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WO2003006629A1 - Culturing method and device for photosynthetic microbes - Google Patents

Culturing method and device for photosynthetic microbes Download PDF

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Publication number
WO2003006629A1
WO2003006629A1 PCT/JP2002/007043 JP0207043W WO03006629A1 WO 2003006629 A1 WO2003006629 A1 WO 2003006629A1 JP 0207043 W JP0207043 W JP 0207043W WO 03006629 A1 WO03006629 A1 WO 03006629A1
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WO
WIPO (PCT)
Prior art keywords
aeration tank
suspension
liquid
photosynthetic
photosynthetic microorganisms
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.)
Ceased
Application number
PCT/JP2002/007043
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French (fr)
Japanese (ja)
Inventor
Toshirou Sekine
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Individual
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Individual
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Filing date
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Priority to JP2003512388A priority Critical patent/JP4038772B2/en
Publication of WO2003006629A1 publication Critical patent/WO2003006629A1/en
Anticipated expiration legal-status Critical
Ceased legal-status Critical Current

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Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • C02F3/348Biological treatment of water, waste water, or sewage characterised by the microorganisms used characterised by the way or the form in which the microorganisms are added or dosed
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12MAPPARATUS 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
    • C12M21/00Bioreactors or fermenters specially adapted for specific uses
    • C12M21/02Photobioreactors
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12MAPPARATUS 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
    • C12M23/00Constructional details, e.g. recesses, hinges
    • C12M23/02Form or structure of the vessel
    • C12M23/18Open ponds; Greenhouse type or underground installations
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12MAPPARATUS 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
    • C12M29/00Means for introduction, extraction or recirculation of materials, e.g. pumps
    • C12M29/06Nozzles; Sprayers; Spargers; Diffusers
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

