CN1164506C - Ceramic film tube bioreaction and separation system - Google Patents
Ceramic film tube bioreaction and separation system Download PDFInfo
- Publication number
- CN1164506C CN1164506C CNB011081899A CN01108189A CN1164506C CN 1164506 C CN1164506 C CN 1164506C CN B011081899 A CNB011081899 A CN B011081899A CN 01108189 A CN01108189 A CN 01108189A CN 1164506 C CN1164506 C CN 1164506C
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- film
- pipe
- bioreaction
- film pipe
- ceramic
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- 238000000926 separation method Methods 0.000 title claims abstract description 29
- 239000000919 ceramic Substances 0.000 title claims abstract description 14
- 238000005273 aeration Methods 0.000 claims abstract description 17
- 239000012528 membrane Substances 0.000 claims description 22
- 238000005842 biochemical reaction Methods 0.000 claims description 15
- 239000000463 material Substances 0.000 claims description 5
- MCMNRKCIXSYSNV-UHFFFAOYSA-N Zirconium dioxide Chemical compound O=[Zr]=O MCMNRKCIXSYSNV-UHFFFAOYSA-N 0.000 claims description 4
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims description 3
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 claims description 3
- TWNQGVIAIRXVLR-UHFFFAOYSA-N oxo(oxoalumanyloxy)alumane Chemical compound O=[Al]O[Al]=O TWNQGVIAIRXVLR-UHFFFAOYSA-N 0.000 claims description 3
- 229910052814 silicon oxide Inorganic materials 0.000 claims description 3
- OGIDPMRJRNCKJF-UHFFFAOYSA-N titanium oxide Inorganic materials [Ti]=O OGIDPMRJRNCKJF-UHFFFAOYSA-N 0.000 claims description 3
- 239000000706 filtrate Substances 0.000 claims description 2
- 239000011148 porous material Substances 0.000 claims description 2
- 238000006243 chemical reaction Methods 0.000 abstract description 6
- 238000011010 flushing procedure Methods 0.000 abstract description 3
- 238000005245 sintering Methods 0.000 abstract 1
- 239000007789 gas Substances 0.000 description 19
- 239000007788 liquid Substances 0.000 description 8
- 239000010865 sewage Substances 0.000 description 6
- 230000004907 flux Effects 0.000 description 5
- 230000000694 effects Effects 0.000 description 4
- 238000000034 method Methods 0.000 description 4
- 239000000203 mixture Substances 0.000 description 4
- 239000000126 substance Substances 0.000 description 4
- 238000005265 energy consumption Methods 0.000 description 3
- 238000000746 purification Methods 0.000 description 3
- 239000002253 acid Substances 0.000 description 2
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 2
- 229960000074 biopharmaceutical Drugs 0.000 description 2
- 230000015556 catabolic process Effects 0.000 description 2
- 238000005859 coupling reaction Methods 0.000 description 2
- 238000006731 degradation reaction Methods 0.000 description 2
- 230000008021 deposition Effects 0.000 description 2
- 239000012530 fluid Substances 0.000 description 2
- 238000009472 formulation Methods 0.000 description 2
- 244000005700 microbiome Species 0.000 description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 2
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 1
- 241000589651 Zoogloea Species 0.000 description 1
- 230000006978 adaptation Effects 0.000 description 1
- 238000013019 agitation Methods 0.000 description 1
- 238000012271 agricultural production Methods 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 229930013930 alkaloid Natural products 0.000 description 1
- 150000003797 alkaloid derivatives Chemical class 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 238000009395 breeding Methods 0.000 description 1
- 230000001488 breeding effect Effects 0.000 description 1
- 238000003889 chemical engineering Methods 0.000 description 1
- 238000001311 chemical methods and process Methods 0.000 description 1
- 239000012141 concentrate Substances 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 230000007797 corrosion Effects 0.000 description 1
- 230000008878 coupling Effects 0.000 description 1
- 238000010168 coupling process Methods 0.000 description 1
- 238000003795 desorption Methods 0.000 description 1
- 230000002542 deteriorative effect Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 239000006185 dispersion Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000000855 fermentation Methods 0.000 description 1
- 230000004151 fermentation Effects 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 230000002779 inactivation Effects 0.000 description 1
- 238000009776 industrial production Methods 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 229920002521 macromolecule Polymers 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 239000012764 mineral filler Substances 0.000 description 1
