CN104649410A - Double-carrier fixed bed biomembrane reactor - Google Patents
Double-carrier fixed bed biomembrane reactor Download PDFInfo
- Publication number
- CN104649410A CN104649410A CN201310602802.5A CN201310602802A CN104649410A CN 104649410 A CN104649410 A CN 104649410A CN 201310602802 A CN201310602802 A CN 201310602802A CN 104649410 A CN104649410 A CN 104649410A
- Authority
- CN
- China
- Prior art keywords
- carrier
- support
- reactor
- bed biomembrane
- static bed
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
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
- C02F3/02—Aerobic processes
- C02F3/10—Packings; Fillings; Grids
-
- 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
- C02F3/02—Aerobic processes
- C02F3/10—Packings; Fillings; Grids
- C02F3/105—Characterized by the chemical composition
-
- 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
-
- 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
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Biodiversity & Conservation Biology (AREA)
- Microbiology (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Biological Treatment Of Waste Water (AREA)
Abstract
The invention discloses a double-carrier fixed bed biomembrane reactor which comprises a biomembrane carrier and a carrier, wherein the outer surface of the carrier is coated with antibacterial nanoparticles. According to the double-carrier fixed bed biomembrane reactor, the problems that the traditional fixed bed biomembrane reactor needs operations of periodically backwash and cleaning the carrier, replacing an aerator and the like can be overcome.
Description
Technical field
The present invention relates to a kind of static bed biomembrane reactor, particularly relate to a kind of complex carries static bed biomembrane reactor with biofilm carrier and antibacterial carrier.
Background technology
The process of highly difficult trade effluent proposes very large challenge to environmental protection industry (epi), and taking it by and large trade effluent has following feature: 1) differences between industries are very large; 2) COD value is higher, often crosses ten thousand; 3) one-tenth is grouped into very complicated, and some molecule is difficult to degraded, and toxicity is very large; 4) some waste water saltness is very high, and it is even higher that concentration reaches 50g/L; 5) impact load is very large, can reach peak value in the short period of time.
Meanwhile, the biochemistry of the nitrogenous substances of trade effluent is removed extremely important equally because nitrogenous too high be one of major reason causing body eutrophication, and causing toxicity very high to fish of Ammonia material, nitroso-group is carcinogenic substance in addition.Can carry out biochemical treatment to nitrogenous substances by nitrification and denitrification, but the cultivation of nitrifier and denitrifying bacteria is abnormal difficult, this is because: 1) reproduction speed of these mushrooms is very slow, and productive rate is very low, is easy to be taken out of from reaction tank by waste water; 2) very high to the susceptibility of potential of hydrogen, temperature and salinity; 3) organic and inorganic inhibitory substance is very large on the impact of nitration reaction, often causes nitration reaction unstable.
Effectively can remove all kinds of pollution substances of trade effluent by using biomembrane process.Carrier filler is the core of biomembrane process.Microorganism can on its huge surface flourish, rapidly form highly active microbial film.Microbial film utilizes C, N, P etc. in water to carry out metabolism, thus plays the effect of purifying waste water.The good processing power that why has biomembrane process should give the credit to fixing microbial film in the carrier, can obtain very high biomass by it.The advantage of high-biomass makes biomembrane process have the ability of good reply toxic pollutants load impact, and still can keep the stability of whole treating processes when influent quality fluctuation is larger.The performance quality of carrier, directly have influence on biomass in the complexity of biofilm, reactor number, reactor for treatment effect quality.