Definitions

  • the present invention relates to a method and an apparatus for culturing photosynthetic microorganisms such as pearl oysters and photosynthetic bacteria.
  • the present invention can be used for purification of organic wastewater in addition to the production of algal cells described above.
  • photosynthetic microorganisms are cultivated on a large scale, such as edible cucumber cultivation ponds using acetic acid / glucose as a carbon source and high-rate oxidation ponds for organic sewage purification, as seen in microalgae cultivation. It is carried out in a shallow and wide flat pond p with a depth of about 2 Ocm, constructed outdoors. These are all open-top culture devices that receive sunlight directly on the water surface. For this reason,
  • Wastewater treatment requires a certain level of capacity every day.
  • photosynthetic microorganisms with sunlight their growth depends greatly on weather conditions such as solar radiation and temperature. Since the growth of photosynthetic microorganisms decreases most in winter, the scale of culture is set based on this winter growth. For this reason, a vast area of the site is still needed.
  • the present invention provides a method and an apparatus for culturing photosynthetic microorganisms, which can prevent the suspension from cooling in a cold region and can provide a certain excellent culturing result without being influenced by the weather conditions such as sunshine. It is intended to provide.
  • Photosynthetic microorganisms such as microalgae, red sulfur-free bacteria,
  • the photosynthetic microorganisms are suspended in a liquid in which organic matter is dissolved.
  • the suspension s of the photosynthetic microorganisms is irradiated with sunlight in a shallow flat pond p slightly open to the gas-liquid contact surface opened to the atmosphere.
  • the suspension s is transferred to a deep aeration tank a with a small gas-liquid contact area, and the suspension s in the aeration tank a is aerated with oxygen-containing gas such as air.
  • a method for culturing a photosynthetic microorganism which comprises culturing the photosynthetic microorganism
  • the photosynthetic microorganisms are suspended in a solution in which organic matter is dissolved.
  • the suspension S of the photosynthetic microorganisms is irradiated with sunlight in a shallow ⁇ -plane pond p, which has a large gas-liquid contact area opened to the atmosphere.
  • the suspension s is transferred to a deep aeration tank a with a small gas-liquid contact area, and the suspension s in the aeration tank a is aerated with oxygen-containing gas such as air.
  • the suspension s is transferred to the deep aeration tank a with a small gas-liquid contact area, the suspension s in the aeration tank a is aerated with oxygen-containing gas such as air, and flows into the flat pond p.
  • oxygen-containing gas such as air
  • the method of growing photosynthetic microorganisms such as microalgae and photosynthetic bacteria
  • the photosynthetic microorganisms are suspended in the liquid in which the organic matter is dissolved.
  • the suspension S of the photosynthetic microorganisms is placed in the shallow flat pond P, which is open to the atmosphere and has a large gas-liquid contact area. Irradiate light,
  • the suspension S is transferred to a deep aeration tank with a small gas-liquid contact area, and the suspension s in the aeration tank is aerated with oxygen-containing gas such as air, and the aeration is stopped and suspended. With a period to make the suspension s anaerobic,
  • a method for culturing a photosynthetic microorganism which comprises culturing the photosynthetic microorganism
  • the photosynthetic microorganisms are suspended in a liquid in which organic matter is dissolved.
  • the suspension s of the photosynthetic microorganisms is irradiated with sunlight in a shallow flat pond p having a large gas-liquid contact area opened to the atmosphere,
  • the suspension s is transferred to a deep aeration tank with a small gas-liquid contact area, and the suspension s in the aeration tank is aerated with air, and the aeration is stopped and the anaerobic state is stopped.
  • the suspension s In the daytime, during rainfall, the suspension s is transferred to the aeration tank, and the suspension s in the aeration tank ⁇ is aerated with oxygen-containing gas such as air to culture photosynthetic microorganisms.
  • P is a method for cultivating photosynthetic microorganisms, which is characterized by culturing the photosynthetic microorganisms to the outside,
  • a deep aeration tank having a small gas-liquid contact area which is filled with a liquid containing the photosynthetic microorganisms, aerated with an oxygen-containing gas, and provided with an aerator for growing the photosynthetic microorganisms.
  • a liquid transfer mechanism m for transferring liquid between the flat pond p and the aeration tank a.
  • a culture device for photosynthetic microorganisms comprising:
  • a deep aeration tank with a floating lid b2 which is filled with a liquid containing the photosynthetic microorganisms, and is provided with an aerator for aerating an oxygen-containing gas to grow the photosynthetic microorganisms and a floating body covering the liquid surface.
  • An apparatus for culturing photosynthetic microorganisms comprising: As described above, the present invention allows daytime breeding using solar energy to be performed in a shallow flat pond p, and breeding using energy by nighttime oxygen respiration without sunlight in a deep aeration tank with high oxygen dissolving efficiency. This is a method and an apparatus for forming a field suitable for each metabolism.
