nitrogen removal integrated apparatus, including bracket 1 and it is mounted on bracket 1
On Anaerobic Contact oxidation pond 2, trickling biofilter 3, sedimentation basin 4, intermediate promote pond 5, filtering dephosphorization tank 6, sterilization pool 7 and control cabinet
8.Bracket 1 is for carrying above-mentioned Anaerobic Contact oxidation pond 2, trickling biofilter 3, sedimentation basin 4, intermediate promotion pond 5, filtering dephosphorization tank
6, sterilization pool 7 and control cabinet 8, are usually frame structure.
Trickling biofilter 3 includes water distribution system, filler module and the outlet system set gradually from top to bottom, and water distribution system is used
Be evenly distributed in filler module in that will intake, filler module be used to form biomembrane to make sewage occur biochemical reaction and
Degradation, outlet system are used to be flowed back in the water handled by trickling biofilter 3, discharge.Water distribution system is connected by inlet pipeline
It connects in the water outlet of Anaerobic Contact oxidation pond 2, water distribution system generally includes multiple water distributors connecting with inlet pipeline and sets
Set multiple water distributing pores or water-distribution nozzle on water distributor;The specific structure present invention of trickling biofilter 3 repeats no more;
In the installation site of bracket 1, trickling biofilter 3 is located at the top of Anaerobic Contact oxidation pond 2, sedimentation basin 4;Therefore originally
In embodiment, need that elevator pump 9 is arranged on inlet pipeline;And the outlet system of trickling biofilter 3 is connected by way of gravity flow
Anaerobic Contact oxidation pond 2 and sedimentation basin 4, so that the water a part handled by trickling biofilter 3 is flowed back into Anaerobic Contact oxidation
Pond 2 carries out denitrification denitrogenation processing, and another part is then drained into sedimentation basin 4 and carries out settlement treatment.
Above-mentioned sedimentation basin 4, it is intermediate promote pond 5, filtering dephosphorization tank 6, sterilization pool 7 successively connect according to drainage flow direction
It connects.Sewage is in sedimentation basin 4, the intermediate flowing promoted between pond 5, filtering dephosphorization tank 6 and sterilization pool 7 using dynamic mode
(by pump) or no-power way (flow by gravity);
But in the present embodiment, the top of sedimentation basin 4 is connected to the intermediate top for promoting pond 5, and sewage is in sedimentation basin 4 and centre
It is promoted between pond 5 through the side of overflow (when running up to a certain amount of in sedimentation basin 4, sewage is flowed out by the mode of flow by gravity)
Formula transfer, being arranged such can be such that the clear water part in sedimentation basin 4 flows into intermediate promotion pond 5 as far as possible, and make the part of precipitating
It is stayed in sedimentation basin 4 as far as possible;Specifically, the lower part of sedimentation basin 4 is additionally provided with sewage draining exit, sewage outfalls setting has blowdown valve.This reality
It applies in example, since sedimentation basin 4 is intake in real time, the internal water accumulated is simultaneously unstable, and the intermediate effect for promoting pond 5 is then
It is to keep in by the sewage of precipitating, so as to guarantee to provide relatively stable input water source for filtering dephosphorization tank 6.
Filtering dephosphorization tank 6 includes tank body, and tank body is equipped with inlet and outlet, and water inlet is connected with water inlet line, should be into
The other end of waterpipe is extend into intermediate promotion pond 5, while an elevator pump 9 is also provided on water inlet line, passes through pump
Power promotes the intermediate water promoted in pond 5 to filtering dephosphorization tank 6;Above-mentioned water outlet then passes through pipeline and water outlet is passed through gravity flow
Mode drain into sterilization pool 7;Specifically, being provided with iron content filtering dephosphorization filler in above-mentioned tank body, iron content filters dephosphorization
Filler is iron ore or iron sand, and iron content filters dephosphorization filler while having the function of that filtering stops, additionally it is possible to be contained by it
Phosphorus containg substances in some ironys and sewage chemically react, and are deposited in tank body to form precipitating;
In the present embodiment, backwash interface is additionally provided on above-mentioned tank body, when the reaction for precipitating retention in tank body remains
After object is more, it is reversely gone out by backwashing water.