Along with the development of environmental protection industry, there is the structure formation of multiple biofilm reactor, to adapt to different wastewater treatment requirements, be mainly divided into fixed bed, fluidized-bed and moving-bed three major types.Static bed biomembrane reactor structure is simple, and carrier filler homogeneous reactor is placed in bed.The difference of it and fluidized bed bio membrane reactor and MBBR is that carrier remains static.The advantage that static bed biomembrane reactor possesses in Industrial Wastewater Treatment: 1) microorganic adhesion on fixing carrier so do not need sludge reflux; 2) floor space is little: under the condition of identical pollution load, and the pond that static bed biomembrane reactor accounts for standard biologic reactor 20-40% holds; 3) being suitable for the dilatation of industrial effluent treatment plant: in view of the reserved area of most of waste water treatment plant is less, when actual influent quality and the water yield change, meeting original design Effluent criteria when ensureing that original design pond holds constant; 4) upgrading of existing industrial effluent treatment plant is suitable for: static bed biomembrane reactor design and operation is simple flexibly, adapt to dissimilar pond type, and very strong with the compatibility of other technique, can with most of technique of built waste water treatment plant as A
2o, AO, SBR and oxidation ditch process etc. are combined.Therefore be suitable for the upgrading of existing waste water treatment plant, make it meet emission standard; 5) feature that static bed biomembrane reactor had both had other biological embrane method anti impulsion load, mud age is long, excess sludge is few, occur without sludge bulking phenomenon, has again the high efficiency of activated sludge process and going slick property.On the other hand, temperature variation will be far smaller than the impact on activated sludge process to the impact of static bed biomembrane technique, and when temperature, sewage composition change or sewage toxicity increases, the tolerance of static bed biomembrane reactor is very strong.
As can be seen here, static bed biomembrane reactor has development and apply prospect very much, simple and easy to operate because building, existing conventional sewage plants can be transformed under the condition not increasing reactor volume, make it to improve organic clearance and the object reaching denitrogenation dephosphorizing.
But although static bed biomembrane reactor is obtaining very large development in recent years, it is also having its distinctive defect, as constantly growth under long-time running microbes cloth full carrier between space, passing through of block air and current.This blocking can cause the effective volume of reactor to reduce, finally cause the distributivity of air and current very poor and make system process result degrades, thus traditional static bed biomembrane reactor needs periodically back flushing, cleaning carrier and changes the complex operations problems such as aerator.
Summary of the invention
The invention provides a kind of complex carries static bed biomembrane reactor, can overcome traditional static bed biomembrane reactor needs periodically back flushing, cleaning carrier and changes the complex operations problems such as aerator.
In order to reach above technique effect, technical scheme of the present invention is as follows:
A kind of complex carries static bed biomembrane reactor, comprising: reactor, has the first carrier and Second support in described reactor.
Described first carrier is used for the biofilm carrier of biofilm development.
Described Second support is the antibacterial carrier that outside surface scribbles anti-biotic material; Described Second support is distributed between described first carrier.
Described reactor is aerobic or one in anaerobic type reactor.
The material of described first carrier and Second support is amino formate filler.
Preferably, described amino formate filler is polyurethane foam.
Preferably, described antimicrobial nano particle is antibacterial metal nanoparticle.
Further, described antibacterial metal nanoparticle is the combination of any one or more in gold and silver, copper, zinc, titanium.
Further, described first carrier and Second support arrangement mode in reactor can be the one in following four kinds of modes:
(1) by the first carrier, Second support two kinds of carrier mixing placing response devices.
(2) the first carrier, Second support two kinds of fillers are put into reactor successively by horizontally-arranged, it puts in order, and to be that the first carrier is placed first horizontally-arranged, and Second support is placed second horizontally-arranged, and the first carrier is placed the 3rd horizontally-arranged, by that analogy.
(3) the first carrier, Second support two kinds of fillers are put into reactor successively by vertical setting of types, it puts in order is that the first carrier places the first vertical setting of types, and Second support places the second vertical setting of types, and the first carrier places the 3rd vertical setting of types, by that analogy.
(4), the first carrier, Second support two kinds of fillers are put into reactor successively by the mode replaced, it puts in order is the first carrier, Second support, first carrier, Second support, the first carrier, Second support are placed first horizontally-arranged, Second support, the first carrier, Second support, the first carrier, Second support, the first carrier are placed second horizontally-arranged, the first carrier, Second support, the first carrier, Second support, the placement the 3rd of first carrier, Second support is horizontally-arranged, by that analogy.