  • FIG. 1 is a plan view showing one embodiment of the present invention.
  • Fig. 2 is a vertical cross-sectional view taken along the line A-A in Fig. 1, showing the state during daytime operation. ing.
  • FIG. 3 is a vertical cross-sectional view taken along the line AA in FIG. 1 and shows a state during nighttime aeration.
  • FIG. 4 is a plan view showing another embodiment of the present invention.
  • FIG. 5 is a vertical cross-sectional view taken along line BB in FIG. 4, and shows a state during daytime operation.
  • FIG. 6 is a vertical cross-sectional view taken along the line BB in FIG. 4, and shows a state during the night aeration operation.
  • FIG. 7 is a vertical cross-sectional view taken along the line BB in FIG. 4, and shows a state in which night aeration is stopped.
  • FIG. 8 is a plan view showing an embodiment of the plane pond p.
  • FIG. 9 is a plan view showing an embodiment of the plane pond p.
  • FIG. 10 is a plan view showing an embodiment of the plane pond p.
  • FIG. 11 is a longitudinal sectional view showing another embodiment, which corresponds to FIG. 5 of the embodiment shown in FIGS. 4 to 7 and shows a state during operation in the daytime.
  • FIG. 12 is a vertical cross-sectional view of the same device as FIG. 11, and corresponds to FIG. 6, and shows a state during night aeration.
  • FIG. 13 is a longitudinal sectional view of the same device as FIG. 11, and corresponds to FIG. 7, and shows a state in which night aeration is stopped.
  • FIG. 14 is a plan view showing another embodiment.
  • Fig. 15 is a vertical sectional view taken along the line DD in Fig. 14, showing the state during daytime operation.
  • FIG. 16 is a vertical cross-sectional view taken along the line DD in FIG. 14, and shows a state during operation in the daytime.
  • FIG. 17 is a plan view showing another embodiment.
  • FIG. 18 is a longitudinal sectional view taken along the line E--E in FIG. 17, and shows a state during operation in the daytime.
  • FIG. 19 is a longitudinal sectional view taken along the line EE in FIG. 17 and shows a state during daytime operation.
  • FIG. 20 is a plan view showing another embodiment. Corresponds to Figure 14.
  • FIG. 21 is a plan view showing another embodiment. Corresponds to FIG.
  • FIG. 22 is a plan view showing another embodiment.
  • FIG. 23 is a vertical sectional view of F—: F in FIG. 22, showing a state during daytime operation.
  • FIG. 24 is a cross-sectional view taken along the line HH in FIG. 23, and shows a state during daytime operation.
  • Fig. 25 is a vertical sectional view taken along the line GG in Fig. 22, showing the state during daytime operation.
  • FIG. 26 is a vertical sectional view taken along the line II in FIG. 22, and shows a state during nighttime aeration.
  • FIG. 27 is a plan view showing one embodiment of the present invention.
  • FIG. 28 is a vertical sectional view taken along the line JJ in FIG. 27, and shows a state during operation during daytime.
  • Fig. 29 is a vertical sectional view taken along the line JJ in Fig. 27, showing the state during the night aeration operation.
  • a is an aeration tank
  • p is a flat pond
  • bl is a closed aeration tank in the capital
  • b 2 is an aeration tank with a floating lid
  • e is a residual liquid discharge pipe
  • f is a rainwater discharge pipe
  • 3 ⁇ 4 is a bubble
  • k is an air layer
  • m Is a liquid transfer mechanism
  • s is a suspension
  • t is a liquid level
  • 2 is a valve
  • 3 is a diffuser
  • 4 is a flow control valve
  • is a blower
  • 6 is a pump
  • 7 is a valve
  • 8 is a pipe
  • 9 Is a pipe
  • 11 is a valve
  • 13 is a valve
  • 14 is a pipe
  • 15 is a valve
  • 16 is a stirring rotor
  • 17 is a rectifying wall
  • 18 is a pipe
  • 19 is a pump
  • 20 is a stirring device
  • 21 is a bogie
  • 22 is a center rotating part
  • 24 is a water pipe
  • 25 is a water pipe.
  • a diffuser, 27 is a return pipe
  • 28 is a rectifying wall
  • 29 is a spout water pipe
  • 30 is a suction water pipe
  • 31 is a suction water pipe
  • 33 is a rectifying wall
  • 37 is a rectifying wall
  • 38 is a floating body
  • 39 is the support
  • Dashed arrows indicate the flow direction of the suspension.
  • Examples and actions 1 to 3 are views showing an embodiment of the present invention.
  • Fig. 1 is a plan view
  • Fig. 2 is an A-A longitudinal section during daytime operation
  • Fig. 3 is an A-A longitudinal section during night operation.
  • This embodiment is particularly useful for cultures that do not require the suppression of the growth of predators, ie, culture of photosynthetic bacteria under conditions of high organic matter, batch culture of microalga such as chlorella (harvested before the occurrence of insects), insecticides This shows the case of ⁇ such as addition culture.
  • the system consists of a shallow flat pond p that receives sunlight and a deep aeration tank a with a small gas-liquid contact area.
  • a diffuser 3 is provided at the bottom of the aeration tank a.
  • Pump 6 and pipe 8 for sending a liquid in which photosynthetic microorganisms are suspended in a nutrient solution containing organic matter (hereinafter referred to as suspension S ) from aeration tank a to plane pond p, and from plane pond p to aeration tank a
  • the liquid transfer mechanism m is constituted by the tube 9 for sending the suspension s.
  • Plane pond The bottom of p is set low toward the pipe 9 installation site. Near the pipe 9, a residual liquid discharge pipe e and a rainwater discharge pipe f are provided.
