WO2019165689A1 - Microbubble photobioreactor for economic microalgae cultivation - Google Patents
Microbubble photobioreactor for economic microalgae cultivation Download PDFInfo
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- WO2019165689A1 WO2019165689A1 PCT/CN2018/083710 CN2018083710W WO2019165689A1 WO 2019165689 A1 WO2019165689 A1 WO 2019165689A1 CN 2018083710 W CN2018083710 W CN 2018083710W WO 2019165689 A1 WO2019165689 A1 WO 2019165689A1
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- C12M—APPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
- C12M21/00—Bioreactors or fermenters specially adapted for specific uses
- C12M21/02—Photobioreactors
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- C12M23/00—Constructional details, e.g. recesses, hinges
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- C12M27/00—Means for mixing, agitating or circulating fluids in the vessel
- C12M27/18—Flow directing inserts
- C12M27/24—Draft tube
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- C12M29/00—Means for introduction, extraction or recirculation of materials, e.g. pumps
- C12M29/06—Nozzles; Sprayers; Spargers; Diffusers
- C12M29/08—Air lift
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- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12M—APPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
- C12M31/00—Means for providing, directing, scattering or concentrating light
- C12M31/02—Means for providing, directing, scattering or concentrating light located outside the reactor
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- C12M—APPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
- C12M41/00—Means for regulation, monitoring, measurement or control, e.g. flow regulation
- C12M41/02—Means for regulation, monitoring, measurement or control, e.g. flow regulation of foam
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- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
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- C12M41/00—Means for regulation, monitoring, measurement or control, e.g. flow regulation
- C12M41/26—Means for regulation, monitoring, measurement or control, e.g. flow regulation of pH
Definitions
- the invention belongs to the field of bioengineering, and in particular relates to a microbubble photobioreactor for economical microalgae cultivation.
- Economic microalgae is widely used in food, aquaculture, medicine, beauty, bioenergy and other industries because it is rich in a variety of biologically active substances.
- chlorella can be applied to single-cell protein production; Trichosanthes elegans is used in sea cucumber breeding; while Haematococcus pluvialis is rich in astaxanthin and has strong antioxidant capacity in health products, cosmetics,
- the pharmaceutical industry has a broad market. Therefore, the economic microalgae biomass energy industry is a new type of industry that countries are striving to develop first. To achieve rapid development of the economic microalgae biomass energy industry, the first condition is to obtain high-density biomass at low cost and efficiently.
- the main cultivation methods of economic microalgae are open-air culture and photobioreactor culture.
- Traditional open-air cultures have led to the development of microalgae culture processes due to their low controllability, large footprint, and easy to stain bacteria.
- photobioreactor culture has the characteristics of high controllability, small footprint, flexible operation, high yield and suitable for single culture, especially favored by economical microalgae cultivation.
- traditional photobioreactor cultivation still faces technical bottlenecks such as insufficient carbon supply, dissolved oxygen accumulation, and low utilization rate of light energy.
- the current main ideas include the improvement of the light source and the shortening of the optical path.
- Bourgoin et al. placed an illumination barrier consisting of photovoltaic cells in the center of the photobioreactor to provide the wavelengths required for growth of different microalgae species.
- Bazaire et al. provides 360 degree illumination to the reactor through built-in fiber optics.
- Friederich et al. collects and introduces the light flux generated by an external LED light source through a light pipe into the interior of the photobioreactor to provide illumination for the culture.
- Huang Xuxiong et al. achieves energy saving, shortened optical path, and improved utilization of light energy by reducing the inner diameter of the photobioreactor and incorporating LED strips.
- the optimization of the light source or optical path can not really improve the light energy effectively. Utilization, on the contrary, excess light may cause microalgae photorespiration to affect biomass production.
- Zheng Fanxi et al. supplied CO 2 to the hollow fiber membrane module external to the photobioreactor and mixed well with the medium to increase the CO 2 saturation rate in the medium.
- the principle of this method is to increase the gas-liquid mass transfer efficiency by increasing the contact time between the gas and the liquid through the porous structure of the filler.
- the external gas-liquid mixing device that is, the hollow fiber membrane module
- the invention patent also needs to be equipped with a liquid pump to pump the culture medium into the reactor body, which increases the system complexity and additional energy consumption.
- Patent No. CN105985910 passed the spray of the algae into the external absorption tower of the reactor by atomization spray to make full contact with the CO 2 gas passing through the bottom of the tower to improve gas-liquid mass transfer.
- the algae liquid passing through the absorption tower contains a higher CO 2 concentration and is pumped back into the reactor body via a liquid pump.
- This method utilizes the principle of increasing the gas-liquid specific surface area to increase CO 2 mass transfer.
- the algae liquid is highly likely to cause cell damage through the spray atomization device, thereby affecting its growth.
- a more reasonable and effective method for increasing the gas-liquid mass transfer specific surface area is atomizing bubbles, that is, microbubbles.
- microbubbles are widely used in the water treatment industry, which can effectively improve the mass transfer of dissolved oxygen.
- its application in the microalgae cultivation neighborhood is less, even if the existing related patents are mainly used for microalgae harvesting, for example, Pan Kehou et al. (Patent No. CN105002086) continuously floats the algae cells in the running pool through microbubbles. .
- Using microbubbles as a carrier for CO 2 gas can greatly increase the utilization of CO 2 by microalgae to overcome the bottleneck of insufficient carbon supply.
- the Chengguang mold uses an external microbubble generator to generate process water containing microbubbles, and supplies the process water to the photobioreactor for culturing the microalgae.
- Yang Weimin et al. (patent number CN106434326, etc.) cut the CO 2 bubbles in the gas-liquid two fluids into tiny bubbles by the high-speed axial rotation of the rotor screw pump, and then pass the microbubble containing microbubbles into the tubular photobioreaction.
- the microalgae are cultured in the device. In principle, both methods improve the biomass production of microalgae through the efficient gas-liquid mass transfer of microbubbles.
- the principle of microbubbles is to inject CO 2 gas into the spiral wound hose in the mixing chamber and soft.
- the water in the tube is mixed, and the CO 2 is dissolved in the liquid or retained in the form of tiny bubbles to form process water through a long residence time, and the process water is introduced into the culture system to provide the growth of the microalgae.
- the latter uses micro-bubble water to supply the culture system using the principle of mechanical shearing.
- the two only consider the mass transfer characteristics of the microbubbles, but ignore the advantages of the microbubble high-efficiency momentum conduction. They all adopt the method of external microbubble generator to make microbubble water. Therefore, it is necessary to use an additional liquid pump for photobioreaction.
- the body of the device supplies microbubble water and enhances liquid circulation.
- the size of the microbubbles generated by the two is uncontrollable, and there may be a problem of excess supply or insufficient supply for the carbon demand of different economic microalgae.
- the generation of microbubble water is accompanied by large energy consumption and more complicated microbubble production process.
- an object of the present invention is to provide a microbubble photobioreactor (MPBR) for economical microalgae cultivation, which can solve the main technical bottleneck faced by traditional culture and stimulate the growth potential of microalgae in one stop. Improve the economic microalgae biomass production, suitable for laboratory and large-scale cultivation.
- MPBR microbubble photobioreactor
- a microbubble photobioreactor for economical microalgae cultivation characterized in that it comprises a photobioreactor body having a predetermined volume, and a controllable particle size microbubble a generating device, a flow guiding device, and an LED wave frequency double-change illumination system;
- the controllable particle size microbubble generating device is disposed at a bottom of the photobioreactor body for providing carbon mass transfer required for economical microalgae cultivation And circulating power, while dissolving dissolved oxygen;
- the flow guiding device is suspended inside the photobioreactor body for promoting liquid circulation and microbubble mass transfer;
- the LED wave frequency double variable illumination system is disposed in the The outside or inside of the photobioreactor body is used to provide its optimal growth wavelength and light-dark frequency according to the needs of specific economic microalgae.
- the photobioreactor body has a tubular or plate-like structure, and a detachable reactor cover with an air outlet is disposed at a top thereof, and the bottom bolt is connected to the controllable particle size microbubble generating device.
- the bottom of the photobioreactor main body is provided in a funnel shape, but is not limited thereto.
- the controllable particle size microbubble generating device comprises a detachable base, a microporous ceramic membrane and an annular fixing piece;
- the detachable base comprises a substrate and a cavity disposed on the substrate, the substrate is provided with a base threadedly coupled to a bottom wall of the photobioreactor main body, the cavity being provided with a discharge end thread for connection with the discharge valve;
- a central portion of the upper portion of the cavity is provided with a conical groove
- An air inlet penetrating through the upper and lower ends of the cavity is disposed in a middle portion of the conical groove, and a lower end of the air inlet is connected to a variable diameter air inlet provided in a middle portion of the substrate, and the variable diameter is
- the other end of the gas nozzle is connected to the CO 2 mixed gas through the intake valve and the intake pipe in sequence;
- the microporous ceramic diaphragm is fixedly disposed on the cone groove through the annular fixing piece, the microporous
- the upper surface of the microporous ceramic membrane is provided with a plurality of micropores for gas circulation, and the microporous ceramic membrane is internally provided with a plurality of drainage channels for uniformly distributing incident gas, and each of the drainage channels
- the inlet is located on the side of the microporous ceramic membrane.