The present invention compared with prior art has following beneficial effect:
The invention provides a kind of complex carries static bed biomembrane reactor, breach the restriction of traditional static bed biomembrane reactor (blocking and water distribution inequality), good basis has been established in the biological treatment being applied more broadly in industrial sewage for static bed biomembrane method.The carrier scribbling antimicrobial nano particle by introducing a kind of outside surface can suppress microorganism to grow at this carrier surface effectively, the good distribution effects of air and current in keeping system, thus overcomes the blockage problem caused because of too high biological density.This carrier is blended between biofilm carrier and distributes, thus makes to keep relatively abundant space between biofilm carrier.Thisly scribble the carrier of antimicrobial nano particle by outside surface and be full of combined the formed space of microorganism carrier and can ensure that gas and current are by obtaining ideal distribution during reactor.The distinguished characteristic of the present invention makes it to tackle various extreme loads condition and there is not the problem of the aspects such as blocking and material transfer restriction.
Accompanying drawing explanation
Fig. 1 is according to complex carries fixed-bed reactor schematic diagram of the present invention;
Four kinds of arrangement modes of the first carrier and Second support in reactor shown in Fig. 2;
Wherein, A is the first carrier, and B is Second support.
Embodiment
Describe technical scheme of the present invention in detail below in conjunction with specific embodiment, be used for explaining technical scheme of the present invention in this illustrative examples of the present invention and explanation, but not as a limitation of the invention.
The present embodiment provides a kind of complex carries static bed biomembrane reactor, comprising: reactor, has the first carrier and Second support in described reactor; Described first carrier is used for the biofilm carrier of biofilm development; Described Second support is the antibacterial carrier that outside surface scribbles antimicrobial silver nanoparticle; Described Second support is distributed between described first carrier; Described reactor is aerobic or one in anaerobic type reactor; The material of described first carrier and Second support is polyurethane foam; Described antimicrobial nano particle is antibacterial metal nanoparticle; Described first carrier and Second support arrange by one of following four kinds of modes in reactor:
(1) by the first carrier, Second support two kinds of carrier mixing placing response devices.
(2) the first carrier, Second support two kinds of fillers are put into reactor successively by horizontally-arranged, it puts in order, and to be that the first carrier is placed first horizontally-arranged, and Second support is placed second horizontally-arranged, and the first carrier is placed the 3rd horizontally-arranged, by that analogy.
(3) the first carrier, Second support two kinds of fillers are put into reactor successively by vertical setting of types, it puts in order is that the first carrier places the first vertical setting of types, and Second support places the second vertical setting of types, and the first carrier places the 3rd vertical setting of types, by that analogy.
(4), the first carrier, Second support two kinds of fillers are put into reactor successively by the mode replaced, it puts in order is the first carrier, Second support, first carrier, Second support, the first carrier, Second support are placed first horizontally-arranged, Second support, the first carrier, Second support, the first carrier, Second support, the first carrier are placed second horizontally-arranged, the first carrier, Second support, the first carrier, Second support, the placement the 3rd of first carrier, Second support is horizontally-arranged, by that analogy.
The present invention breaches the restriction of traditional static bed biomembrane reactor (blocking and water distribution inequality), and good basis has been established in the biological treatment being applied more broadly in industrial sewage for static bed biomembrane method.The carrier scribbling antimicrobial nano particle by introducing a kind of outside surface can suppress microorganism to grow at this carrier surface effectively, the good distribution effects of air and current in keeping system, thus overcomes the blockage problem caused because of too high biological density.This carrier is blended between biofilm carrier and distributes, thus makes to keep relatively abundant space between biofilm carrier.Thisly scribble the carrier of antimicrobial nano particle by outside surface and be full of combined the formed space of microorganism carrier and can ensure that gas and current are by obtaining ideal distribution during reactor.The distinguished characteristic of the present invention makes it to tackle various extreme loads condition and there is not the problem of the aspects such as blocking and material transfer restriction.
The above is the preferred embodiment of the present invention; it should be pointed out that for those skilled in the art, under the premise without departing from the principles of the invention; can also make some improvements and modifications, these improvements and modifications are also considered as protection scope of the present invention.
Claims (10)
1. a complex carries static bed biomembrane reactor, comprising: reactor, has the first carrier and Second support, it is characterized in that in described reactor: described first carrier is used for the biofilm carrier of biofilm development; Described Second support is the antibacterial carrier that outside surface scribbles anti-biotic material; Described Second support is distributed between described first carrier.