- 239000002052 molecular layer Substances 0.000 description 1
- 230000007935 neutral effect Effects 0.000 description 1
- 239000011664 nicotinic acid Substances 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 238000002203 pretreatment Methods 0.000 description 1
- 102000004169 proteins and genes Human genes 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
- 238000005086 pumping Methods 0.000 description 1
- 239000000376 reactant Substances 0.000 description 1
- 238000009738 saturating Methods 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000002352 surface water Substances 0.000 description 1
- 239000008399 tap water Substances 0.000 description 1
- 235000020679 tap water Nutrition 0.000 description 1
- 230000003245 working effect Effects 0.000 description 1
Images
Classifications
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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
Landscapes
- Separation Using Semi-Permeable Membranes (AREA)
Abstract
The present invention relates to a ceramic film tube bioreaction and separation system which comprises a biochemical reactor and a film pipe separator which are connected into a circulation loop, a film pipe is a ceramic tube whose inner wall is provided with a layer of multihole sintering film, the film pipe is a component part of the circulation loop, a film separator is operated in a negative pressure mode by a vacuum pump, the film separator is connected with a pressure air source, radial back flushing aeration is carried out toward the film pipe by the pressure air source, or an air lifting type aeration pipe is provided, and aerated air lifted in the film pipe is dissolved in a medium in an air bubble mode. The system is operated in a negative pressure mode, the system has mild reaction and no pump, the back flushing aeration and the air lift type aeration effectively solve the problem of film pollution, and the present invention is suitable for industrialized popularization.
Description
The present invention relates to a kind of ceramic film tube bioreaction and separation system, be used for various needs carry out biochemical reaction and and then reactant carried out isolating various field, as by the sewage purification process field of biochemical reaction degradation of organic substances, by fermentation or biochemical reaction production, concentrate, fields such as enrichment, purification biotechnological formulation and biologics.
Film and biological coupling reaction are a kind of new and high technologies of developing in recent years, it can be widely used in various physics and the chemical processes that need life entity such as microorganism, cell protein or macromolecular substance to participate in, the purifying treatment of for example various aqueous systems and surface water; The degradation treatment of the sewage that produces in the industrial and agricultural production and qualified discharge; The purifying treatment of tap water and pre-treatment; Fields such as biochemical reaction is produced, concentrated, enrichment, purification biotechnological formulation and biologics.Have important economic worth and social benefit in environment protection, biotechnology, chemical engineering in each field.Seeing the film of report and biological coupling reactive system at present remains in weak point and be: membrane module adopts organic high molecular layer more, and physical strength is low, and flux is little, and treatment capacity is little, is subject to the corrosion of microorganism and soda acid system, and chemical stability is poor, and work-ing life is short; System adopts positive pressure operation, material needs to send to face after the pump supercharging to be separated, cause film seriously polluted, fenestra stops up and causes filtration flux to reduce, can not steady in a long-term operate, the easy deteriorative reaction condition of vigorous agitation of pump convection cell generation causes life entity inactivation or death in addition, influences reaction effect; Direct aeration in reactor, energy consumption is big, also destroys the stability of biochemical reaction system easily.
The purpose of this invention is to provide a kind of ceramic film tube bioreaction and separation system, it can overcome the shortcoming of existing homogeneous system, and system is more suitable in biochemical reaction and isolating needs, can improve membrane flux, prevent that film from polluting, guarantee the stable operation of system, make it to be suitable for industrial applications.
