CN202594841U - Solar nanometer packing moving bed biofilm reactor - Google Patents
Solar nanometer packing moving bed biofilm reactor Download PDFInfo
- Publication number
- CN202594841U CN202594841U CN2012201798439U CN201220179843U CN202594841U CN 202594841 U CN202594841 U CN 202594841U CN 2012201798439 U CN2012201798439 U CN 2012201798439U CN 201220179843 U CN201220179843 U CN 201220179843U CN 202594841 U CN202594841 U CN 202594841U
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- Prior art keywords
- solar
- mbbr
- moving bed
- aerator
- tank body
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A20/00—Water conservation; Efficient water supply; Efficient water use
- Y02A20/20—Controlling water pollution; Waste water treatment
- Y02A20/208—Off-grid powered water treatment
- Y02A20/212—Solar-powered wastewater sewage treatment, e.g. spray evaporation
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/30—Wastewater or sewage treatment systems using renewable energies
- Y02W10/37—Wastewater or sewage treatment systems using renewable energies using solar energy
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- Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)
Abstract
The utility model discloses a solar nanometer packing moving bed biofilm reactor which structurally comprises a solar power generation system located above ground and a moving bed biofilm reactor located under the ground, wherein the solar power generation system comprises a solar battery panel and a storage battery, the moving bed biofilm reactor comprises a main disposal area and a sediment area communicated with the main disposal area through a diversion groove, and a water inlet pipe is arranged at the upper end of the main disposal area and filled with nanometer suspension packing; a water outlet pipe and a tilted plate sedimentator are arranged at the upper end of the sediment area, the diversion groove communicated with the main disposal area is arranged at the lower end of the sediment area, an aeration machine is arranged on the top of a tank body, and the aeration machine is connected with an aeration device arranged at the lower end of the main disposal area through an aeration pipeline and is connected with the storage battery of the solar power generation system through an automatic control circuit. The solar nanometer packing moving bed biofilm reactor is simple in structure, small in occupied space, convenient to install and transport, simple in operation and management, saving in energy, and suitable for treatment of scattered sanitary sewage.
Description
Technical field
The utility model belongs to the sewage purification technology field, relates to a kind of sun power Nano filling MBBR.
Background technology
The many geographic tourist attractions of China, road service area, middle samll cities and towns, particularly Rural areas etc., owing to do not lay sewage network, a large amount of sewages just directly are discharged into surface water body without collection and treatment, cause water pollution.The decentralized type sewage treatment process is the main method of these regional sanitary sewage disposals, and buried integrated domestic sewage treatment device is one of the most frequently used equipment of decentralized type sewage treatment process, and the processing of dispersant type domestic wastewater is had vital role.
At present, the technology of integrated domestic sewage treatment device employing mainly contains microbial film contact oxidation method and activated sludge process.Adopt the integrated sewage treating apparatus of these two kinds of technologies to have shortcomings such as device structure is complicated, floor space is big, operational and administrative expenses is high, energy consumption is high, management maintenance is complicated, surplus sludge volume is more.MBBR is with biomembrance process and activated sludge process process combined, have anti impulsion load, mud age long, surplus sludge volume is few, processing efficiency is high and the energy consumption advantage that has biomembrance process and activated sludge process concurrently such as low.
The integrated sewage treating apparatus that has completed for use at present; Because working cost is high, treatment capacity is 10～100 tons/day a integration apparatus, and working cost is about 0.2～1.0 yuan of/ton water; Owing to lack the operational management fund, many equipment use just discarded in the near future simultaneously.The working cost of integration apparatus mainly is the power source consumption of equipment, and high working cost greatly influences its promoting the use of in decentralized type sewage is handled.For reducing the working cost that decentralized type sewage is handled, the substitute energy of seeking convenient cleaning is significant to applying of integrated sewage treating apparatus.Sun power is as a kind of cleaning and the extensive energy that distributes; In the energy resource supply of decentralized type sewage treatment facility, has vital role; At present existing comparatively sophisticated solar energy generation technology with the power resources of sun power as the MBBR integrated sewage treating apparatus, can effectively solve the energy source and power problem that decentralized type sewage is handled; Reduce the WWT working cost, greatly promote the widespread use of integrated sewage treating apparatus in decentralized type sewage is handled.
The filler of MBBR plays an important role to WWT, and the filler of bigger serface can provide more microorganism growth and adhere to, and improves the processing efficiency of reactor drum.Therefore, be necessary through improving the processing efficiency that floating stuffing improves reactor drum.
Summary of the invention
The purpose of the utility model is to overcome the deficiency of above prior art, and a kind of sun power Nano filling MBBR is provided.