  • the valve 7 is opened, and the suspension s flows down to the aeration tank a via the pipe 9.
  • flow into the suspension s filled in the a. Air is supplied through control valve 4, pipe 10, and diffuser 3 (g indicates air bubbles), and oxygen is supplied. Photosynthetic microorganisms use this oxygen to breathe It decomposes, degrades, and proliferates organic matter.
  • the rainwater flowing into the flat pond P is opened to the drainage channel (not shown) via the rainwater discharge pipe f by opening the valve 11.
  • the water depth of the flat pond p is appropriate to be less than 20 cm to preferentially grow photosynthetic microorganisms. At depths above 20 cm, the depth of the photosynthetic microorganisms decreases, making it difficult to grow preferentially.
  • the flat pond p At night or during rainfall, it is possible to ventilate the flat pond p and supply oxygen to allow photosynthetic microorganisms to grow by respiratory metabolism as described above.However, since the flat pond P is shallow, oxygen supply per unit power Performance is extremely low and is not practically feasible in terms of cost.
  • the oxygen supply capacity per unit power is high and the suspension s can be practically implemented.
  • an oxygen dissolution efficiency of 6-8% can be obtained at an aeration water depth of 3-4m.
  • the water depth of the aeration tank a of the present invention may be set to 2.5-4 m.
  • FIG. 4 to 7 show another embodiment of the present invention (a side view.
  • FIG. 4 is a plan view
  • FIG. 5 is a vertical sectional view taken along the line BB during daytime operation
  • FIG. Fig. 7 is a vertical sectional view taken along the line B-B while the aeration is stopped during night operation
  • This embodiment is particularly applicable to cultures that require suppression of the growth of predators, that is, insecticides.
  • This device shows the case of continuous cultivation of photosynthetic microorganisms with no addition.
  • This equipment has a point that the aeration tank is configured as an upper closed aeration tank bl, and is equipped with a pipe 14 for taking in and out air and a valve 15. This is similar to the device shown in FIGS.
  • the suspension In the daytime (Fig. 5), the suspension is a flat pond! ) And receive sunlight irradiation. The photosynthetic microorganisms in the liquid absorb light and use this energy to absorb and degrade organic matter and proliferate.
  • valves 7 and 15 are opened, The suspension flows down via pipe 9 into the upper closed aeration tank bl. Suspension s that fills upper closed aeration tank b 1 remains in flat pond p. In the residual liquid remaining in the flat pond p, the residual liquid is in contact with air, so that photosynthetic microorganisms such as insects can survive and grow.
  • the residual liquid is discharged as a harvest into a storage tank or the like (not shown) through the residual liquid discharge pipe e by opening the valve 2.
  • air is supplied to the suspension filled in the upper closed aeration tank bl through the flow control valve 4, the pipe 10, and the air diffuser 3 by the blower 5 to supply oxygen.
  • the photosynthetic microorganisms decompose, degrade, and multiply organic matter by respiration using this oxygen.
  • blower 5 is stopped, and valves 7, 13 and 15 are closed.
  • the oxygen in the upper closed aeration tank b is gradually consumed and becomes anaerobic. Under anaerobic conditions, predators such as worms gradually die.
  • the photosynthetic microorganism is alive for about 1 to 23 days.
  • ⁇ worms can be killed in half under anaerobic conditions in about 6 hours, and all in about 12 hours, and return to their original state when a half of them are aerated for 48 hours. It is appropriate to stop the aeration at night for 8 hours or more.
  • the bottom of the pond p is set low toward the pipe 9 installation site, and a residual liquid discharge pipe e is provided near the pipe 9. This is not an essential condition, and the p-bottom of the flat pond may be almost horizontal. If it is almost horizontal, the suspension s does not turn yellow and continuous culturing is not possible.
  • the aeration is stopped at night after the aeration, and then the anaerobic state is achieved.
  • the same effect can be obtained by performing the aeration after the order is reversed and the anaerobic state is maintained.
  • the flat pond p shown in Fig. 1 to Fig. 7 does not have a specific stirring mechanism, but the flow when the suspension s is moved daily to the aeration tank a or the upper closed aeration tank bl. Harvest can be almost prevented.
  • the mixing with the added nutrient solution is performed in the aeration tank a or the upper closed aeration tank b1, the concentration of nutrients in the flat pond P is also prevented from becoming uneven.
  • a stirrer is needed to speed up breeding.
  • FIGS. Each is a shallow flat pond with a depth of 10-40 cm.
  • a stirring rotor 16 for flowing the suspension s in the direction of the arrow is provided in one endless water channel defined by the rectifying wall 17, and a stirring mechanism is configured.
  • the flat pond p in Fig. 9 is obtained by sending the suspension s via the pipe 18 by the pump 19 from the downstream end to the upstream end of one waterway defined by the rectifying wall 17-.. H, The suspension s is caused to flow in the direction of the arrow to form a stirring mechanism.
  • FIG. 10 shows that a stirrer 20 with a brush is provided from the center rotating part 22 of the circular flat pond p to the bogie 21 on the upper end of the circumferential side wall, and the bogie 21 is moved in the direction of the arrow. And stir the pond.