- the pore diameter of the upper surface of the microporous ceramic membrane is 0.01 to 10 ⁇ m.
- the gap between the side surface of the microporous ceramic membrane and the groove of the cone is 1 to 2 mm.
- the flow guiding device is suspended inside the photobioreactor main body by a guiding fulcrum disposed at upper and lower ends thereof, and the guiding device divides the interior of the photobioreactor main body into a rising zone and a descending zone, the rising zone refers to the photobioreactor body cavity portion located inside the flow guiding device, and the descending zone refers to the photobioreaction located outside the flow guiding device The body cavity portion.
- the flow guiding device When the external illumination is used, the flow guiding device is made of a specular reflective material, and the inner wall of the photoreactor body is made of a transparent plexiglass material; when the built-in illumination is used, the flow guiding device adopts a lens plexiglass material, and the The inner wall of the photoreactor body is made of a mirror reflective material.
- the LED wave frequency double-variation illumination system comprises a preset number and proportion of white, red and blue LED lamp beads, a frequency conversion system and a time relay; the frequency conversion system is used for controlling the LED lamp bead according to actual cultivation requirements. Realizing white, red, blue and combined illumination of any two or more wavelengths, and adjusting the illumination intensity; the time relay is used to control the LED lamp bead according to actual cultivation requirements, and realize illumination time and dark processing time adjustment .
- the invention adopts the above technical solutions, and has the following advantages: 1.
- the invention provides a controllable particle size microbubble generating device at the bottom of the microbubble photobioreactor body, and utilizes the efficient mass transfer and momentum conduction capability of the microbubbles to provide economy.
- the microalgae rapidly grows the carbon source needed, and at the same time drives the algae cells to enter the descending zone to receive light, which improves the utilization rate of light energy and photosynthetic efficiency, reduces process complexity and maintenance cost, reduces floor space, and is one-stop. Solve the bottleneck of traditional technology. 2.
- the present invention provides a microporous gas outlet surface at the top of the microporous ceramic membrane in the controllable particle size microbubble generating device, and a drainage channel is arranged inside the membrane, so that the generated microbubbles are evenly distributed, the flux is large, and the gas resistance is small. It can be adjusted in size and flexible in application. 3.
- the microbubble photobioreactor since the microbubble photobioreactor is used, it is possible to accurately control the internal culture solution of the microbubble photobioreactor by using a single dose of carbonate and continuous microbubble ventilation without using additional pH monitoring and regulating equipment.
- the pH is in the optimum range, reducing process complexity and maintenance costs.
- the present invention can be widely applied to economical microalgae cultivation.
- FIG. 1(a) is a schematic view showing the structure of a microbubble photobioreactor for economical microalgae cultivation according to the present invention
- Figure 1 (b) is a 3D schematic view of a microbubble photobioreactor for economical microalgae cultivation of the present invention
- FIG. 2(a) is a schematic structural view of a microbubble generator of the present invention
- Figure 2 (b) is a 3D schematic view of the microbubble generator of the present invention.
- Figure 2 (c) is a schematic view of the microbubble generator base 3D of the present invention.
- Figure 3 is a schematic view showing the cultivation of economic microalgae using a microbubble photobioreactor
- FIG. 4(a) is a schematic view showing a plurality of unit ring-type joint structures of a microbubble photobioreactor according to the present invention
- 4(b) is a schematic view showing a plurality of unit line type joint structures of the microbubble photobioreactor of the present invention.
- Figure 5 (a) is a diagram showing the particle size distribution of microbubbles generated by different pore microporous ceramic membranes of the present invention
- Figure 5 (b) is a test result of the mass transfer coefficient of the microbubble photobioreactor under different conditions of the present invention.
- Microbubble photobioreactor (MPBR); 2. Controllable particle size microbubble generator; 3. Built-in diversion tube; 4. Guide device fulcrum; , photobioreactor main body; 6, reactor cover; 7, LED wave frequency double variable illumination system; 8, unloading valve; 9, intake valve; 10, microporous ceramic diaphragm; 11, diversion channel; 12, annular fixed piece; 13, base; 14, base fastening thread; 15, unloading end thread; 16, curved air cavity; 17, annular fixing piece first fastening nut; 18, annular fixing piece second tight Solid nut; 19, variable diameter air inlet; 20, microbubble photobioreactor bracket; 21, fixed clamp; 22, fixed bottom; 23, intake pipe; 24, algae liquid; 25, CO 2 mixture ; 26, air outlet.
- MPBR Microbubble photobioreactor
- the present invention provides a microbubble photobioreactor for economical microalgae cultivation, comprising: a microbubble photobioreactor 1, the microbubble photobio
- the reactor 1 comprises a photobioreactor body 5 having a predetermined volume, a controllable particle size microbubble generating device 2, a flow guiding device 3, and an LED wave frequency dimorphic illumination system 7.
- controllable particle size microbubble generating device 2 is disposed at the bottom of the photobioreactor main body 5 for providing carbon mass transfer and circulating power required for economical microalgae cultivation, and simultaneously analyzing dissolved oxygen; the flow guiding device 3 is suspended at The inside of the photobioreactor body 5 is used to promote liquid circulation and microbubble mass transfer and can adjust the suspension height according to actual needs; the LED wave frequency double-variation illumination system 7 is disposed outside or inside the photobioreactor body 5 for Provide optimal growth wavelength and light-dark frequency according to the demand of specific economic microalgae.
- the photobioreactor body 5 is of a tubular or plate-like structure, the top of which is provided with a detachable reactor cover 6 with an air outlet 26, and the bottom bolt is connected to the controllable particle size microbubble generating device 2.
- the controllable particle size microbubble generating device 2 includes a detachable base 13, a microporous ceramic diaphragm 10, and an annular fixing piece 12.
- the detachable base 13 includes a substrate and a cavity disposed on the substrate, and the base is provided with a base fastening thread 14 for bolting to the bottom side wall of the photobioreactor body 5, and the cavity is provided with a connection for unloading a discharge end thread 15 of the valve 8; a conical groove is arranged in the center of the upper portion of the cavity, and an air inlet is formed in the middle of the conical groove through the upper and lower ends of the cavity, and the lower end of the inlet is disposed in the middle of the substrate
- the variable diameter air inlet nozzle 19 is connected, and the other end of the variable diameter air inlet nozzle 19 is sequentially connected to the CO 2 mixed gas 25 through the intake valve 9 and the intake duct 23; the microporous ceramic diaphragm 10 is
- the upper surface of the microporous ceramic membrane 10 is provided with a plurality of micropores for gas circulation, and the pore diameter of the micropores is 0.01 to 10 micrometers; the microporous ceramic membrane 10 is provided with a plurality of diversion channels 11 inside, and each diversion flow
- the inlet of the canal 11 is located on the side of the microporous ceramic membrane 10 for distributing the incident gas to prevent microbubble accumulation in a certain area of the microporous gas outlet surface, thereby ensuring uniform distribution of the microbubbles.
- the flow guiding device 3 is suspended from the cavity of the photobioreactor main body 5 by a baffle fulcrum 4 disposed at the upper and lower ends thereof, and the flow guiding device 3 divides the interior of the photobioreactor main body 5 into a rising region and
- the descending zone refers to the cavity portion of the photobioreactor body 5 located inside the flow guiding device 3, and the descending zone refers to the cavity portion of the photobioreactor body 5 located outside the flow guiding device 3.
- the flow guiding device 3 can adopt a hollow draft tube or a baffle according to the structure of the photobioreactor main body 5.
- the photobioreactor main body 5 has a tubular structure
- a hollow diversion tube is used, when photobioreaction
- a baffle is used.
- the flow guiding device 3 can be replaced, position adjusted, cleaned, etc. according to actual cultivation needs.
- the LED wave frequency double-change illumination system 7 includes white, red, and blue three-color LED lamp beads, a frequency conversion system, and a time relay of a preset number and proportion.
- the frequency conversion system is used to realize the combined illumination of white, red, blue and any two or more wavelengths according to the actual culture requirements, and adjust the illumination intensity; the time relay is used to adjust the illumination time and dark processing time according to the actual culture requirements. To achieve "light flash effect" and improve photosynthetic efficiency.