Separation system of the present invention contains biochemical reactor and membrane separation apparatus, is connected to membrane separation apparatus behind the biochemical reactor, is linked to be the part circulation loop with pipeline, and system is provided with aerating apparatus, can be provided with machine or mineral filler, column plate, sieve plate in the reactor.Said membrane separation apparatus is made up of film pipe and housing, be provided with jacket space between film pipe and the housing, the film pipe is the vitrified pipe that inwall is loaded with the sintered porous film of one deck, this vitrified pipe can be hyperchannel or single passage, the mean pore size of porous-film is 5 nanometers～10 micron, selecting material as required is the porous-film of aluminum oxide or zirconium white, titanium oxide, silicon oxide, the film pipe is the integral part of circulation line, the filtrate exit pipe of membrane separation apparatus is connected with negative suction system, make system be in negative pressure state, liquid in pipe radially sees through tube wall and output is collected or discharging.Aerating apparatus of the present invention can be the pressure gas source that links to each other with membrane separation apparatus, by this pressure gas source to the film caliber to the recoil aeration, provide the required air of biochemical reaction or other gas, simultaneously towards the pollutent on demoulding surface.Above-mentioned recoil process is intermittently carried out, and during recoil, negative suction system quits work, and the two switches by valve, and the time length of the timed interval of recoil aeration and recoil process decides according to the oxygen requirement of biochemical reaction.Among the present invention, circulatory mediator flows in the film pipe from bottom to top, aerating apparatus can be provided in a side of the airway of film pipe lower end, the shower nozzle of airway exposes to the sun in the film pipe into biochemical reaction required air or other gas, and the gas dispersion of exposing to the sun becomes small bubbles to rise in the film pipe and dissolve in to participate in biochemical reaction in the medium.In one scheme of back, membrane separation apparatus also can link to each other with a recoil pressure source, and this pressure source is eliminated film and polluted only for the film pipe is recoiled in good time at this moment, can be pressed gas, also can be pressure fluid.
The mineral membrane that system of the present invention adopts, membrane flux is big, the physical strength height, the industrial applications of adaptation high throughput, the chemical stability of film is good, can not be corroded in the acid-alkali medium of biochemical reaction; The present invention adopts the negative-pressure operation of vacuum take-off to replace the positive pressure operation of existing system, need not to establish pump in the circulation loop, saves energy consumption, and guarantees that being reflected under the gentle and stable condition of system carry out, and is beneficial to zoogleic growth and breeding; The present invention adopts the film pipe recoil aeration that pressurizes in good time, exposes to the sun into the gaseous tension height, and the amount of dissolving in is big, and the mass-transfer efficiency height, and speed is fast.Simultaneously the pollutent attached to the film inside pipe wall is come off, guarantee that filter opening is unimpeded; In addition, the present invention is provided with aeration tube in film pipe lower end, mix effect with gas in the process of bubble gas lift in the film pipe, can prevent that pollutent in the medium is at the film surface deposition, improve the film contamination phenomenon greatly, the continuous bubble that rises forms Media density in the loop poor, and this density official post medium reaches the result who circulates continuously and stably.As seen, the film pipe biochemical reaction separation system of the present invention's design has improved the stability of Biochemistry Reaction System, has solved membrane pollution problem, the film toughness height, and flux is big, and energy consumption is low, is suitable for industrialization promotion.
Two flow implementation examples and film pipe cyclone separator arrangement below in conjunction with description of drawings system of the present invention.
Fig. 1 is the schema that the ceramic film tube bioreaction and separation system of the present invention of recoil aerating system is set.
Fig. 2 is the schema that the ceramic film tube bioreaction and separation system of the present invention of gas lift aerating system is set.
Fig. 3 is the structural representation of film pipe separator, and Fig. 4 is a film pipe cross-sectional structure embodiment synoptic diagram.