  • the plane pond p having the stirring mechanism shown in FIGS. 8 to 10 can be used also in the present invention because of the power required to increase the operating cost of the facility by the amount of the stirring device.
  • FIGS. 11 to 13 show another embodiment, and correspond to the embodiments shown in FIGS. 4 to 7.
  • FIG. Fig. 11, which corresponds to Fig. 5, is a daytime crop.
  • FIG. 12 corresponding to FIG. 6 is a longitudinal sectional view during night aeration operation, and
  • FIG. 13 corresponding to FIG. 7 is a longitudinal sectional view during night aeration stop.
  • the difference from the embodiment shown in FIGS. 4 to 7 is that the pipe 9 opens at the bottom of the upper sealed aeration tank b1.
  • the pump is not required, and the suspension s can be easily moved by the on-off of the blower 5.
  • FIG. 14 to 16 are views showing still another embodiment.
  • FIG. 14 is a plan view
  • FIGS. 15 and 16 are vertical sectional views taken along the line DD during daytime operation.
  • the difference from the embodiment shown in FIGS. 1 to 13 is that the upper sealed aeration tank b1 is provided below the center of the flat pond p, and the bottom of the flat pond p and the bottom of the upper sealed aeration tank b1 are connected by the water pipe 24. Has been contacted.
  • air is sent from the air diffuser 25 through the pipe 10 by the blower 5 with the valve 15 closed and the valve 4 open. The suspension s is pushed out to the flat pond p via the conduit.
  • the liquid level t in the upper closed aeration tank b descends and reaches the lower end of the water pipe 24. Further, the liquid surface descends due to the surface tension of the water, and the air k eventually flows into the water conduit 24. Gushing. Then, the suspension s in the headrace channel 24 rises with the air k and jets into the flat pond P (FIG. 15). When the jetting ends, the suspension s in the flat pond p descends in the headrace 24 and flows into the upper closed aeration tank bl (Fig. 16). By this series of operations, a wave is generated in the plane pond p, and the suspension s is stirred.
  • the suspension s is irradiated with sunlight while being stirred, and the photosynthetic microorganisms proliferate.
  • the valve 15 is opened, and the turbid liquid s is allowed to flow down to the upper closed aeration tank bl via the water pipe 24.
  • the flow control valve 4 is opened, and air is supplied to the suspension s filled in the upper sealed aeration tank bl via the flow control valve 4, the pipe 10, and the air diffuser 25 by the blower 5. Ventilate and supply oxygen.
  • the photosynthetic microorganisms decompose, degrade, and grow organic matter by respiration using this oxygen.
  • the blower 5 is stopped, the flow control valve 4 and the valve 15 are closed, and the inside of the upper sealed aeration tank bl is made anaerobic.
  • the valve 4 is opened, the blower 5 is operated, and the suspension is sent to the flat pond p. Thereafter, the above steps are repeated for culturing. Other operations such as rain during the day are performed in the same manner as in the above embodiment.
  • the suspension can be easily moved by the on-off of the blower 5, and the suspension in the flat pond p can be easily stirred without newly installing a stirring device.
  • FIG. 17 to 19 are diagrams showing still another embodiment.
  • FIG. 17 is a plan view
  • FIG. 18 is a longitudinal sectional view of E-E during daytime operation
  • FIG. 19 is a longitudinal sectional view of E-E during daytime operation.
  • FIG. The difference from the embodiment shown in FIGS. 14 to 16 is that a return pipe 27 is provided to connect the end of the flat pond p and the bottom of the upper closed aeration tank bl.
  • the return pipe 27 is provided so as to open below the lower end of the water pipe 24 in the upper closed aeration tank bl. In this embodiment, when the air flows out of the water pipe 24 to the flat pond p (FIG.
  • FIG. 20 is a plan view corresponding to FIG. 14 of the embodiment shown in FIGS.
  • Plane pond p is composed of a long water channel and an upper closed aeration tank below its end.
  • b 1 is provided.
  • FIG. 21 is a plan view corresponding to FIG. 17 of the embodiment shown in FIGS.
  • the flat pond p is composed of a long waterway, and an upper closed aeration tank bl is provided below its end.
  • the return pipe 27 connects the end of the flat pond p and the bottom of the upper closed aeration tank b.
  • the shape of the flat pond p is not limited to the above embodiment, but may be determined in consideration of various conditions such as the shape of the site and the budget for the facility.
  • FIGS. 22 to 26 are views showing another embodiment of the present invention.
  • FIG. 22 is a plan view
  • FIG. 23 is a longitudinal sectional view taken along the line FF during daytime operation
  • FIG. G longitudinal section
  • Fig. 24 is H-H transverse section during daytime operation
  • Fig. 26 is I-I longitudinal section during night aeration.
  • This embodiment has the same function as the device shown in FIG.
  • the suspension s is configured to flow in the order of the water pipe 24 in the upper closed aeration tank b1, the channel-shaped flat pond p, the return pipe 27, and the upper closed aeration tank b. I have.
  • the flat pond p is divided by the rectifying wall 28, and the upstream end and the downstream end are configured as one adjacent water channel on the upper closed aeration tank b.