- the bottom of the photobioreactor body 5 can be arranged in a funnel shape for reducing cell sedimentation buildup by structural dead angles while promoting fluid circulation. It will be appreciated that the photobioreactor body 5 can employ other structures that are effective in reducing structural dead angles.
- the photobioreactor body 5 employs a higher aspect ratio for increasing the residence time of the gas phase in the photobioreactor body 5 and reducing the footprint.
- the specific value of the aspect ratio of the photobioreactor main body 5 can be determined according to the specific culture scale and the target mass transfer value.
- the lower surface of the annular fixing piece 12 is provided with a groove for placing a 0-shaped rubber ring, and the annular fixing piece 12 passes through the annular fixing piece first,
- the second fastening nuts 17, 18 achieve a point pressure seal.
- controllable particle size microbubble generating device 2 can adopt an integrated design in consideration of the convenience of engineering operation, wherein the microporous ceramic diaphragm 10 and the microbubble generator base 13 and The annular fixing piece 12 is bonded by superglue or other means to form a microbubble generator having a fixed aperture, and the target microbubble particle size is obtained directly by replacing the microbubble generators of different apertures.
- the flow guiding device 3 adopts a specular reflective material that can increase the light reflection to improve the utilization of light energy, and the photobioreactor main body 5 is made of a transparent plexiglass material, when the built-in illumination is used.
- the photobioreactor main body 5 is made of a mirror reflective material.
- the ratio of the inner diameter to the inner diameter of the cavity of the photobioreactor body 5 is determined according to the actual culture scale to increase the interior of the photobioreactor body 5.
- the flow rate of the liquid in the ascending and descending zones and reduces the residence time.
- the microbubble photobioreactor for economical microalgae cultivation of the present invention further comprises a microbubble photobioreactor support 20, which is a rectangular parallelepiped frame, the cuboid frame
- a fixing base 22 is disposed on one side of the bottom portion for fixing the bottom of the photobioreactor main body 5
- a fixing clamp 21 is disposed on one side of the upper portion of the rectangular parallelepiped frame for fixing the upper portion of the photobioreactor main body 5, and each side of the rectangular parallelepiped frame It is used to fix the three-color LED lamp bead in the LED wave frequency double-change illumination system 7.
- the method for using the microbubble photobioreactor for economical microalgae cultivation of the present invention is further described below, and specifically includes the following steps:
- the microbubble photobioreactor 1 when used to carry out single unit culture of economic microalgae, the microbubble photobioreactor 1 is placed in the microbubble photobioreactor holder 20, by fixing the bottom tray 22 and The fixing clip 21 fixes it.
- the LED wave frequency double growth lamp in the illumination system is placed around the microbubble photobioreactor 1 or fixed to the reactor holder 20.
- the CO 2 mixed gas 25 is supplied from a high pressure gas cylinder and enters the controllable particle size microbubble generating device 2 through the intake pipe 23.
- the CO 2 mixed gas enters the curved air chamber 16 through the variable diameter nozzle 19 to accumulate the pressure, and enters the internal guide channel 11 from the side of the microporous ceramic diaphragm 10, and is generated on the microporous gas outlet surface of the microporous ceramic diaphragm 10.
- Uniformly distributed microbubbles The microbubbles ejected by the controllable particle size microbubble generating device 2 enter the photobioreactor main body 5.
- the inside of the diversion device 3 is a dark area, and the outside is a light area, a dark area, and a micro area.
- the bubble rise causes the liquid to rise.
- the rising liquid drops in the light zone, thereby achieving alternating circulating flow of the liquid in the dark zone and the light zone (as indicated by the arrow in Fig. 1(a)).
- the liquid surface of the algae liquid 24 in the photobioreactor main body 5 and the reactor cover 6 reserve a space to prevent the liquid surface from overflowing, and the exhaust gas is discharged through the gas outlet port 26.
- a plurality of reactor units can also be connected in a circular or linear shape to achieve a large-scale culture volume requirement.
- multiple reactor units operate in parallel with better controllability and flexibility while facilitating maintenance.
- Embodiment 1 is a diagrammatic representation of Embodiment 1:
- microporous ceramic membranes with different pore diameters are used to form a microbubble photobioreactor, and the particle size distribution of the microbubble photobioreactor is as follows. Mass transfer performance was tested.
- Fig. 5(a) it is the result of microbubble particle size distribution of the microbubble photobioreactor.
- a 1% CO 2 mixed gas was introduced at a flow rate of 50 ml min ⁇ 1 to generate microbubbles composed of four different pore size microporous ceramic membranes (type 1, species 2, species 3, species 4).
- the average particle diameter d 32 of the microbubbles produced was 554 ⁇ m, 464 ⁇ m, 333 ⁇ m, and 115 ⁇ m, respectively.
- the type 1 ceramic diaphragm produces larger microbubbles, and about 30% of the microbubbles have a particle size of 400-500 um, which can be used for pre-cultivation of most economical microalgae or pre-cultivation of laboratory algae.
- the number of microbubbles with a particle size of 100-200 ⁇ m accounts for about 35% and 65%, respectively, and can be used for the early stage or laboratory algae species of economic microalgae logarithmic growth. Expanded.
- the type 4 ceramic diaphragm produces the smallest microbubbles, about 65% of the microbubbles have a particle size of less than 100 ⁇ m, and 25% of the microbubbles have a particle size of less than 50 ⁇ m, which can be used for the middle or late stage of economical microalgae logarithmic growth or high scale. Density culture.
- the mass transfer performance of the four microbubble generators composed of different pore microporous ceramic membranes under different gas fluxes and different reactor height to diameter ratios was tested.
- the mass transfer coefficient K L a increases with the increase of gas flux or height to diameter ratio; for the same gas flux and high aspect ratio conditions, the mass transfer coefficient K L a increases as the average particle size of the microbubbles decreases.
- the mass transfer coefficient of the microbubble generator composed of the above four different pore microporous ceramic membranes can reach 0.0035min -1 -1.92min -1 , which is about 200 ⁇ of the mass transfer performance of traditional bubbles (for example, particle size 3mm).
- the present invention provides the main factors affecting mass transfer performance (bubble particle size, reactor height to diameter ratio, gas flux) and mass transfer coefficient.
- the mathematical model between them provides a theoretical basis for the preferred method of microbubble photobioreactor structure and operating parameters.
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Abstract
Description
本发明属于生物工程领域,特别是涉及一种用于经济微藻培养的微泡光生物反应器。The invention belongs to the field of bioengineering, and in particular relates to a microbubble photobioreactor for economical microalgae cultivation.
经济微藻因富含多种生物活性物质,在食品、水产养殖、医药、美容、生物能源等行业具有广泛的应用。例如小球藻可以应用于单细胞蛋白生产;三角褐指藻被应用于海参养殖育苗;而雨生红球藻因其富含虾青素,具有强大的抗氧化能力,在保健品,化妆品,医药行业拥有广阔市场。因此,经济微藻生物质能产业是各国争先发展的新型产业。而要实现经济微藻生物质能产业的快速发展,首要条件是低成本且高效地获取高密度生物量。Economic microalgae is widely used in food, aquaculture, medicine, beauty, bioenergy and other industries because it is rich in a variety of biologically active substances. For example, chlorella can be applied to single-cell protein production; Trichosanthes elegans is used in sea cucumber breeding; while Haematococcus pluvialis is rich in astaxanthin and has strong antioxidant capacity in health products, cosmetics, The pharmaceutical industry has a broad market. Therefore, the economic microalgae biomass energy industry is a new type of industry that countries are striving to develop first. To achieve rapid development of the economic microalgae biomass energy industry, the first condition is to obtain high-density biomass at low cost and efficiently.
目前经济微藻的主要培养方式为露天培养和光生物反应器培养。传统的露天培养由于可控性不高、占地面积大、易染菌等缺点,使得微藻培养工艺的研发趋势慢慢推向了光生物反应器。相比露天培养,光生物反应器培养具有培养条件可控性高、占地面积小、操作灵活、产率高及适合单一性培养等特点,尤其受到经济微藻培养的青睐。但是传统光生物反应器培养仍然面临着供碳不足、溶氧堆积、光能利用率低等技术瓶颈。具体体现如下:At present, the main cultivation methods of economic microalgae are open-air culture and photobioreactor culture. Traditional open-air cultures have led to the development of microalgae culture processes due to their low controllability, large footprint, and easy to stain bacteria. Compared with open-air culture, photobioreactor culture has the characteristics of high controllability, small footprint, flexible operation, high yield and suitable for single culture, especially favored by economical microalgae cultivation. However, traditional photobioreactor cultivation still faces technical bottlenecks such as insufficient carbon supply, dissolved oxygen accumulation, and low utilization rate of light energy. The specific embodiment is as follows:
(a)、光能利用率低:在较高细胞浓度时,易发生藻间遮蔽效应,使得藻细胞对光源的利用变得十分有限,从而难以实现经济微藻的高密度培养。(a) Low utilization rate of light energy: At higher cell concentrations, the inter-algae shielding effect is liable to occur, so that the utilization of the light source by the algae cells becomes very limited, and it is difficult to achieve high-density culture of economic microalgae.