Among Fig. 1 embodiment, biochemical reactor 1 is linked to be circulation loop with film pipe separator 2, and the medium in the reactor returns reactor through valve F2 and also constantly circulates by valve F1, F4, under meter L1, film pipe separator 2, and D1 is a feed valve among the figure, and LS is a fluid level controller.The output tube of film pipe separator links to each other with vacuum pump 6, and when medium flow during through the film pipe, under the negative pressure-pumping effect, the radially saturating filmed passing tube of the liquid in the medium is realized solid-liquid separation.Isolated liquid is gone into liquid collecting jar 3 and is collected through valve D2 output.Number in the figure 4 is vacuum buffer tanks.In Fig. 1 flow process, separator 2 can to film pipe recoil aeration, can participate in biochemical reaction after recoil gas enters circulation loop by valve D3 by air compressor machine 7-1 (also can adopt gas bomb 8-1) input pressure gas.The pollutent of desorption on filter membrane that recoil simultaneously avoids fenestra to stop up.Also be provided with pressure buffer jar 10 in the backflushing pipe.
Set up air lift type aeration tube 9 among Fig. 2 embodiment, this aeration tube 9 is by air compressor machine 7-2 (or gas bomb 8-2) aeration in the film pipe of separator 2, provide biochemical reaction required gas to system, the bottom-up form that is dispersed into microvesicle by shower nozzle of gas is exposed to the sun in the film pipe, it can form gas to medium in the film pipe and mix, prevent deposition of solids at face, alleviate pollution filter membrane.Also be provided with pressure buffer jar 5 and under meter L2 on the aerating pipelines.Valve D3 among Fig. 2 connects recoiling device.Therefore this example can reduce the recoil operation because the microvesicle gas lift effect in the film pipe reduces the film pollution, even need not recoil.
The structure of film pipe separator 2 is seen Fig. 3, is jacket space 2-3 between film pipe 2-1 and the housing 2-2, and the two ends up and down of film pipe 2-1 are connected with circulation line with 2-5 with joint 2-4 respectively, and housing is provided with liquid discharge conection 2-7 and 2-6 is taken in the back flushing air input; Film pipe 2-1 can be single-pass deferent or hyperchannel vitrified pipe.Among Fig. 3, stretch into an air-lift tube 11 in the lower end pipeline 10 of membrane separation apparatus, the shower nozzle 11-1 of air-lift tube aeration in the film pipe, the 12nd, air pump.Fig. 4 represents the cross-sectional structure of multi-channel membrane, and as shown in Figure 4, film pipe 2-1 contains a plurality of passage 2-1-1, and the inwall of each passage is loaded with the sintered porous film 2-1-2 of one deck, and its material is aluminum oxide or zirconium white, titanium oxide, silicon oxide, (seeing A portion).Reaction substance Jie axial flow in passage, liquid wherein radially sees through porous-film 2-1-2 and supporting layer 2-1-3, and the two is cross-flow passes.
Application Example of the present invention is provided below.
Embodiment: the degraded purifying treatment of sanitary sewage
COD of sewage is 450 mg/litre before handling, ammonia-nitrogen content 20 mg/litre, and black, turbidity 2000NTU has obvious foul smell.
Add 20 liters of sewage in the reactor to certain liquid level, during system works, intake continuously to reactor by 85 milliliters/hour, add 5 gram zoogloeas in per 1000 milliliters of sewage, and drip bionic acid or alkaloid, regulate the pH value, make it keep neutral, temperature of reaction keeps about 20 ℃ of room temperatures.Separator adopts inwall to be loaded with the membrane pipe module of the sintered porous film of one deck, and the material of porous-film is a zirconium white.Open vacuum pump, the suction negative pressure is below 0.1Mpa.When adopting Fig. 1 system, started pneumatics pump aeration that recoils in per 20 minutes, continue 15 seconds at every turn, recoil pressure 0.5MPa during recoil, closes vacuum pump; If adopt Fig. 2 system, the continuous air feed of the air pump of airway, air pump pressure 0.02MPa, the gas lift circulation is carried out continuously, and the gas lift flow is 3 liters/minute.
Water outlet COD after present embodiment is handled is the 2-50 mg/litre, and the ammonia nitrogen amount is reduced to the 0.02-0.1 mg/litre, and water white transparency, turbidity be less than 4NTU, free from extraneous odour.