  • a water pipe 29, suction water pipes 30 and 31 are provided at the downstream end, and a suspension water pipe 29, a flat pond p, a suction water pipe 30 and 31 and an upper closed aeration tank bl in this order. It is configured to flow cyclically.
  • 37 is a rectifying wall. In FIG. 21, it is expensive to provide the return pipe 27 corresponding to the flow product of the channel-shaped flat pond P.
  • the flat pond p is divided by the rectifying wall 28, and the upstream end and the downstream end are formed as one adjacent water channel on the upper closed aeration tank b1, and the upstream end of the pond is used for jetting. Since the water supply pipe 29 and the suction water supply pipes 30 and 31 are provided at the downstream end, the cost is low, the flow in the flat pond P is good, and the mixing and stirring can be performed efficiently.
  • FIG. 27 to FIG. 29 are views showing still another embodiment, and correspond to the embodiment shown in FIG. 4 to FIG. Fig. 27 corresponding to Fig. 4 is a plan view, Fig. 28 corresponding to Fig. 5 is a J-J vertical cross-section during daytime operation, and Fig. 29 corresponding to Fig. 6 is a J-J vertical cross-section during night aeration operation. is there.
  • the aeration tank is configured as an aeration tank b2 with a deep floating lid having a liquid surface and a floating body 38. In the daytime, the floating body 38 is the support 39 Rest on top.
  • the floating body 38 covers most of the liquid level and floats on the liquid level.
  • oxygen is supplied to the liquid level in the gap between the floating body 38 and the tank wall, etc., but the supply amount is small, and in the presence of organic substances, the oxygen in the aeration tank b2 with a floating lid is supplied.
  • the suspension s is in an air state, the growth of small animals such as stink bugs is suppressed, and continuous culture of photosynthetic microorganisms is possible.
  • a synthetic resin foam plate or the like may be used as the floating body 38.
  • the cost is lower than that of the upper sealed aeration tank b1, efficient movement and stirring of the suspension s by press-in of air as in the upper sealed aeration tank b1 cannot be performed. Also, during aeration, the impact is severe and the floating body 38 may be damaged.
  • the device of this example is suitable for small-scale culture.
  • the flat pond p is made of a concrete block side wall water tank with an average water depth of 15.5 cm and a light receiving area of 3.6 m2 (2.0 m * 1.8 m), and the upper sealed aeration tank b1 is made of a PVC pipe ⁇ ⁇ ⁇ 500 (inner diameter of 490 mm). The depth was 3.05m and the water depth was 2.95m. A and B units were prepared. Pig urine and garbage leachate were mixed, water was added to the mixture, water was added to the supernatant that had been removed for one week, and water was added. Into the flat pond p, and the culture was started.
  • B does not ventilate. From 8:30 a.m. to 4:30 p.m., both A and B were cultivated in a flat pond p and then returned to the upper closed aeration tank bl. During the experiment, water was added to adjust the amount of water, and valve 15 was opened at night. The experiment was performed in Transparent Vinyl House II. At 4:30 pm, the average water temperature was All.5 and B at 11.0 ° C. The results of the culture are shown in the table below. Culture days A: Night aeration B: No night aeration PCV BOD (ppm) PCV BOD (ppm)
  • the yellowish liquid which produced pests, was added to the PCV5 suspension, and the mixture was added to the flat ponds ⁇ and ⁇ ', and the culture was resumed.
  • a solenoid valve was used for the device of (1), and its opening and closing were performed automatically.
  • the culture in A was carried out from 8:30 in the morning to 4:30 in the afternoon in a flat pond p, followed by aeration for 6 hours, followed by stopping the aeration for 10 hours and maintaining an anaerobic state.
  • the cultivation in B was performed in a flat pond p throughout the day. During the period, the nutrient solution prepared as described above was appropriately added.
  • the flat pond p of B turned yellow, and a large number of devils were observed. In the device A, the dark green state continued for 2 months until the end of the experiment.
  • the present invention can be used not only for cultivation of the above-mentioned cloaca, but also for cultivation of other photosynthetic microorganisms having a respiratory function (green algae, red non-sulfur bacteria, kaya algae, etc.). Needless to say, the present invention can also be used for purification of organic wastewater by these photosynthetic microorganisms.
  • daytime breeding using solar energy is performed in a shallow flat pond p
  • breeding using nighttime oxygen respiration without sunlight is performed in a deep aeration tank with high oxygen dissolution efficiency. It is characterized by forming a field suitable for each metabolism, and can increase the growth rate of photosynthetic microorganisms by increasing the amount of aeration and the aeration time at night in winter when the temperature decreases.
  • the present invention it is possible to increase the cultivation speed during periods of insufficient sunshine and low temperatures, and to achieve almost constant cultivation and cultivation that is not affected by weather conditions throughout the year. This leads to a reduction in facility costs.
  • mass production of small animals such as pests can be prevented, and efficient high-concentration continuous culture can be performed throughout the year.