(b)、CO 2供给不足:微藻的供碳主要通过通入一定比例的CO 2气体来实现,而在实际培养过程中,CO 2的供给并不能满足微藻最优生长的需求。有研究显示微藻对CO 2的吸收速度高达0.2~0.3×10 -4mol/L/min。而传统曝气方式的CO 2传质速率仅为0.4×10 -7~0.7×10 -5mol/L/min,远不能满足微藻对溶解CO 2的需求。因此,即使光照充足,如果反应器达不到充足的CO 2供给,同样无法使得微藻最优生长。 (b) Insufficient supply of CO 2 : The supply of carbon by microalgae is mainly achieved by introducing a certain proportion of CO 2 gas, and in the actual cultivation process, the supply of CO 2 cannot satisfy the requirement of optimal growth of microalgae. Studies have shown that the absorption rate of CO 2 by microalgae is as high as 0.2 to 0.3×10 -4 mol/L/min. The conventional aeration mode CO 2 mass transfer rate is only 0.4×10 -7 to 0.7×10 -5 mol/L/min, which is far from satisfying the demand of microalgae for dissolving CO 2 . Therefore, even if the light is sufficient, if the reactor does not reach a sufficient supply of CO 2 , the microalgae cannot be optimally grown.
(c)、溶氧积累严重:微藻的光合放氧速率可达0.3×10 -4mol/L,而传统鼓气对O 2的吹脱速率只有约0.16×10 -4mol/L/min,小于微藻的光合放氧速率。因此,在密闭培养中容易发生溶氧的累积,造成溶氧过饱和从而抑制藻类生长。 (c) The accumulation of dissolved oxygen is serious: the photosynthetic oxygen evolution rate of microalgae can reach 0.3×10 -4 mol/L, while the conventional blown gas to O 2 is only about 0.16×10 -4 mol/L/min. , less than the photosynthetic oxygen evolution rate of microalgae. Therefore, accumulation of dissolved oxygen easily occurs in the closed culture, causing supersaturation of dissolved oxygen to suppress algae growth.
关于光能利用率的优化,目前的主要思路包括光源的改进和光路的缩短。例如Bourgoin等(专利号US20130029404A1)将由光伏电池组成的照明隔板置于光生物反应器中心,为不同微藻品种提供生长所需波长。Bazaire等(专利号US20090203116A1)通过内置光纤为反应器提供360度光照。Friederich等(专利号US20140073035A1) 通过导光管将外置LED光源产生的光通量收集并导入光生物反应器内部,为培养提供光照。黄旭雄等(专利号CN104651215A)通过减小光生物反应器内径,并内置LED灯带的方式,实现节能、缩短光程、提高光能利用率等目的。除此之外,还有许多类似的设计,在一定程度上提高了反应器的光能利用率。然而这些设计并没有从根本上解决高浓度时藻间遮蔽的问题,此外,在传统CO 2供给不能满足微藻快速生长所需的条件下,光源或光路的优化并不能真正有效地提高光能利用率,相反过剩的光照可能导致微藻光呼吸作用从而影响生物质产量。 Regarding the optimization of light energy utilization, the current main ideas include the improvement of the light source and the shortening of the optical path. For example, Bourgoin et al. (Patent No. US20130029404A1) placed an illumination barrier consisting of photovoltaic cells in the center of the photobioreactor to provide the wavelengths required for growth of different microalgae species. Bazaire et al. (Patent No. US20090203116A1) provides 360 degree illumination to the reactor through built-in fiber optics. Friederich et al. (Patent No. US20140073035A1) collects and introduces the light flux generated by an external LED light source through a light pipe into the interior of the photobioreactor to provide illumination for the culture. Huang Xuxiong et al. (patent number CN104651215A) achieves energy saving, shortened optical path, and improved utilization of light energy by reducing the inner diameter of the photobioreactor and incorporating LED strips. In addition, there are many similar designs that improve the light energy utilization of the reactor to some extent. However, these designs do not fundamentally solve the problem of inter-algae shielding at high concentrations. In addition, under the conditions that the traditional CO 2 supply cannot meet the rapid growth of microalgae, the optimization of the light source or optical path can not really improve the light energy effectively. Utilization, on the contrary, excess light may cause microalgae photorespiration to affect biomass production.
对于CO 2供给不足及溶氧堆积问题,提高曝气装置的气液传质能力是主要的解决方法。郑范锡等(专利号CN102776117)将CO 2供应至光生物反应器外接的中空纤维膜模件中,与培养基充分混合,增加培养基中的CO 2饱和率。此方法的原理是通过填料的多孔结构,增加气体与液体接触时间,从而提高气液传质效率。然而该发明专利中的外接气液混合装置(也就是中空纤维膜模件)还需要配备液体泵将培养基抽吸到反应器主体中,增加了系统复杂程度及额外能耗。施云海等(专利号CN105985910)通过将藻液以雾化喷淋的方式通入反应器外接吸收塔中,使其与塔底部通入的CO 2气体充分接触,以提高气-液传质。经过吸收塔的藻液含有较高CO 2浓度,经液体泵抽回反应器主体中。此方法利用增加气-液比表面积的原理提高CO 2传质。然而,藻液经过喷淋雾化装置极有可能造成细胞损伤,从而影响其生长。相比雾化藻液,增加气-液传质比表面积更为合理且有效的方法是雾化气泡,即微气泡。目前,微气泡被广泛应用于水处理业,可有效提高溶氧的传质。而其在微藻培养邻域的应用较少,即使已有的相关专利也主要用于微藻采收,例如潘克厚等(专利号CN105002086)通过微气泡持续气浮采收跑池中的藻细胞。将微泡作为CO 2气体的载体,可大幅增加微藻对CO 2利用率从而克服供碳不足的瓶颈。成光模(专利号CN102978102A)利用外接微泡发生器产生含有微泡的工艺水,并将工艺水供应至光生物反应器用于培养微藻。杨卫民等(专利号CN106434326等)通过转子螺旋泵的高速轴向旋转,将气液两项流体中的CO 2气泡切成微小气泡,之后将含有微小气泡的微泡液通入管式光生物反应器中培养微藻。这两个方法在原理上均通过微泡高效的气液传质提高微藻的生物质产量,然而前者微泡产生的原理是将CO 2气体注入到混合室内呈螺旋缠绕的软管中与软管中的水混合,通过较长的停留时间,CO 2溶于液体或以微小气泡形式滞留于水中形成工艺水,再将工艺水通入培养体系中提供微藻生长所需。后者利用机械剪切的原理产生微泡水,供给培养体系。然而两者只考虑到了微泡的传质特性,却忽略了微泡高效动量传导的优点,均采取了外接微泡发生器的方式制作微泡水,因此需通过额外的液体泵为光生物反应器主体供给微泡水及加强液体循环。此外两者产生的微气泡大小不可控,对于不同经济微藻对碳的需求量可能存在供给过剩或供给不足的问题。同时,微泡水的产生还伴 随着较大的能耗以及较复杂的微泡产生工艺,在工业化扩大的应用中可能存在维护成本、能耗成本、建造成本等过高的问题。 For the problem of insufficient CO 2 supply and dissolved oxygen accumulation, improving the gas-liquid mass transfer capability of the aeration device is the main solution. Zheng Fanxi et al. (Patent No. CN102776117) supplied CO 2 to the hollow fiber membrane module external to the photobioreactor and mixed well with the medium to increase the CO 2 saturation rate in the medium. The principle of this method is to increase the gas-liquid mass transfer efficiency by increasing the contact time between the gas and the liquid through the porous structure of the filler. However, the external gas-liquid mixing device (that is, the hollow fiber membrane module) in the invention patent also needs to be equipped with a liquid pump to pump the culture medium into the reactor body, which increases the system complexity and additional energy consumption. Shi Yunhai et al. (Patent No. CN105985910) passed the spray of the algae into the external absorption tower of the reactor by atomization spray to make full contact with the CO 2 gas passing through the bottom of the tower to improve gas-liquid mass transfer. The algae liquid passing through the absorption tower contains a higher CO 2 concentration and is pumped back into the reactor body via a liquid pump. This method utilizes the principle of increasing the gas-liquid specific surface area to increase CO 2 mass transfer. However, the algae liquid is highly likely to cause cell damage through the spray atomization device, thereby affecting its growth. Compared with atomized algae liquid, a more reasonable and effective method for increasing the gas-liquid mass transfer specific surface area is atomizing bubbles, that is, microbubbles. At present, microbubbles are widely used in the water treatment industry, which can effectively improve the mass transfer of dissolved oxygen. However, its application in the microalgae cultivation neighborhood is less, even if the existing related patents are mainly used for microalgae harvesting, for example, Pan Kehou et al. (Patent No. CN105002086) continuously floats the algae cells in the running pool through microbubbles. . Using microbubbles as a carrier for CO 2 gas can greatly increase the utilization of CO 2 by microalgae to overcome the bottleneck of insufficient carbon supply. The Chengguang mold (patent number CN102978102A) uses an external microbubble generator to generate process water containing microbubbles, and supplies the process water to the photobioreactor for culturing the microalgae. Yang Weimin et al. (patent number CN106434326, etc.) cut the CO 2 bubbles in the gas-liquid two fluids into tiny bubbles by the high-speed axial rotation of the rotor screw pump, and then pass the microbubble containing microbubbles into the tubular photobioreaction. The microalgae are cultured in the device. In principle, both methods improve the biomass production of microalgae through the efficient gas-liquid mass transfer of microbubbles. However, the principle of microbubbles is to inject CO 2 gas into the spiral wound hose in the mixing chamber and soft. The water in the tube is mixed, and the CO 2 is dissolved in the liquid or retained in the form of tiny bubbles to form process water through a long residence time, and the process water is introduced into the culture system to provide the growth of the microalgae. The latter uses micro-bubble water to supply the culture system using the principle of mechanical shearing. However, the two only consider the mass transfer characteristics of the microbubbles, but ignore the advantages of the microbubble high-efficiency momentum conduction. They all adopt the method of external microbubble generator to make microbubble water. Therefore, it is necessary to use an additional liquid pump for photobioreaction. The body of the device supplies microbubble water and enhances liquid circulation. In addition, the size of the microbubbles generated by the two is uncontrollable, and there may be a problem of excess supply or insufficient supply for the carbon demand of different economic microalgae. At the same time, the generation of microbubble water is accompanied by large energy consumption and more complicated microbubble production process. In the industrialized expansion application, there may be problems of excessive maintenance cost, energy consumption cost, and construction cost.
