CN206359323U - A kind of simultaneous denitrification removes algae membrane bioreactor - Google Patents

A kind of simultaneous denitrification removes algae membrane bioreactor Download PDF

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Publication number
CN206359323U
CN206359323U CN201621357449.4U CN201621357449U CN206359323U CN 206359323 U CN206359323 U CN 206359323U CN 201621357449 U CN201621357449 U CN 201621357449U CN 206359323 U CN206359323 U CN 206359323U
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CN
China
Prior art keywords
zone
aerobic
reactor body
membrane bioreactor
simultaneous denitrification
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Expired - Fee Related
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CN201621357449.4U
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Chinese (zh)
Inventor
孔赟
邹培
邹桐
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Yixing City Product Quality Supervision And Testing Institute
Wuxi City Bywater Environmental Technology Co Ltd
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Yixing City Product Quality Supervision And Testing Institute
Wuxi City Bywater Environmental Technology Co Ltd
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Priority to CN201621357449.4U priority Critical patent/CN206359323U/en
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Publication of CN206359323U publication Critical patent/CN206359323U/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

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  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

A kind of simultaneous denitrification removes algae membrane bioreactor, including reactor body, reactor body, which is separated into anaerobic zone arranged side by side, aerobic area and the region of aerobic zone three, aerobic zone, is provided with membrane module, and aerator is provided with below membrane module, aerobic zone top is provided with discharge outlet, bottom is provided with settling zone, and settling zone bottom is provided with mud discharging mouth, anaerobic zone and is provided with agitating device, it is provided with the nearly bottom housing in anaerobic zone in water inlet, aerobic area and is provided with hanging filler.Have the advantages that small floor space, small investment, processing cost are low.