In the present embodiment, chlorine tablets and/or ultraviolet disinfection lamp are provided in sterilization pool 7 for sterilizing, the water after disinfection is then
Sewage disposal process is completed, can be used for production and living.
In order to improve automatization level, solenoid valve, and above-mentioned blowdown valve are respectively provided on pipeline and inlet pipeline
Preferably solenoid valve;The electricity consumptions such as above-mentioned control cabinet and elevator pump 9, solenoid valve, ultraviolet disinfection lamp or element are electrically connected, with
Control its working condition.
As shown in figure 3, the invention also discloses a kind of sewage simultaneous phosphorus and nitrogen removal methods, comprising the following steps:
Sewage lifting to Anaerobic Contact oxidation pond 2 is carried out anaerobic hydrolysis-acidification reaction by step 1;
Step 2 carries out the water promotion for passing through anaerobic hydrolysis-acidification reaction in Anaerobic Contact oxidation pond 2 to trickling biofilter 3
Aerobic reaction;
The water a part for passing through aerobic reaction in trickling biofilter 3 is flowed back into Anaerobic Contact oxidation pond 2 and carried out instead by step 3
Denitrogenation processing is nitrified, another part flows into sedimentation basin 4 and settled;
Step 4, by the water promotion settled by sedimentation basin 4, to filtering, dephosphorization tank 6 is filtered and dephosphorization is handled;
Step 5, by filtering and dephosphorization, treated that water enters obtains clean water after sterilization pool 7 carries out sterilizing.
In step 3, trickling biofilter 3 flows back into two that the water of Anaerobic Contact oxidation pond 2 is the water of inflow sedimentation basin 4
Times.
In step 4, further include intermediate promotion pond 5, first flow into the intermediate pond 5 that promoted by the water that settling tank 4 settles and concentrate,
It is thus lifted to filtering dephosphorization tank 6 again.
In steps of 5, sterilizing includes chlorine tablets sterilization, one of ultraviolet sterilization or several combinations, wherein
Ultraviolet sterilization is realized by way of ultraviolet germicidal lamp 10 is arranged in sterilization pool 7.
In conjunction with attached drawing, the embodiments of the present invention are described in detail above, but the present invention is not limited to described implementations
Mode.For a person skilled in the art, in the case where not departing from the principle of the invention and spirit, to these embodiments
A variety of change, modification, replacement and modification are carried out, are still fallen in protection scope of the present invention.
Claims (10)
1. a kind of sewage simultaneous phosphorus and nitrogen removal integrated apparatus, it is characterised in that: on the bracket including bracket and installation
Anaerobic Contact oxidation pond, trickling biofilter, sedimentation basin, intermediate promotion pond, filtering dephosphorization tank and sterilization pool;The trickling biofilter is located at
The top of the Anaerobic Contact oxidation pond, the sedimentation basin, the trickling biofilter include the cloth water system set gradually from top to bottom
System, filler module and outlet system, the Anaerobic Contact oxidation pond are connect by inlet pipeline with the water distribution system, it is described into
Elevator pump, the connection Anaerobic Contact oxidation pond and the sedimentation basin of the outlet system gravity flow are installed in water lines;Institute
State sedimentation basin, the centre promotes pond, the filtering dephosphorization tank, the sterilization pool are sequentially connected according to drainage flow direction.
2. sewage simultaneous phosphorus and nitrogen removal integrated apparatus according to claim 1, it is characterised in that: the filtering dephosphorization tank
Including tank body, the tank body is equipped with inlet and outlet, and iron content filtering dephosphorization filler, the iron content are provided in the tank body
Filtering dephosphorization filler is iron ore or iron sand.
3. sewage simultaneous phosphorus and nitrogen removal integrated apparatus according to claim 2, it is characterised in that: also set on the tank body
It is equipped with backwash interface.
4. sewage simultaneous phosphorus and nitrogen removal integrated apparatus according to claim 1, it is characterised in that: set in the sterilization pool
It is equipped with chlorine tablets and/or ultraviolet disinfection lamp.
5. sewage simultaneous phosphorus and nitrogen removal integrated apparatus according to claim 1, it is characterised in that: under the sedimentation basin
Portion is provided with sewage draining exit, and the sewage outfalls setting has blowdown valve.