Claims (6)
1. ceramic film tube bioreaction and separation system, contain biochemical reactor and membrane separation apparatus, be connected to membrane separation apparatus behind the biochemical reactor, be linked to be the part circulation loop with pipeline, system is provided with aerating apparatus, it is characterized in that said membrane separation apparatus is made up of film pipe and housing, be provided with jacket space between film pipe and the housing, the film pipe is the vitrified pipe that is loaded with sintered porous film, and the film pipe is the integral part of circulation line, the filtrate outlet of membrane separation apparatus links to each other with negative suction system, is negative-pressure operation.
2. ceramic film tube bioreaction and separation system according to claim 1 is characterized in that said aerating apparatus is the pressure gas source that links to each other with membrane separation apparatus, by this pressure gas source to the film caliber to the recoil aeration.
3. ceramic film tube bioreaction and separation system according to claim 1, the medium that it is characterized in that said circulation loop flows in the film pipe from bottom to top, said aerating apparatus is arranged on the upwards airway of aeration of film pipe lower end, and the shower nozzle of airway exposes to the sun in the film pipe into the required gas of biochemical reaction.
4. ceramic film tube bioreaction and separation system according to claim 3, membrane separation apparatus is connected with the pressure source that is used to recoil.
5. according to claim 1 or 2 or 3 or 4 described ceramic film tube bioreaction and separation systems, it is characterized in that ceramic-film tube can be hyperchannel or single passage.
6. ceramic film tube bioreaction and separation system according to claim 5, the mean pore size that it is characterized in that porous-film are 5 nanometers～10 micron, and the material of porous-film can be aluminum oxide or zirconium white, titanium oxide, silicon oxide.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNB011081899A CN1164506C (en) | 2001-04-09 | 2001-04-09 | Ceramic film tube bioreaction and separation system |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNB011081899A CN1164506C (en) | 2001-04-09 | 2001-04-09 | Ceramic film tube bioreaction and separation system |
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| Publication Number | Publication Date |
|---|---|
| CN1310138A CN1310138A (en) | 2001-08-29 |
| CN1164506C true CN1164506C (en) | 2004-09-01 |
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| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CNB011081899A Expired - Fee Related CN1164506C (en) | 2001-04-09 | 2001-04-09 | Ceramic film tube bioreaction and separation system |
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Families Citing this family (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE10318736A1 (en) * | 2003-04-25 | 2004-11-11 | Thyssenkrupp Encoke Gmbh | Process for the treatment of coking plant waste water |
| CN102154408B (en) * | 2011-01-13 | 2013-06-05 | 天津市工业微生物研究所 | Sclerotium rolfssii scleroglucan online fermentation extraction method and system |
| CN102908963A (en) * | 2011-08-01 | 2013-02-06 | 江苏欧赛德钢涂有限公司 | Ceramic membrane filtering apparatus for transferring ethanol by using CO |
| CN102745815A (en) * | 2012-06-29 | 2012-10-24 | 宋瑞平 | Domestic sewage and wastewater advanced centralized treatment process |
| CN103977713B (en) * | 2014-04-24 | 2015-10-28 | 宁波信远膜工业股份有限公司 | A kind of ceramic support hybridization silicon oxide film preparation technique |
| CN105819903B (en) * | 2016-03-16 | 2019-06-25 | 武汉大学 | A kind of titanium nitride/aluminium oxide micro-filtrate and its preparation method and application |
| CN108101281A (en) * | 2017-12-20 | 2018-06-01 | 上海康盛环保能源科技有限公司 | A kind of catalytic ceramics membrane reactor |
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2001
- 2001-04-09 CN CNB011081899A patent/CN1164506C/en not_active Expired - Fee Related
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| CN1310138A (en) | 2001-08-29 |
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Assignee: JIANGSU JIUWU HITECH Co.,Ltd. Assignor: NANJING CHEMICAL University Contract fulfillment period: 2006.4.20 to 2016.4.20 Contract record no.: 2008320000318 Denomination of invention: Ceramic film tube bioreaction and separation system Granted publication date: 20040901 License type: Exclusive license Record date: 20080924 |
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