综上,近年来国内外已经对经济微藻的培养工艺进行了大量的研究,但上述技术瓶颈仍未得到有效的解决,大部分研究依然停留在实验室阶段,只有极个别公司和研究机构建立了工业化生产模式,不免形成了生产技术和产品价格上的垄断。因此如何突破这些技术瓶颈,实现经济微藻的高密度培养仍然是国内外微藻生物技术邻域研究的焦点。In summary, in recent years, a lot of research has been done on the culture process of economic microalgae at home and abroad, but the above technical bottlenecks have not been effectively solved. Most of the research is still in the laboratory stage, and only a few companies and research institutions have established The industrial production mode has inevitably formed a monopoly on production technology and product prices. Therefore, how to break through these technical bottlenecks and achieve high-density culture of economic microalgae is still the focus of research on microalgae biotechnology neighborhood at home and abroad.
发明内容Summary of the invention
针对上述问题,本发明的目的是提供一种用于经济微藻培养的微泡光生物反应器(MPBR),其能够一站式解决传统培养所面临的主要技术瓶颈,激发微藻生长潜能,提高经济微藻生物质产量,适用于实验室及规模化培养。In view of the above problems, an object of the present invention is to provide a microbubble photobioreactor (MPBR) for economical microalgae cultivation, which can solve the main technical bottleneck faced by traditional culture and stimulate the growth potential of microalgae in one stop. Improve the economic microalgae biomass production, suitable for laboratory and large-scale cultivation.
为实现上述目的,本发明采取以下技术方案:一种用于经济微藻培养的微泡光生物反应器,其特征在于:其包括具有预定容积的光生物反应器主体、可控粒径微泡发生装置、导流装置、以及LED波频双变光照系统;所述可控粒径微泡发生装置设置在所述光生物反应器主体底部,用于提供经济微藻培养所需的碳传质和循环动力,同时解析溶氧;所述导流装置悬挂设置在所述光生物反应器主体内部,用于促进液体循环及微泡传质;所述LED波频双变光照系统设置在所述光生物反应器主体外侧或内部,用于根据特定经济微藻需求提供其生长最优波长及光暗频率。In order to achieve the above object, the present invention adopts the following technical solution: a microbubble photobioreactor for economical microalgae cultivation, characterized in that it comprises a photobioreactor body having a predetermined volume, and a controllable particle size microbubble a generating device, a flow guiding device, and an LED wave frequency double-change illumination system; the controllable particle size microbubble generating device is disposed at a bottom of the photobioreactor body for providing carbon mass transfer required for economical microalgae cultivation And circulating power, while dissolving dissolved oxygen; the flow guiding device is suspended inside the photobioreactor body for promoting liquid circulation and microbubble mass transfer; the LED wave frequency double variable illumination system is disposed in the The outside or inside of the photobioreactor body is used to provide its optimal growth wavelength and light-dark frequency according to the needs of specific economic microalgae.
所述光生物反应器主体为管状或板状结构,其顶部设置有带出气口的可拆卸反应器封盖,底部螺栓连接所述可控粒径微泡发生装置。The photobioreactor body has a tubular or plate-like structure, and a detachable reactor cover with an air outlet is disposed at a top thereof, and the bottom bolt is connected to the controllable particle size microbubble generating device.
所述光生物反应器主体底部设置为漏斗状,但不限于此。The bottom of the photobioreactor main body is provided in a funnel shape, but is not limited thereto.
所述可控粒径微泡发生装置包括可拆卸底座、微孔陶瓷膜片和环形固定片;所述可拆卸底座包括基板和设置在所述基板上的腔体,所述基板上设置有用于与所述光生物反应器主体底部侧壁螺栓连接的底座紧固螺纹,所述腔体上设置有用于与卸流阀门连接的卸流端螺纹;所述腔体上部中央设置有一圆锥形凹槽,所述圆锥形凹槽中部设置有贯穿所述腔体上、下两端的进气口,所述进气口下端与设置在所述基板中部的变径进气嘴相连,所述变径进气嘴的另一端依次通过进气阀门、进气管道与CO 2混合气相连;所述微孔陶瓷膜片通过所述环形固定片固定设置在所述圆锥体凹槽上,所述微孔陶瓷膜片下表面与所述圆锥体凹槽之间形成用于气体积累增压的弧形气腔,所述微孔陶瓷膜片的侧面与所述圆锥体凹槽之间预留有用于气体流通的间隙。 The controllable particle size microbubble generating device comprises a detachable base, a microporous ceramic membrane and an annular fixing piece; the detachable base comprises a substrate and a cavity disposed on the substrate, the substrate is provided with a base threadedly coupled to a bottom wall of the photobioreactor main body, the cavity being provided with a discharge end thread for connection with the discharge valve; a central portion of the upper portion of the cavity is provided with a conical groove An air inlet penetrating through the upper and lower ends of the cavity is disposed in a middle portion of the conical groove, and a lower end of the air inlet is connected to a variable diameter air inlet provided in a middle portion of the substrate, and the variable diameter is The other end of the gas nozzle is connected to the CO 2 mixed gas through the intake valve and the intake pipe in sequence; the microporous ceramic diaphragm is fixedly disposed on the cone groove through the annular fixing piece, the microporous ceramic An arcuate air cavity for gas accumulation pressurization is formed between the lower surface of the diaphragm and the cone groove, and a gas passage is reserved between a side surface of the microporous ceramic diaphragm and the cone groove Clearance.
所述微孔陶瓷膜片的上表面设置有多个用于气体流通的微孔,所述微孔陶瓷膜片内部设置有用于均匀分布入射气体的多条导流渠,各所述导流渠的入口位于所述微孔陶瓷膜片的侧面。The upper surface of the microporous ceramic membrane is provided with a plurality of micropores for gas circulation, and the microporous ceramic membrane is internally provided with a plurality of drainage channels for uniformly distributing incident gas, and each of the drainage channels The inlet is located on the side of the microporous ceramic membrane.
所述微孔陶瓷膜片上表面的微孔孔径为0.01~10微米。所述微孔陶瓷膜片侧面与所述圆锥体凹槽之间的间隙为1~2mm。The pore diameter of the upper surface of the microporous ceramic membrane is 0.01 to 10 μm. The gap between the side surface of the microporous ceramic membrane and the groove of the cone is 1 to 2 mm.