2. a kind of complex carries static bed biomembrane reactor according to claim 1, is characterized in that: described reactor is aerobic or one in anaerobic type reactor.
3. a kind of complex carries static bed biomembrane reactor according to claim 1, is characterized in that: the material of described first carrier and Second support is amino formate filler.
4. a kind of complex carries static bed biomembrane reactor according to claim 1, is characterized in that: described antimicrobial nano particle is antibacterial metal nanoparticle.
5. a kind of complex carries static bed biomembrane reactor according to claim 3, is characterized in that: described amino formate filler is polyurethane foam.
6. a kind of complex carries static bed biomembrane reactor according to claim 4, is characterized in that: described antibacterial metal nanoparticle is the combination of any one or more in gold and silver, copper, zinc, titanium.
7. foretell a kind of complex carries static bed biomembrane reactor described in 6 any one according to claim, it is characterized in that: described first carrier and Second support arrangement mode in reactor is by the first carrier, Second support two kinds of carrier mixing placing response devices.
8. a kind of complex carries static bed biomembrane reactor according to any one of claim 1-6, it is characterized in that: described first carrier and Second support arrangement mode in reactor is by horizontally-arranged reactor of putting into successively by the first carrier, Second support two kinds of fillers, it puts in order, and to be that the first carrier is placed first horizontally-arranged, Second support is placed second horizontally-arranged, first carrier placement the 3rd is horizontally-arranged, by that analogy.
9. foretell a kind of complex carries static bed biomembrane reactor described in 6 any one according to claim, it is characterized in that: described first carrier and Second support in reactor arrangement mode for the first carrier, Second support two kinds of fillers are put into reactor successively by vertical setting of types, it puts in order is that the first carrier places the first vertical setting of types, Second support places the second vertical setting of types, first carrier places the 3rd vertical setting of types, by that analogy.
10. foretell a kind of complex carries static bed biomembrane reactor described in 6 any one according to claim, it is characterized in that: described first carrier and Second support arrangement mode in reactor is by the first carrier, Second support two kinds of fillers put into reactor successively by the mode replaced, it puts in order is the first carrier, Second support, first carrier, Second support, first carrier, Second support is placed first horizontally-arranged, Second support, first carrier, Second support, first carrier, Second support, first carrier is placed second horizontally-arranged, first carrier, Second support, first carrier, Second support, first carrier, Second support placement the 3rd is horizontally-arranged, by that analogy.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201310602802.5A CN104649410B (en) | 2013-11-26 | 2013-11-26 | A kind of complex carries static bed biomembrane reactor |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201310602802.5A CN104649410B (en) | 2013-11-26 | 2013-11-26 | A kind of complex carries static bed biomembrane reactor |
Publications (2)
Publication Number | Publication Date |
---|---|
CN104649410A true CN104649410A (en) | 2015-05-27 |
CN104649410B CN104649410B (en) | 2017-08-08 |
Family
ID=53241123
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201310602802.5A Expired - Fee Related CN104649410B (en) | 2013-11-26 | 2013-11-26 | A kind of complex carries static bed biomembrane reactor |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN104649410B (en) |
Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH081181A (en) * | 1994-06-24 | 1996-01-09 | Tonen Corp | Bacteria gel carrier and treatment of pollutant using the same |
CN1554599A (en) * | 2003-12-23 | 2004-12-15 | 清华大学 | Process for treating waste water by aerobic-anaerobic microbic repeated coupling |
CN2675237Y (en) * | 2003-10-08 | 2005-02-02 | 徐晓军 | Combined biological filtering device |
CN1631976A (en) * | 2003-12-24 | 2005-06-29 | 兰州大学 | Modified nano SiOx composite polyurethane foam and its preparation method and use |