Description

A kind of simultaneous denitrification removes algae membrane bioreactor
Technical field
The utility model is related to a kind of reactor of the high ammonia nitrogen micro pollution drinking water source processing of high algae, more particularly to a kind of Simultaneous denitrification removes the membrane bioreactor of algae.
Background technology
With the fast development of Chinese society economy, town and country drinking water source area is generally dirty in various degree by nitrogen, phosphorus etc. Dye, lake storehouse water body eutrophication degree constantly aggravates.According to statistics, in state's control emphasis monitoring lake (reservoir) of 62, the whole nation, I~III Lake (reservoir) ratio of class, IV~V class and bad V class water quality is respectively 61.3%, 30.6% and 8.1%;It there are about 60% lake In eutrophic state, the large-scale fresh water lake eutrophication such as Taihu Lake, Chaohu, Dian Chi, Wuhan East Lake is extremely serious, algae water China happens occasionally.
The Algae toxins of algae and its secretion cause drinking water source water quality deterioration, add waterworks intractability and Processing cost;In addition, the algae organic matter produced in algae metabolic processes holdup time length, difficult biology in water body environment Degraded, causes to generate DBPs in conventional water treatment process chlorination link, wherein nitrogenous disinfection byproducts are extremely bright Aobvious, high degree threatens drinking water quality safety.Therefore, the removal of algae and ammonia nitrogen seems outstanding in raw water of micropolluted water To be important.
Membrane biological reactor process (MBR techniques) is a kind of new waste water that membrane separation technique is organically combined with biotechnology Biologic treating technique.MBR has efficient crown_interception because of its membrane module, and microorganism can be made to be trapped in bioreactor so as to real Existing reactor hydraulic detention time (HRT's) and sludge age (SRT) is kept completely separate, and realizes to deep purification of waste water;Meanwhile, ammonia Oxidation bacteria, nitrifier and polyP bacteria etc. can fully be bred in reactor, realize synchronous denitrification dephosphorizing.In recent years, MBR is in life It is widely applied in sewage, industrial wastewater and micro pollution drinking water source processing.By denitrogenation and except algae unites two into one, exploitation Simultaneous denitrification removes algae membrane bioreactor, can not only simplify raw water of micropolluted water handling process, reduce cost of investment and Operating cost is reduced, can also realize that system high efficiency simultaneous denitrification removes algae stable operation.
Utility model content
The utility model in view of the shortcomings of the prior art there is provided a kind of compact conformation, small floor space, high treating effect, The low simultaneous denitrification of operating cost removes algae membrane bioreactor.
To realize the utility model purpose, there is provided following technical scheme:A kind of simultaneous denitrification removes algae membrane bioreactor, Including reactor body, it is characterised in that reactor body is separated into anaerobic zone arranged side by side, aerobic area and the region of aerobic zone three, It is provided with aerobic zone below membrane module, membrane module and is provided with aerator, aerobic zone top is provided with discharge outlet, and bottom is provided with Settling zone and sludge refluxing apparatus, settling zone bottom, which is provided with mud discharging mouth, anaerobic zone, is provided with agitating device, the nearly bottom in anaerobic zone It is provided with end housing in water inlet and sludge reflux mouthful, aerobic area and is provided with hanging filler.
Preferably, reactor body is separated by two pieces of dividing plates, a dividing plate top and reactor body top interval, bottom End is affixed with reactor body bottom, and No. two dividing plate tops and reactor body top are affixed, bottom and reactor body bottom Interval, makes to be formed from bottom to top, then in the top-down flow path in aerobic area in anaerobic zone into water.
Preferably, settling zone is separately provided with back the sludge reflux mouthful of the mud pipeline connection nearly bottom in anaerobic zone, mud pipeline is returned On be provided with sludge refluxing apparatus.
Preferably, membrane module is tubular membrane, curtain type membrane or plate film assembly.
Preferably, the volume ratio of anaerobic zone, aerobic area and aerobic zone three is 1:1:1.
Preferably, settling zone bottom is using rectangular pyramid, its base angle is 30 ~ 60 °.
The utility model beneficial effect:There is advantages below compared with prior art:1)Reactor is divided into from left to right to be detested Oxygen area, aerobic area and the unit of aerobic zone three, compact conformation, floor space are small;2)Aerobic area hanging filler can apposition growth it is big Biomembrane is measured, is conducive to strengthened denitrification to remove algae effect;3)Sewage treatment process is melted into a whole by reactor with membrane separation technique;4) Aerobic zone membrane module is by algae and rejection to organics to settling zone, good separating effect.
Brief description of the drawings
Fig. 1 is structural representation of the present utility model.
Embodiment
Embodiment 1:A kind of simultaneous denitrification removes algae membrane bioreactor, including reactor body 1, and reactor body 1 separates Into anaerobic zone 2 arranged side by side, aerobic area 3 and the region of aerobic zone 4 three, it is provided with aerobic zone 4 under membrane module 4.1, membrane module 4.1 Side is provided with aerator 4.2, and the top of aerobic zone 4 is provided with discharge outlet 4.3, and bottom is provided with settling zone 4.4, the bottom of settling zone 4.4 Portion, which is provided with mud discharging mouth 4.4.1, anaerobic zone 2, is provided with agitating device 2.1, is provided with the nearly bottom housing in anaerobic zone 2 into water Hanging filler 3.1 is provided with mouth 2.2, aerobic area 3, described hanging filler 3.1 can be variously-shaped organic filler.Reactor Body 1 is separated by two pieces of dividing plates, a top of dividing plate 1.1 and the top interval of reactor body 1, bottom and the bottom of reactor body 1 End is affixed, and No. two tops of dividing plate 1.2 and the top of reactor body 1 are affixed, bottom and the bottom interval of reactor body 1, makes into water Formed from bottom to top, then top-down flow path.Settling zone 4.4 is separately provided with go back to the connection of the mud pipeline 5 nearly bottom in anaerobic zone 2 Sludge reflux mouthfuls 7, return on mud pipeline 5 and be provided with sludge refluxing apparatus 6.Membrane module 4.1 is tubular membrane, curtain type membrane or Flat Membrane Component.The volume ratio of anaerobic zone 2, aerobic area 3 and the three of aerobic zone 4 is 1:1:1.The bottom of settling zone 4.4 uses rectangular pyramid, Its base angle is 30 ~ 60 °.
The utility model reactor can make of PVC board and stainless steel, and its course of work is as follows:Containing high algae high NH4 source water Entered by water inlet 2.2 in anaerobic zone 2, agitating device 2.1 is stirred in anaerobic zone 2, and raw water is after Anaerobic Treatment by detesting The top of oxygen area 2 enters aerobic area 3, from top to bottom with entering aerobic by the bottom of aerobic area 3 after the abundant haptoreaction of hanging filler 3.1 Aerator 4.2 removes ammonia nitrogen by being aerated in area 4, aerobic zone 4, and algae and organic matter etc. are retained in precipitation by membrane module 4.1 Area 4.4, raw water is discharged after processing from discharge outlet 4.3, and a sediment part for generation is returned by sludge refluxing apparatus 6 and sludge Head piece 7 enters anaerobic zone 2, and another part is discharged through mud discharging mouth 4.4.1.