The technical scheme of the utility model is:
It is power that the utility model adopts sun power, handles sewage with MBBR, and solving and handling the water yield is 5～50 tons/day dispersant type domestic wastewater processing and the power supply problem in the treating processes.Supply with the electricity consumption of entire sewage treatment system through solar electrical energy generation, solve the energy consumption problem in the sewage treatment process, reduce the running cost of sewage disposal device, utilize renewable, cleaning novel energy simultaneously, practiced thrift the energy and reduced Carbon emission.Through adopting the nanoparticle suspension filler,, improve sewage treating efficiency for the specific surface area that provides big is adhered in biomembranous growth.This sewage disposal device adopts the aerobic moving bed biomembrane process, in conjunction with the advantage of biomembrance process and activated sludge process, have device structure simply, easy transportation and installation, characteristics such as operational management is simple, processing efficiency is high, save energy.
The utility model is achieved in that
A kind of sun power Nano filling MBBR; Comprise solar power system and MBBR, it is characterized in that: described solar power system is provided with solar panel and store battery, and MBBR is provided with tank body; The tank body inner route clapboard is separated out main treatment zone and settling region; Solar panel and store battery are provided with on the ground, and tank body is provided with underground, and aerator is provided with the tank body top; Solar panel, store battery and aerator are connected successively.
Filling nanoparticle suspension filler in the above-described main treatment zone, the upper end is provided with water inlet pipe, and the lower end is provided with aerating apparatus, and aerating apparatus is connected with aerator with aerating pipelines.
Upper end, above-described settling region sets out water pipe and tilted plate separator, and the lower end is provided with diversion trench and is communicated with main treatment zone.
Above-described aerator and store battery and/or mains-supplied are provided with automatic control.
Above-described aerating pipelines adopts the pipeline of plastics or metal.
The utility model compared with prior art has following characteristics:
1, as propulsion source, ability source clean, renewable reduces working cost to the utility model with sun power, and save energy also reduces conventional energy resources and uses the pollution that brings, and effectively solves decentralized type sewage and handles the supply of power problem.
2, the large-specific surface area nano floating stuffing provides and moves microbial film and active sludge coexistence system, improves coefficient of oxygen utilization and sewage treating efficiency, and organic loading is high, reduces the excess sludge generation simultaneously.
3, MBBR is designed to aerobic main reaction region and the settling region separates, and is communicated with through diversion trench, and mud does not need power consumption to reflux automatically, reduces operation energy consumption.
4, the optimization design that combines of MBBR design mixed flow and plug-flow, processing efficiency is high, and capacity of resisting impact load is strong.
5, the MBBR structure realizes simplification, the miniaturized, integrated and integrated of entire treatment system through optimizing and being embedded in undergroundly.This occupation area of equipment is little, and is simple in structure, and transportation and easy for installation is fit to decentralized type sewage and handles.
Description of drawings
Fig. 1 is the utility model sun power Nano filling MBBR structural representation.
Identify among the figure: 1-solar panel, 2-store battery, 3-aerator, 4-master's treatment zone, 5-rising pipe; The 6-tilted plate separator, 7-dividing plate, 8-settling region, 9-aerating pipelines, 10-diversion trench; The 11-aerating apparatus, 12-nanoparticle suspension filler, 13-tank body, 14-water inlet pipe.
Embodiment
To the utility model further explain, the embodiment that lifts only is used to explain the utility model below in conjunction with specific embodiment, is not the scope that is defined in the utility model.
Embodiment 1
Fig. 1 is the structural representation of the utility model, comprises solar power system and MBBR.Solar power system is provided with solar panel 1 and store battery 2, and MBBR is provided with tank body 13, and tank body 13 inner route clapboards 7 are separated out main treatment zone 4 and settling region 8.Filling nanoparticle suspension filler 12 in the main treatment zone 4, the upper end is provided with water inlet pipe 14, and the lower end is provided with aerating apparatus 11, and aerating apparatus 11 adopts the aerating pipelines 9 of plastics to be connected with aerator 3.8 upper ends, settling region set out water pipe 5 and tilted plate separator 6, and the lower end is provided with diversion trench 10 and is communicated with main treatment zone 4.Solar panel 1 is provided with on the ground with store battery 2, and tank body 13 is provided with underground, and aerator 3 is provided with the top of tank body 13.Solar panel 1, store battery 2 and aerator 3 are connected successively, and aerator 3 is provided with automatic control with store battery 2 and mains-supplied.