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Abstract

A culturing method for photosynthetic microbes characterized by culturing photosynthetic microbes by suspending photosynthetic microbes in an organic matter-dissolved liquid in growing photosynthetic microbes such as fine algae and photosynthetic bacteria, in daytime, irradiating the suspension (s) of the photosynthetic microbes with sun rays in a flat pond (p) opened to the atmosphere and having a large gas-liquid contact area, and at night, transferring the suspension (s) to a deep aeration tank (a) having a small gas-liquid contact area and aerating the suspension (s) in the aeration tank (a) with oxygen-containing gas such as air, or transferring the suspension (s) to a deep aeration tank (a) having a small gas-liquid contact area and providing a period of aerating the suspension (s) in the aeration tank (a) with oxygen-containing gas such as air and a period of stopping aeration to keep the suspension (s) in an anaerobic state; and a system associated with this method.

Description

明細睿  Detail

光合成微生物の培養方法と装置 Method and apparatus for culturing photosynthetic microorganisms

産業上の利用分野 Industrial applications

本発明は、 微細澳類、 光合成細菌等光合成微生物の培養方法とその装置 に関する。 本発明は、 上記藻菌体生産のほか、 有機性廃水の浄化処理に も利用できる。 The present invention relates to a method and an apparatus for culturing photosynthetic microorganisms such as pearl oysters and photosynthetic bacteria. The present invention can be used for purification of organic wastewater in addition to the production of algal cells described above.

従来の技術 Conventional technology

一般に光合成微生物の培養は、 微細藻類の培養において見られるよう に、 大規模なものでは酢酸ゃブドウ糖を炭素源とした食用ク口レラ培養 池や有機汚水浄化のための高率酸化池を代表とする、 屋外に建設された 水深 2 O cm 程度の浅く広い平面池 pで行なわれている。 これらはいず れも水面で直接太陽光を受ける上部開放式の培養装置である。 このため、 In general, photosynthetic microorganisms are cultivated on a large scale, such as edible cucumber cultivation ponds using acetic acid / glucose as a carbon source and high-rate oxidation ponds for organic sewage purification, as seen in microalgae cultivation. It is carried out in a shallow and wide flat pond p with a depth of about 2 Ocm, constructed outdoors. These are all open-top culture devices that receive sunlight directly on the water surface. For this reason,

( 1) 寒冷地においては, 広大な水面からの熱損失が大きく, 特に夜間 の熱損失が大きく、 光合成微生物懸濁液が冷却され増殖速度が小 さくなる. (1) In a cold region, the heat loss from the vast water surface is large, especially at night, and the photosynthetic microorganism suspension is cooled and the growth rate is reduced.

(2) 水温がおよそ 1 0 以上となると光合成微生物を捕食するミジン コ, ヮムシ等微小動物の増殖が活発となり, 光合成微生物が活発 に捕食され, ク口レラの場合一昼夜にして全滅させられる例が多 数ある。前記微小動物は, 風、 鳥、 虫などによって運ばれるため、 培養池への侵入とその繁殖を防ぐことが困難であり,, この大量発 生を防ぐには, 大量の薬品を使用せざるを得ない a (2) When the water temperature rises to about 10 or more, the growth of small animals such as daphnids and maggots, which prey on photosynthetic microorganisms, becomes active. There are many. Since the microanimals are carried by wind, birds, insects, etc., it is difficult to prevent invasion into the culture pond and its propagation. To prevent this mass outbreak, a large amount of chemicals must be used. Can't get a

(3) 降雨により光合成微生物懸濁液が希釈され、 光合成微生物漉度が 低下する。さらには、 培桊池から光合成微生物懸濁液が流失する。 この流失を防止するには、 必要以上に培赛池の側壁を高くする必 要性や、温室が必要ない温暖地域においても透明フィルム製の上 屋が必要となる。  (3) Rainfall dilutes the suspension of photosynthetic microorganisms, reducing the filtration rate of photosynthetic microorganisms. Furthermore, the photosynthetic microorganism suspension is washed away from the culture pond. In order to prevent this loss, it is necessary to raise the side wall of the cultivation pond more than necessary, and a transparent film roof is necessary even in a warm region where a greenhouse is not required.

などの問題点があった。 There were problems such as.

これらが解決されれば、光合成細菌、微細藻類等光合成微生物による、 食糧生産、 廃水処理、 炭酸ガス固定、 などが大きく進展する。 このよう な観点から、 本発明者は、 平成 4年 9月 8 日に特願平 4一 282146 (光合 成微生物の培養装置とその運転方法) を、平成 8年 12月 29日に特願平 8—282146 (微細藻類培養装置) を考案し出願した。 If these are solved, food production, wastewater treatment, carbon dioxide fixation, etc. by photosynthetic microorganisms such as photosynthetic bacteria and microalgae will greatly advance. like this From this point of view, the inventor of the present invention filed Japanese Patent Application No. 4-282146 (Photo-synthetic microorganism culturing apparatus and its operation method) on September 8, 1994, and filed Japanese Patent Application No. 282146 (Microalgae cultivation device) was devised and filed.