6. sewage simultaneous phosphorus and nitrogen removal integrated apparatus according to claim 5, it is characterised in that: also pacify on the bracket
Equipped with control cabinet, the control cabinet is electrically connected with the elevator pump, the blowdown valve.
7. a kind of sewage simultaneous phosphorus and nitrogen removal method, it is characterised in that: the following steps are included:
Sewage lifting to Anaerobic Contact oxidation pond is carried out anaerobic hydrolysis-acidification reaction by step 1;
Step 2, the water promotion that will be reacted in Anaerobic Contact oxidation pond by anaerobic hydrolysis-acidification carry out aerobic anti-to trickling biofilter
It answers;
Step 3, by trickling biofilter pass through aerobic reaction water a part flow back into Anaerobic Contact oxidation pond carry out denitrification take off
Nitrogen processing, another part flow into sedimentation basin and are settled;
Step 4, by the water promotion by sedimentation basin sedimentation, to filtering, dephosphorization tank is filtered and dephosphorization is handled;
Step 5, by filtering and dephosphorization, treated that water enters obtains clean water after sterilization pool carries out sterilizing.
8. sewage simultaneous phosphorus and nitrogen removal method according to claim 7, it is characterised in that: in step 3, trickling biofilter reflux
Water to Anaerobic Contact oxidation pond is twice of the water of inflow sedimentation basin.
9. sewage simultaneous phosphorus and nitrogen removal method according to claim 7, it is characterised in that: further include that centre mentions in step 4
Pond is risen, the intermediate pond that promoted is first flowed by the water that settling tank settles and concentrates, then be thus lifted to the filtering dephosphorization tank.
10. sewage simultaneous phosphorus and nitrogen removal method according to claim 7, it is characterised in that: in steps of 5, the sterilization disappears
Poison includes one of chlorine tablets sterilization, ultraviolet sterilization or several combinations.
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Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20020009738A (en) * | 2000-07-26 | 2002-02-02 | 오시덕 | Compact System and Device of the Advanced Wastewater Treatment Process |
CN102190374A (en) * | 2011-04-07 | 2011-09-21 | 上海浩为环境工程有限公司 | Trickling biofilter |
CN202011812U (en) * | 2011-03-08 | 2011-10-19 | 四川四通欧美环境工程有限公司 | Integrated equipment for treating high-concentration organic wastewater |
CN204211601U (en) * | 2014-09-30 | 2015-03-18 | 四川中测环境技术有限公司 | Sewerage integrated processing system |
CN104773826A (en) * | 2015-04-10 | 2015-07-15 | 绵阳科勤环保科技有限公司 | Hydrolytic acidification two-stage contact oxidization integrated domestic sewage treatment equipment |
CN106277558A (en) * | 2015-06-25 | 2017-01-04 | 安徽华骐环保科技股份有限公司 | A kind of integrate process for removing nitrogen and phosphor from sewage and the device that physical biochemistry filters |
-
2019
- 2019-08-29 CN CN201910809590.5A patent/CN110498568A/en active Pending
Patent Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20020009738A (en) * | 2000-07-26 | 2002-02-02 | 오시덕 | Compact System and Device of the Advanced Wastewater Treatment Process |
CN202011812U (en) * | 2011-03-08 | 2011-10-19 | 四川四通欧美环境工程有限公司 | Integrated equipment for treating high-concentration organic wastewater |
CN102190374A (en) * | 2011-04-07 | 2011-09-21 | 上海浩为环境工程有限公司 | Trickling biofilter |
CN204211601U (en) * | 2014-09-30 | 2015-03-18 | 四川中测环境技术有限公司 | Sewerage integrated processing system |
CN104773826A (en) * | 2015-04-10 | 2015-07-15 | 绵阳科勤环保科技有限公司 | Hydrolytic acidification two-stage contact oxidization integrated domestic sewage treatment equipment |
CN106277558A (en) * | 2015-06-25 | 2017-01-04 | 安徽华骐环保科技股份有限公司 | A kind of integrate process for removing nitrogen and phosphor from sewage and the device that physical biochemistry filters |
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