In the present embodiment, total hydraulic detention time is 9h, and the aeration of aerator 3 carries out aeration for controlling automatically, and aeration time is 8h every day, and aeration mode is aeration 10min, stops 20min.Sewage gets into main treatment zone 4 via water inlet pipe 14; Solar panel 1 is stored in the store battery 2 after luminous energy is converted into electric energy, and aerator 3 carries out aeration under the power supply of store battery 2 and civil power, filling nanoparticle suspension filler 12 in the main treatment zone 4; Interior filling nanoparticle suspension filler 12 proportions are near 1; Interior filling nanoparticle suspension filler 12 generates microbial film gradually behind device start, pollutants in sewage is removed under the effect of microbial film and active sludge, and sewage is purified; Sewage after the purification is via diversion trench 10 entering settling regions 8; Mud flows back to main treatment zone 4 by diversion trench 11 after tilted plate separator 6 sedimentations, the sewage after the processing is discharged water outlet pH, CODcr, NH through rising pipe 5
3Leading indicator such as-N, SS reach " urban wastewater treatment firm pollutant emission standard " (GB18918-2002) in one-level B standard qualified discharge go into surface water body.
Embodiment 2
Fig. 1 is the structural representation of the utility model, comprises solar power system and MBBR.Solar power system is provided with solar panel 1 and store battery 2, and MBBR is provided with tank body 13, and tank body 13 inner route clapboards 7 are separated out main treatment zone 4 and settling region 8.Filling nanoparticle suspension filler 12 in the main treatment zone 4, the upper end is provided with water inlet pipe 14, and the lower end is provided with aerating apparatus 11, and aerating apparatus 11 adopts the aerating pipelines 9 of metal to be connected with aerator 3.8 upper ends, settling region set out water pipe 5 and tilted plate separator 6, and the lower end is provided with diversion trench 10 and is communicated with main treatment zone 4.Solar panel 1 is provided with on the ground with store battery 2, and tank body 13 is provided with underground, and aerator 3 is provided with the top of tank body 13.Solar panel 1, store battery 2 and aerator 3 are connected successively, and aerator 3 is provided with automatic control with store battery 2.
In the present embodiment, total hydraulic detention time is 9h, and the aeration of aerator 3 carries out aeration for controlling automatically, and aeration time is 8h every day, and aeration mode is aeration 10min, stops 20min.Sewage gets into main treatment zone 4 via water inlet pipe 14; Solar panel 1 is stored in the store battery 2 after luminous energy is converted into electric energy, and aerator 3 carries out aeration under the power supply of store battery 2, filling nanoparticle suspension filler 12 in the main treatment zone 4; Interior filling nanoparticle suspension filler 12 proportions are near 1; Interior filling nanoparticle suspension filler 12 generates microbial film gradually behind device start, pollutants in sewage is removed under the effect of microbial film and active sludge, and sewage is purified; Sewage after the purification is via diversion trench 10 entering settling regions 8; Mud flows back to main treatment zone 4 by diversion trench 11 after tilted plate separator 6 sedimentations, the sewage after the processing is discharged water outlet pH, CODcr, NH through rising pipe 5
3Leading indicator such as-N, SS reach " urban wastewater treatment firm pollutant emission standard " (GB18918-2002) in one-level B standard qualified discharge go into surface water body.
Claims (5)
1. sun power Nano filling MBBR; Comprise solar power system and MBBR, it is characterized in that: described solar power system is provided with solar panel (1) and store battery (2), and MBBR is provided with tank body (13); Tank body (13) inner route clapboard (7) is separated out main treatment zone (4) and settling region (8); Solar panel (1) and store battery (2) are provided with on the ground, and tank body (13) is provided with underground, and aerator (3) is provided with tank body (13) top; Solar panel (1), store battery (2) and aerator (3) are connected successively.
2. a kind of sun power Nano filling MBBR according to claim 1; It is characterized in that: described main treatment zone (4) interior filling nanoparticle suspension filler (12); The upper end is provided with water inlet pipe (14); The lower end is provided with aerating apparatus (11), and aerating apparatus (11) is connected with aerator (3) with aerating pipelines (9).
3. a kind of sun power Nano filling MBBR according to claim 1 is characterized in that: described settling region (8) upper end sets out water pipe (5) and tilted plate separator (6), and the lower end is provided with diversion trench (10) and is communicated with main treatment zone (4).
4. a kind of sun power Nano filling MBBR according to claim 1 and 2 is characterized in that: described aerator (3) is provided with automatic control with store battery (2) and/or mains-supplied.