所述导流装置通过设置在其上、下两端的导流支点悬挂设置在所述光生物反应器主体腔体内部,且所述导流装置将所述光生物反应器主体腔体内部划分为上升区和下降区,所述上升区是指位于所述导流装置内部的所述光生物反应器主体腔体部分,所述下降区是指位于所述导流装置外部的所述光生物反应器主体腔体部分。The flow guiding device is suspended inside the photobioreactor main body by a guiding fulcrum disposed at upper and lower ends thereof, and the guiding device divides the interior of the photobioreactor main body into a rising zone and a descending zone, the rising zone refers to the photobioreactor body cavity portion located inside the flow guiding device, and the descending zone refers to the photobioreaction located outside the flow guiding device The body cavity portion.
当外置光照时,所述导流装置采用镜面反光材料制作,所述光反应器主体内壁采用透明有机玻璃材料;当采用内置光照时,所述导流装置采用透镜有机玻璃材料,所述所述光反应器主体内壁采用镜面反光材料。When the external illumination is used, the flow guiding device is made of a specular reflective material, and the inner wall of the photoreactor body is made of a transparent plexiglass material; when the built-in illumination is used, the flow guiding device adopts a lens plexiglass material, and the The inner wall of the photoreactor body is made of a mirror reflective material.
所述LED波频双变光照系统包括预设数量和比例的白、红、蓝三色LED灯珠、变频系统以及时间继电器;所述变频系统用于根据实际培养需求控制所述LED灯珠,实现白、红、蓝及任意两种或多种波长的组合光照,并对光照强度进行调节;所述时间继电器用于根据实际培养需求控制所述LED灯珠,实现光照时间及暗处理时间调节。The LED wave frequency double-variation illumination system comprises a preset number and proportion of white, red and blue LED lamp beads, a frequency conversion system and a time relay; the frequency conversion system is used for controlling the LED lamp bead according to actual cultivation requirements. Realizing white, red, blue and combined illumination of any two or more wavelengths, and adjusting the illumination intensity; the time relay is used to control the LED lamp bead according to actual cultivation requirements, and realize illumination time and dark processing time adjustment .
本发明由于采取以上技术方案,其具有以下优点:1、本发明在微泡光生物反应器本体底部设置可控粒径微泡发生装置,利用微泡的高效传质及动量传导能力,提供经济微藻快速生长所需碳源,同时带动藻细胞由上升区进入下降区循环接受光照,提高了光能利用率及光合效率,降低了工艺复杂性及维护成本、减少占地面积、一站式解决传统技术瓶颈。2、本发明由于可控粒径微泡发生装置中的微孔陶瓷膜片顶部设置微孔出气面,膜片内部设置有引流渠,使得产生的微泡分布均匀、通量大、气阻小、可调节大小、应用灵活。3、本发明由于微泡光生物反应器在使用时,无需通过额外pH监测及调控设备,通过一次性投加碳酸盐及持续微泡通气即可以精准控制微泡光生物反应器内部培养液pH在最适范围,降低了工艺复杂性及维护成本。本发明可以广泛应该于经济微藻培养中。The invention adopts the above technical solutions, and has the following advantages: 1. The invention provides a controllable particle size microbubble generating device at the bottom of the microbubble photobioreactor body, and utilizes the efficient mass transfer and momentum conduction capability of the microbubbles to provide economy. The microalgae rapidly grows the carbon source needed, and at the same time drives the algae cells to enter the descending zone to receive light, which improves the utilization rate of light energy and photosynthetic efficiency, reduces process complexity and maintenance cost, reduces floor space, and is one-stop. Solve the bottleneck of traditional technology. 2. The present invention provides a microporous gas outlet surface at the top of the microporous ceramic membrane in the controllable particle size microbubble generating device, and a drainage channel is arranged inside the membrane, so that the generated microbubbles are evenly distributed, the flux is large, and the gas resistance is small. It can be adjusted in size and flexible in application. 3. In the present invention, since the microbubble photobioreactor is used, it is possible to accurately control the internal culture solution of the microbubble photobioreactor by using a single dose of carbonate and continuous microbubble ventilation without using additional pH monitoring and regulating equipment. The pH is in the optimum range, reducing process complexity and maintenance costs. The present invention can be widely applied to economical microalgae cultivation.
图1(a)为本发明用于经济微藻培养的微泡光生物反应器结构示意图;1(a) is a schematic view showing the structure of a microbubble photobioreactor for economical microalgae cultivation according to the present invention;
图1(b)为本发明用于经济微藻培养的微泡光生物反应器的3D示意图;Figure 1 (b) is a 3D schematic view of a microbubble photobioreactor for economical microalgae cultivation of the present invention;
图2(a)为本发明微泡发生器的结构示意图;2(a) is a schematic structural view of a microbubble generator of the present invention;
图2(b)为本发明微泡发生器的3D示意图;Figure 2 (b) is a 3D schematic view of the microbubble generator of the present invention;
图2(c)为本发明微泡发生器底座3D示意图;Figure 2 (c) is a schematic view of the microbubble generator base 3D of the present invention;
图3为使用微泡光生物反应器培养经济微藻示意图;Figure 3 is a schematic view showing the cultivation of economic microalgae using a microbubble photobioreactor;
图4(a)为本发明的微泡光生物反应器多个单元环型联立结构示意图;4(a) is a schematic view showing a plurality of unit ring-type joint structures of a microbubble photobioreactor according to the present invention;
图4(b)为本发明的微泡光生物反应器多个单元线型联立结构示意图;4(b) is a schematic view showing a plurality of unit line type joint structures of the microbubble photobioreactor of the present invention;
图5(a)为本发明不同孔径微孔陶瓷膜片产生微气泡粒径分布图;Figure 5 (a) is a diagram showing the particle size distribution of microbubbles generated by different pore microporous ceramic membranes of the present invention;
图5(b)为本发明不同条件下微泡光生物反应器传质系数测试结果;Figure 5 (b) is a test result of the mass transfer coefficient of the microbubble photobioreactor under different conditions of the present invention;
附图中涉及的附图标记如下所示:1、微泡光生物反应器(MPBR);2、可控粒径微泡发生器;3、内置导流筒;4、导流装置支点;5、光生物反应器主体;6、反应器封盖;7、LED波频双变光照系统;8、卸流阀门;9、进气阀门;10、微孔陶瓷膜片;11、导流渠;12、环形固定片;13、底座;14、底座紧固螺纹;15、卸流端螺纹;16、弧形气腔;17、环形固定片第一紧固螺母;18、环形固定片第二紧固螺母;19、变径进气嘴;20、微泡光生物反应器支架;21、固定卡箍;22、固定底托;23、进气管道;24、藻液;25、CO 2混合气;26、出气口。 The reference numerals referred to in the drawings are as follows: 1. Microbubble photobioreactor (MPBR); 2. Controllable particle size microbubble generator; 3. Built-in diversion tube; 4. Guide device fulcrum; , photobioreactor main body; 6, reactor cover; 7, LED wave frequency double variable illumination system; 8, unloading valve; 9, intake valve; 10, microporous ceramic diaphragm; 11, diversion channel; 12, annular fixed piece; 13, base; 14, base fastening thread; 15, unloading end thread; 16, curved air cavity; 17, annular fixing piece first fastening nut; 18, annular fixing piece second tight Solid nut; 19, variable diameter air inlet; 20, microbubble photobioreactor bracket; 21, fixed clamp; 22, fixed bottom; 23, intake pipe; 24, algae liquid; 25, CO 2 mixture ; 26, air outlet.
下面结合附图和实施例对本发明进行详细的描述。The invention will now be described in detail in conjunction with the drawings and embodiments.