Claims (6)

1. a kind of simultaneous denitrification removes algae membrane bioreactor, including reactor body, it is characterised in that reactor body is separated into It is provided with anaerobic zone, aerobic area and the region of aerobic zone three arranged side by side, aerobic zone below membrane module, membrane module and is provided with aeration Device, aerobic zone top is provided with discharge outlet, and bottom is provided with settling zone, and settling zone bottom is provided with mud discharging mouth and sludge reflux dress Put, be provided with agitating device, the nearly bottom housing in anaerobic zone and be provided with water inlet and sludge reflux mouthful, aerobic area in anaerobic zone It is provided with hanging filler.
2. a kind of simultaneous denitrification according to claim 1 remove algae membrane bioreactor, it is characterised in that reactor body by Two pieces of dividing plates separate, and a dividing plate top and reactor body top interval, bottom and reactor body bottom are affixed, No. two every Plate top and reactor body top are affixed, bottom and reactor body bottom interval, make to be formed in anaerobic zone from lower into water On, then in the top-down flow path in aerobic area.
3. a kind of simultaneous denitrification according to claim 1 removes algae membrane bioreactor, it is characterised in that settling zone is separately set There is back mud pipeline to connect the sludge reflux mouthful of the nearly bottom in anaerobic zone, return on mud pipeline and be provided with sludge refluxing apparatus.
4. a kind of simultaneous denitrification according to claim 1 removes algae membrane bioreactor, it is characterised in that membrane module is tubular type Film, curtain type membrane or plate film assembly.
5. a kind of simultaneous denitrification according to claim 1 removes algae membrane bioreactor, it is characterised in that anaerobic zone, aerobic area Volume ratio with aerobic zone three is 1:1:1.
6. a kind of simultaneous denitrification according to claim 1 removes algae membrane bioreactor, it is characterised in that settling zone bottom is equal Using rectangular pyramid, its base angle is 30 ~ 60 °.
CN201621357449.4U 2016-12-12 2016-12-12 A kind of simultaneous denitrification removes algae membrane bioreactor Expired - Fee Related CN206359323U (en)

Priority Applications (1)

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CN201621357449.4U CN206359323U (en) 2016-12-12 2016-12-12 A kind of simultaneous denitrification removes algae membrane bioreactor

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CN201621357449.4U CN206359323U (en) 2016-12-12 2016-12-12 A kind of simultaneous denitrification removes algae membrane bioreactor

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107055774A (en) * 2016-12-12 2017-08-18 无锡市拜沃特环保科技有限公司 A kind of simultaneous denitrification removes algae membrane bioreactor

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107055774A (en) * 2016-12-12 2017-08-18 无锡市拜沃特环保科技有限公司 A kind of simultaneous denitrification removes algae membrane bioreactor

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CF01 Termination of patent right due to non-payment of annual fee
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Granted publication date: 20170728

Termination date: 20201212