5. a kind of sun power Nano filling MBBR according to claim 2 is characterized in that: described aerating pipelines (9) adopts the pipeline of plastics or metal.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN2012201798439U CN202594841U (en) | 2012-04-24 | 2012-04-24 | Solar nanometer packing moving bed biofilm reactor |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN2012201798439U CN202594841U (en) | 2012-04-24 | 2012-04-24 | Solar nanometer packing moving bed biofilm reactor |
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| Publication Number | Publication Date |
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| CN202594841U true CN202594841U (en) | 2012-12-12 |
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| Application Number | Title | Priority Date | Filing Date |
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| CN2012201798439U Expired - Lifetime CN202594841U (en) | 2012-04-24 | 2012-04-24 | Solar nanometer packing moving bed biofilm reactor |
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Cited By (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105859021A (en) * | 2016-04-01 | 2016-08-17 | 江苏荆溪环保设备有限公司 | Novel solar water restoration device |
| CN105948228A (en) * | 2016-06-21 | 2016-09-21 | 温州三融环保科技有限公司 | Water body quality purification plant |
| CN106745747A (en) * | 2017-01-18 | 2017-05-31 | 海南天鸿市政设计股份有限公司 | Jet-flow aeration biomembrane reaction pond |
| CN106745748A (en) * | 2017-01-18 | 2017-05-31 | 海南天鸿市政设计股份有限公司 | Using the novel integrated biological reaction pool of solar energy |
| CN107879464A (en) * | 2017-11-24 | 2018-04-06 | 吉林建筑大学 | The sewage water treatment method and device of a kind of low-carbon energy-saving |
| CN111675314A (en) * | 2020-01-21 | 2020-09-18 | 深圳市辰中环境技术有限公司 | Moving bed biofilm reaction system |
| CN114031174A (en) * | 2021-11-22 | 2022-02-11 | 广州市水之道生态环境修复有限公司 | Solar energy circulation aeration suspension type biological filter |
-
2012
- 2012-04-24 CN CN2012201798439U patent/CN202594841U/en not_active Expired - Lifetime
Cited By (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105859021A (en) * | 2016-04-01 | 2016-08-17 | 江苏荆溪环保设备有限公司 | Novel solar water restoration device |
| CN105859021B (en) * | 2016-04-01 | 2019-04-23 | 江苏荆溪环保设备有限公司 | A kind of solar energy water body restoration device |
| CN105948228A (en) * | 2016-06-21 | 2016-09-21 | 温州三融环保科技有限公司 | Water body quality purification plant |
| CN106745747A (en) * | 2017-01-18 | 2017-05-31 | 海南天鸿市政设计股份有限公司 | Jet-flow aeration biomembrane reaction pond |
| CN106745748A (en) * | 2017-01-18 | 2017-05-31 | 海南天鸿市政设计股份有限公司 | Using the novel integrated biological reaction pool of solar energy |
| CN107879464A (en) * | 2017-11-24 | 2018-04-06 | 吉林建筑大学 | The sewage water treatment method and device of a kind of low-carbon energy-saving |
| CN111675314A (en) * | 2020-01-21 | 2020-09-18 | 深圳市辰中环境技术有限公司 | Moving bed biofilm reaction system |
| CN114031174A (en) * | 2021-11-22 | 2022-02-11 | 广州市水之道生态环境修复有限公司 | Solar energy circulation aeration suspension type biological filter |
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Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant | ||
| PE01 | Entry into force of the registration of the contract for pledge of patent right |
Denomination of utility model: Solar nanometer packing moving bed biofilm reactor Effective date of registration: 20140903 Granted publication date: 20121212 Pledgee: Bank of Communications Ltd the Guangxi Zhuang Autonomous Region branch Pledgor: Guangxi Yi River environmental protection science and Technology Co., Ltd.|Guangxi University Registration number: 2014990000733 |
|
| PLDC | Enforcement, change and cancellation of contracts on pledge of patent right or utility model | ||
| C56 | Change in the name or address of the patentee | ||
| CP01 | Change in the name or title of a patent holder |
Address after: 530001, building 5, science and Technology Park, 1, two hi tech Road, the Guangxi Zhuang Autonomous Region, Nanning Patentee after: Guangxi Yi Jiang environmental Polytron Technologies Inc Patentee after: Guangxi University Address before: 530001, building 5, science and Technology Park, 1, two hi tech Road, the Guangxi Zhuang Autonomous Region, Nanning Patentee before: Guangxi Yi Jiang environmental protection science and technology limited Company Patentee before: Guangxi University |
|
| PC01 | Cancellation of the registration of the contract for pledge of patent right |
Date of cancellation: 20190122 Granted publication date: 20121212 Pledgee: Bank of Communications Ltd the Guangxi Zhuang Autonomous Region branch Pledgor: Guangxi Yi Jiang environmental protection science and technology limited Company|Guangxi University Registration number: 2014990000733 |
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| PC01 | Cancellation of the registration of the contract for pledge of patent right | ||
| CX01 | Expiry of patent term |
Granted publication date: 20121212 |
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| CX01 | Expiry of patent term |