如图1(a)、图1(b)所示,本发明提供的一种用于经济微藻培养的微泡光生物反应器,包括:微泡光生物反应器1,该微泡光生物反应器1包括具有预定容积的光生物反应器主体5、可控粒径微泡发生装置2、导流装置3、以及LED波频双变光照系统7。其中,可控粒径微泡发生装置2设置在光生物反应器主体5底部,用于提供经济微藻培养所需的碳传质和循环动力,同时解析溶氧;导流装置3悬挂设置在光生物反应器主体5内部,用于促进液体循环及微泡传质并可以根据实际需求调节悬置高度;LED波频双变光照系统7设置在光生物反应器主体5外侧或内部,用于根据特定经济微藻需求提供其生长最优波长及光暗频率。As shown in FIG. 1(a) and FIG. 1(b), the present invention provides a microbubble photobioreactor for economical microalgae cultivation, comprising: a
光生物反应器主体5为管状或板状结构,其顶部设置有带出气口26的可拆卸反应器封盖6,底部螺栓连接可控粒径微泡发生装置2。The
如图2(a)~图2(c)所示,可控粒径微泡发生装置2包括可拆卸底座13、微孔陶瓷膜片10和环形固定片12。其中,可拆卸底座13包括基板和设置在基板上的腔体,基板上设置有用于与光生物反应器主体5底部侧壁螺栓连接的底座紧固螺纹14,腔体上设置有用于连接卸流阀门8的卸流端螺纹15;腔体上部中央设置有一圆锥形凹槽,该圆锥形凹槽中部设置有贯穿腔体上、下两端的进气口,该进气口下端与设置在基板中部的变径进气嘴19相连,变径进气嘴19的另一端依次通过进气阀门9、进气管道23与CO
2混合气25相连;微孔陶瓷膜片10通过环形固定片12固定设置在可拆卸底座13的上表面,且微孔陶瓷膜片10下表面与可拆卸底座13的圆锥体凹槽之间形成用于气体积累增压的弧形气腔16,微孔陶瓷膜片10的侧面与圆锥体凹槽之间预留有用于气体流通的1~2mm的间隙。
As shown in FIGS. 2(a) to 2(c), the controllable particle size
微孔陶瓷膜片10的上表面设置有多个用于气体流通的微孔,微孔的孔径为0.01~10微米;微孔陶瓷膜片10内部设置有多条导流渠11,各导流渠11的入口位于微孔陶瓷膜片10的侧面,用于分布入射气体,防止在微孔出气表面某一区域发生微气泡堆积 合并,保证微气泡的均匀分布。The upper surface of the microporous
导流装置3通过设置在其上、下两端的导流装置支点4悬挂设置在光生物反应器主体5腔体内部,导流装置3将光生物反应器主体5腔体内部划分为上升区和下降区,上升区是指位于导流装置3内部的光生物反应器主体5腔体部分,下降区是指位于导流装置3外部的光生物反应器主体5腔体部分。其中,导流装置3根据光生物反应器主体5的结构可以采用空心导流筒或导流挡板,当光生物反应器主体5为管状结构时,则采用空心导流筒,当光生物反应器主体5为板状结构时,则采用导流挡板。另外,导流装置3可以根据实际培养需要进行更换、位置调整、清洗等。The
LED波频双变光照系统7包括预设数量和比例的白、红、蓝三色LED灯珠、变频系统以及时间继电器。变频系统用于根据实际培养需求实现白、红、蓝及任意两种或多种波长的组合光照,并对光照强度进行调节;时间继电器用于根据实际培养需求,实现光照时间及暗处理时间调节,实现“光闪效应”,提高光合效率。The LED wave frequency double-
作为一个优选的实施例,光生物反应器主体5底部可以设置为漏斗状,用于减少结构死角带来的细胞沉降堆积,同时促进流体循环。可以理解的是,光生物反应器主体5可以采用其他能够有效减少结构死角的结构。As a preferred embodiment, the bottom of the
作为一个优选的实施例,光生物反应器主体5采用较高高径比,用于增加气相在光生物反应器主体5中的停留时间并减少占地面积。其中,光生物反应器主体5的高径比的具体数值可以根据具体培养规模及目标传质值决定。As a preferred embodiment, the
作为一个优选的实施例,可控粒径微泡发生装置2中,环形固定片12下表面设置有一用于放置0形橡胶圈的凹槽,且该环形固定片12通过环形固定片第一、第二紧固螺母17、18实现点压式密封。As a preferred embodiment, in the controllable particle size
作为一个优选的实施例,在实际应用中,考虑到工程操作的便利,可控粒径微泡发生装置2可以采用一体式设计,其中,微孔陶瓷膜片10、微泡发生器底座13及环形固定片12通过强力胶水或其他方式粘合,制成具有固定孔径的微泡发生器,并直接通过更换不同孔径的微泡发生器来获得目标微泡粒径。As a preferred embodiment, in practical applications, the controllable particle size
作为一个优选的实施例,当采用外置光照时,导流装置3采用可以增加光反射提高光能利用率的镜面反光材料,光生物反应器主体5采用透明有机玻璃材料制作,当采用内置光照时,导流装置3采用透明有机玻璃材料制作,光生物反应器主体5采用镜面反光材料制作。As a preferred embodiment, when external illumination is used, the
作为一个优选的实施例,当导流装置3采用空心导流筒时,其内径与光生物反应器主体5腔体内径的比例关系根据实际培养规模确定,以增大光生物反应器主体5内部液体在上升区及下降区的流速,并减少停留时间。As a preferred embodiment, when the
作为一个优选的实施例,本发明用于经济微藻培养的微泡光生物反应器还包括一 微泡光生物反应器支架20,该微泡光生物反应器支架20为长方体框架,该长方体框架底部一边上设置有固定底托22,用于固定光生物反应器主体5底部,长方体框架上部一边上设置有固定卡箍21,用于固定光生物反应器主体5上部,长方体框架的各侧边用于固定LED波频双变光照系统7中的三色LED灯珠。As a preferred embodiment, the microbubble photobioreactor for economical microalgae cultivation of the present invention further comprises a
下面对本发明用于经济微藻培养的微泡光生物反应器的使用方法,做进一步介绍,具体包括以下步骤:The method for using the microbubble photobioreactor for economical microalgae cultivation of the present invention is further described below, and specifically includes the following steps:
如图3所示,使用微泡光生物反应器1进行单个单元培养经济微藻时,将微泡光生物反应器1置放于微泡光生物反应器支架20中,通过固定底托22和固定卡箍21将其固定。将光照系统中的LED波频双变生长灯珠放置于微泡光生物反应器1四周,或者固定于反应器支架20上。培养过程中,CO
2混合气25由高压气瓶提供,并通过进气管道23进入可控粒径微泡发生装置2。CO
2混合气通过变径气嘴19进入弧形气腔16积累增压,并从微孔陶瓷膜片10侧面进入内部导流渠11,在微孔陶瓷膜片10的微孔出气表面上产生均匀分布的微气泡。经可控粒径微泡发生装置2喷出的微气泡进入光生物反应器主体5内,在外置光照情况下,导流装置3的内部为暗区,外部为光区,暗区内,微泡上升带动液体上升,基于流体连续性,上升的液体在光区下降,从而实现液体在暗区和光区间的交替循环流动(如图1(a)中箭头所示)。考虑到微泡较高的气滞率,光生物反应器主体5内藻液24的液面与反应器封盖6预留一定空间,防止液面溢流,尾气通过出气口26排出。
As shown in FIG. 3, when the
如图4(a)和图4(b)所示,在实际工业化扩大培养过程中,还可以对多个反应器单元进行环形或者线形串联,达到规模化培养体积要求。相比单个反应器单元放大,多个反应器单元联立运行具有更好的可控性和灵活性,同时便于维修。As shown in Fig. 4(a) and Fig. 4(b), in the actual industrialized expansion culture process, a plurality of reactor units can also be connected in a circular or linear shape to achieve a large-scale culture volume requirement. Compared to single reactor unit amplification, multiple reactor units operate in parallel with better controllability and flexibility while facilitating maintenance.
实施例一:Embodiment 1:
如图5(a)和图5(b)所示,本实施例中,采用4种不同孔径微孔陶瓷膜片构成微泡光生物反应器,对微泡光生物反应器的粒径分布及传质性能进行测试。As shown in FIG. 5(a) and FIG. 5(b), in the present embodiment, four kinds of microporous ceramic membranes with different pore diameters are used to form a microbubble photobioreactor, and the particle size distribution of the microbubble photobioreactor is as follows. Mass transfer performance was tested.