CN101696073A (en) * | 2009-10-23 | 2010-04-21 | 兰州大学 | Two-phase distributing bioreactor and application in processing organic wastewater with high concentration |
CN202415260U (en) * | 2011-12-22 | 2012-09-05 | 河南中清环保工程设备有限公司 | Novel static-bed hybrid biological reaction system |
-
2013
- 2013-11-26 CN CN201310602802.5A patent/CN104649410B/en not_active Expired - Fee Related
Patent Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH081181A (en) * | 1994-06-24 | 1996-01-09 | Tonen Corp | Bacteria gel carrier and treatment of pollutant using the same |
CN2675237Y (en) * | 2003-10-08 | 2005-02-02 | 徐晓军 | Combined biological filtering device |
CN1554599A (en) * | 2003-12-23 | 2004-12-15 | 清华大学 | Process for treating waste water by aerobic-anaerobic microbic repeated coupling |
CN1631976A (en) * | 2003-12-24 | 2005-06-29 | 兰州大学 | Modified nano SiOx composite polyurethane foam and its preparation method and use |
CN101696073A (en) * | 2009-10-23 | 2010-04-21 | 兰州大学 | Two-phase distributing bioreactor and application in processing organic wastewater with high concentration |
CN202415260U (en) * | 2011-12-22 | 2012-09-05 | 河南中清环保工程设备有限公司 | Novel static-bed hybrid biological reaction system |
Also Published As
Publication number | Publication date |
---|---|
CN104649410B (en) | 2017-08-08 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Third et al. | Long-term aeration management for improved N-removal via SND in a sequencing batch reactor | |
Panswad et al. | Specific oxygen, ammonia, and nitrate uptake rates of a biological nutrient removal process treating elevated salinity wastewater | |
Wilderer et al. | The SBR and its biofilm application potentials | |
Rocher et al. | Municipal wastewater treatment by biofiltration: comparisons of various treatment layouts. Part 1: assessment of carbon and nitrogen removal | |
CN104710006A (en) | Improved A2/O biological membrane reactor capable of synchronously removing carbon, nitrogen and phosphorus, and operation method thereof | |
Rajesh Banu et al. | Trends in biological nutrient removal for the treatment of low strength organic wastewaters | |
CN100554195C (en) | A kind of waste water treatment process and purposes to high-ammonia nitrogen low C/N ratio | |
CN105384236A (en) | Novel combined packing dual-bed aeration biofilter device | |
CN101792715A (en) | Nitrifying bacterial agent and preparation method thereof | |
Rodgers et al. | Biological nitrogen removal using a vertically moving biofilm system | |
Chung et al. | Comparison of influence of free ammonia and dissolved oxygen on nitrite accumulation between suspended and attached cells | |
Lima et al. | Interpreting the effect of increasing COD loading rates on the performance of a pre-anoxic MBBR system: implications on the attached and suspended biomass dynamics and nitrification–denitrification activity | |
CN101708929A (en) | Method for treating wastewater generated in production process of isophthalonitrile | |
CN203048667U (en) | Novel denitrifying nitrogen removal device | |
CN204529455U (en) | Modified form A 2phosphorus reaction device is denitrogenated in the synchronous decarburization of/O microbial film | |
He et al. | An assessment of the purification performance and resilience of sponge-based aerobic biofilm reactors for treating polluted urban surface waters | |
KR20000055546A (en) | Apparatus for treating sewage or waste water with aquatic microorganism | |
CN105174653A (en) | Sewage treatment process and sewage treatment system for garbage landfill | |
KR101827525B1 (en) | Method for small medium size sewage advanced treatment using float media filtering | |
CN104671407A (en) | Improved A/O (anaerobic/aerobiotic) technique for treating acrylonitrile wastewater | |
Rodziewicz et al. | Anaerobic rotating disc batch reactor nutrient removal process enhanced by volatile fatty acid addition | |
CN104649410A (en) | Double-carrier fixed bed biomembrane reactor | |
CN103373768A (en) | Method for reducing biological slime in circulating water system | |
Makowska et al. | Removal of carbon and nitrogen compounds in hybrid bioreactors | |
Zhang et al. | Biological denitrification in simulated groundwater using polybutylene succinate or polylactic acid-based composites as carbon source |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
GR01 | Patent grant | ||
GR01 | Patent grant | ||
CF01 | Termination of patent right due to non-payment of annual fee | ||
CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20170808 Termination date: 20201126 |