[根据细则26改正05.06.2018]
如图5(a)所示,为微泡光生物反应器微泡粒径分布结果。在500ml培养液中,以50mlmin -1流速通入1%浓度的CO 2混合气体至由4种不同孔径微孔陶瓷膜片(种类1、种类2、种类3、种类4)构成的微泡发生器中,所产生的微气泡平均粒径d 32分别为554μm、464μm、333μm及115μm。其中种类1陶瓷膜片所产生的微泡较大,约30%的微泡其粒径为400-500um,可用于大多数经济微藻的培养前期或实验室藻种预培养。在由种类2和种类3陶瓷膜片所产生的微泡中,粒径100-200μm的微泡数量分别占约35%和65%,可用于经济微藻对数生长的前期或实验室藻种扩培。种类4陶瓷膜片所产生的微泡最小,约65%的微泡粒径小于100μm,其中25%的微泡粒径小于50μm,可以用于经济微藻对数生长的中后期或规模化高密度培养。[Correct according to
As shown in Fig. 5(a), it is the result of microbubble particle size distribution of the microbubble photobioreactor. In a 500 ml culture solution, a 1% CO 2 mixed gas was introduced at a flow rate of 50 ml min −1 to generate microbubbles composed of four different pore size microporous ceramic membranes (
如图5(b)所示,对这四种由不同孔径微孔陶瓷膜片所构成的微泡发生器在不同气通量及不同反应器高径比条件下进行传质性能测试。总体上,对于同种类型微孔陶瓷膜片,传质系数K La随着气通量或者高径比的增加而增加;而对于同种气通量及高径比条件,传质系数K La随着微泡平均粒径的减小而增加。上述四种不同孔径微孔陶瓷膜片所构成的微泡发生器传质系数总体上可达0.0035min -1-1.92min -1,约为传统气泡(例如粒径3mm)传质性能的200–30000倍,可以满足不同经济微藻不同生长时期的碳需求。另一方面,结合上述微泡粒径和传质性能的测试结果及理论推导,本发明提供了影响传质性能主要因素(气泡粒径、反应器高径比、气通量)与传质系数之间的数学模型,为微泡光生物反应器结构及操作参数的优选方法提供了理论依据。 As shown in Fig. 5(b), the mass transfer performance of the four microbubble generators composed of different pore microporous ceramic membranes under different gas fluxes and different reactor height to diameter ratios was tested. In general, for the same type of microporous ceramic membrane, the mass transfer coefficient K L a increases with the increase of gas flux or height to diameter ratio; for the same gas flux and high aspect ratio conditions, the mass transfer coefficient K L a increases as the average particle size of the microbubbles decreases. The mass transfer coefficient of the microbubble generator composed of the above four different pore microporous ceramic membranes can reach 0.0035min -1 -1.92min -1 , which is about 200 ~ of the mass transfer performance of traditional bubbles (for example, particle size 3mm). 30000 times, can meet the carbon demand of different economic microalgae in different growth periods. On the other hand, combined with the above test results and theoretical derivation of microbubble particle size and mass transfer performance, the present invention provides the main factors affecting mass transfer performance (bubble particle size, reactor height to diameter ratio, gas flux) and mass transfer coefficient. The mathematical model between them provides a theoretical basis for the preferred method of microbubble photobioreactor structure and operating parameters.
最后应说明的是:以上实施例仅用以说明本发明的技术方案,而非对其限制;尽管参照前述实施例对本发明进行了详细的说明,本领域的普通技术人员应当理解:其依然可以对前述各实施例所记载的技术方案进行修改,或者对其中部分技术特征进行等同替换,而这些修改或者替换,并不使相应技术方案的本质脱离本发明各实施例技术方案的范围。It should be noted that the above embodiments are only used to illustrate the technical solutions of the present invention, and are not limited thereto; although the present invention has been described in detail with reference to the foregoing embodiments, those skilled in the art should understand that The technical solutions described in the foregoing embodiments are modified, or some of the technical features are equivalently substituted, and the modifications or substitutions do not deviate from the scope of the technical solutions of the embodiments of the present invention.
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Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2023017478A1 (en) * | 2021-08-13 | 2023-02-16 | Botanico Design Ltd | System and method for cultivating and harvesting cyanobacterial biomass |
| CN120818640A (en) * | 2025-09-18 | 2025-10-21 | 爱尔发生物科技(嘉兴)有限公司 | Intelligent coordinated control method and system for dissolved oxygen in Haematococcus culture solution |
Families Citing this family (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| IT201900002641A1 (en) * | 2019-02-25 | 2020-08-25 | Milano Politecnico | Modular kit for integration and installation of one or more bioreactors for the cultivation of microalgae |
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| CN110938533B (en) * | 2019-11-15 | 2022-12-09 | 河海大学 | Bioreactor for microalgae facultative growth mode culture and working method thereof |
| CN111979097A (en) * | 2020-09-04 | 2020-11-24 | 清华大学 | A photobioreactor for microalgae cultivation |
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| CN118772987B (en) * | 2024-09-11 | 2025-01-24 | 青岛科技大学 | A photobioreactor for culturing microalgae and a control method thereof |
| CN119193302A (en) * | 2024-09-29 | 2024-12-27 | 深圳理工大学 | Photobioreactor and photobioreactor aeration method |
Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102443536A (en) * | 2010-10-09 | 2012-05-09 | 新奥科技发展有限公司 | Auxiliary device for photobioreactor |
| CN103374511A (en) * | 2012-04-12 | 2013-10-30 | 中国科学院过程工程研究所 | Air-lift-type circulation photobioreactor |
| US20140356931A1 (en) * | 2013-05-29 | 2014-12-04 | Centre De Recherche Industrielle Du Quebec | Method and system for the culture of microalgae |
| CN105087371A (en) * | 2014-05-04 | 2015-11-25 | 北京工商大学 | Photobioreactor for automatically culturing microalgae |
| CN105219635A (en) * | 2015-09-16 | 2016-01-06 | 浙江大学舟山海洋研究中心 | A kind of built-in light source air lift type inner ring stream photosynthesis physiological target |
| CN205398612U (en) * | 2016-03-21 | 2016-07-27 | 山东大学 | Improve photobioreactor of little algae growth rate |
| CN108395993A (en) * | 2018-02-28 | 2018-08-14 | 清华大学深圳研究生院 | A kind of application method of microvesicle bioreactor for economic microdisk electrode |
Family Cites Families (13)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO1984001992A1 (en) * | 1982-11-11 | 1984-05-24 | Morgan Thermic Ltd | Gas burner |
| DE9302862U1 (en) * | 1993-02-26 | 1993-05-27 | Anton Steinecker Entwicklungs GmbH & Co, 8050 Freising | Aeration nozzle for aerating liquids containing organic substances |
| CN201125191Y (en) * | 2007-11-06 | 2008-10-01 | 宁波德安生态环保工程有限公司 | an aerator |
| CN201525848U (en) * | 2009-09-22 | 2010-07-14 | 梅州市杉维生物医药工程研究有限公司 | Reactor for nursing plant cells of Chinese yew |
| CN102061251A (en) * | 2010-11-26 | 2011-05-18 | 福州骏洋生物科技有限公司 | Novel optical bioreactor |
| CN202038913U (en) * | 2011-02-28 | 2011-11-16 | 南京国能环保工程有限公司 | Variable-diameter efficient aeration device |
| CN102513040B (en) * | 2011-12-29 | 2014-04-23 | 江苏久吾高科技股份有限公司 | Ceramic Membrane Microporous Gas Distributor |
| CN203429170U (en) * | 2013-06-16 | 2014-02-12 | 浙江长城减速机有限公司 | Gas separator for mechanical agitation tank |
| CN203715619U (en) * | 2014-02-25 | 2014-07-16 | 中国科学院水生生物研究所 | Cylindrical air-lift type efficient photobioreactor for microalgae cultivation |
| CN103966086A (en) * | 2014-04-25 | 2014-08-06 | 上海海洋大学 | Internal and external hierarchically-adjusted and controlled light source system capable of adjusting and controlling light intensity and adjusting light color |
| DE102015113691A1 (en) * | 2015-08-18 | 2017-02-23 | Martin Stachowske | Begaservorrichtung |
| CN205892894U (en) * | 2016-08-19 | 2017-01-18 | 四川四通欧美环境工程有限公司 | Modular microporous aerator |
| CN106582460B (en) * | 2017-01-20 | 2023-01-03 | 南京工业大学 | Airlift type external circulation reactor device and process |
-
2018
- 2018-02-28 CN CN201810168434.0A patent/CN108359580B/en active Active
- 2018-02-28 CN CN202010195067.0A patent/CN111411033B/en active Active
- 2018-04-19 WO PCT/CN2018/083710 patent/WO2019165689A1/en not_active Ceased
Patent Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102443536A (en) * | 2010-10-09 | 2012-05-09 | 新奥科技发展有限公司 | Auxiliary device for photobioreactor |
| CN103374511A (en) * | 2012-04-12 | 2013-10-30 | 中国科学院过程工程研究所 | Air-lift-type circulation photobioreactor |
| US20140356931A1 (en) * | 2013-05-29 | 2014-12-04 | Centre De Recherche Industrielle Du Quebec | Method and system for the culture of microalgae |
| CN105087371A (en) * | 2014-05-04 | 2015-11-25 | 北京工商大学 | Photobioreactor for automatically culturing microalgae |
| CN105219635A (en) * | 2015-09-16 | 2016-01-06 | 浙江大学舟山海洋研究中心 | A kind of built-in light source air lift type inner ring stream photosynthesis physiological target |
| CN205398612U (en) * | 2016-03-21 | 2016-07-27 | 山东大学 | Improve photobioreactor of little algae growth rate |
| CN108395993A (en) * | 2018-02-28 | 2018-08-14 | 清华大学深圳研究生院 | A kind of application method of microvesicle bioreactor for economic microdisk electrode |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2023017478A1 (en) * | 2021-08-13 | 2023-02-16 | Botanico Design Ltd | System and method for cultivating and harvesting cyanobacterial biomass |
| CN120818640A (en) * | 2025-09-18 | 2025-10-21 | 爱尔发生物科技(嘉兴)有限公司 | Intelligent coordinated control method and system for dissolved oxygen in Haematococcus culture solution |
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