この結果、 ( 1 ) の問題点が改善され、 光合成微生物のより効率的な 培養が可能となり、 敷地面積が広大となる欠点も改善された。また (2 ) の問題点も解消され、 光合成微生物の安定的連続培養が可能となった。  As a result, the problem of (1) was improved, more efficient cultivation of photosynthetic microorganisms became possible, and the disadvantage that the site area became large was also improved. In addition, the problem of (2) was solved, and stable continuous culture of photosynthetic microorganisms became possible.

しかし、 ( 1 ) の問題点は完全には解消されないままである。  However, the problem (1) has not been completely solved.

光合成微生物の培養、特に廃水処理を目的にした場合、 (1) の問題点 が施設設置の障害となっている。 廃水処理においては、 毎日一定の処理 能力が必要とされる。 太陽光による光合成微生物の培養を行なう場合、 その増殖が日射量や温度等気象条件に大きく左右される。 光合成微生物 の增殖は, 冬期に最も低下するため、 この冬期の增殖を基準に培養^の 規模が設定される。 このため, まだまだ広大な面賴の敷地が必要となつ ている。  When culturing photosynthetic microorganisms, especially for wastewater treatment, the problem (1) is an obstacle to the establishment of facilities. Wastewater treatment requires a certain level of capacity every day. When culturing photosynthetic microorganisms with sunlight, their growth depends greatly on weather conditions such as solar radiation and temperature. Since the growth of photosynthetic microorganisms decreases most in winter, the scale of culture is set based on this winter growth. For this reason, a vast area of the site is still needed.

また、 (3 )の問題点のため、 培養施設の建設費が高価となっている。 発明が解決しょうとする課題  In addition, due to the problem (3), the construction cost of the culture facility is high. Problems to be solved by the invention

そこで本発明は、 寒冷地での懸濁液の冷却を防ぐとともに, 日照等気 象条件に左右されずに一定の優れた培養成績をあげることのできる光 合成微生物の培赛方法及びその装置を提供することを目的とするもの である。  Accordingly, the present invention provides a method and an apparatus for culturing photosynthetic microorganisms, which can prevent the suspension from cooling in a cold region and can provide a certain excellent culturing result without being influenced by the weather conditions such as sunshine. It is intended to provide.

問題を解決するための手段 Means to solve the problem

微細藻類、紅色無硫黄細菌等光合成微生物は、  Photosynthetic microorganisms such as microalgae, red sulfur-free bacteria,

( A) 太陽光エネルギーを吸収し、 このエネルギーを利用して、 炭酸 ガス、 有機物及びその他栄養物を吸収资化し、増殖する能力 ( B )吸収した有機物を異化代謝する過程 (発酵、呼吸)で生成するエネ ルギーを利用して增殖する能力  (A) Ability to absorb solar energy and use this energy to absorb, degrade and proliferate carbon dioxide, organic matter and other nutrients. (B) In the process of catabolizing and metabolizing the absorbed organic matter (fermentation, respiration). Ability to breed using generated energy

を有する。  Having.

夜間、 太陽光の照射がなくなると、 光合成微生物は有機物を異化代謝 する過程 (発酵、呼吸)で生成するエネルギーのみを利用して、 増殖する。 特願平 4一 282146 (光合成微生物の培赛装置とその運転方法)、 及び 特願平 8— 282146 (微細藻類培養装置) の技術は、 昼間、 前記 (A) の 性質により培養し、 夜間にはこの懸濁液を上部密閉容器に収納し、 液の 保温及び嫌気的潔境条件の創出による捕食生物の抑制を可能にした。 そ の後、 上記装置の普及に努める中で、 前述の敷地問題に突き当たり、 こ の問題をさらに改善する研究を重ね、 ついに、 特願平 4一 282146、 及び 特願平 8— 282146に記載された技術に、 (B ) の性質を発揮させる技術 内容を付加する事を考案し、 新たな技術として提案するものである。 ま た、 降雨による問題点も解消するものである。 At night, when sunlight is removed, photosynthetic microorganisms proliferate using only the energy generated during the process of catabolizing and metabolizing organic matter (fermentation, respiration). The technology of Japanese Patent Application No. 4-282146 (culturing device for photosynthetic microorganisms and its operating method) and the technology of Japanese Patent Application No. 8-282146 (microalgae culturing device) are as follows. Stored this suspension in an upper sealed container, and enabled the control of predators by keeping the liquid warm and creating anaerobic and clean conditions. After that, while trying to disseminate the above-mentioned equipment, we came across the above-mentioned site problem and repeated research to further improve this problem. Finally, it was described in Japanese Patent Application Nos. 4-282146 and 8-282146. It is devised to add a technical content that demonstrates the characteristics of (B) to the technology, and proposes it as a new technology. It also solves the problems caused by rainfall.

すなわち本発明は、 That is, the present invention

第 1に, 微細藻類、 光合成細菌等光合成微生物を増殖させる方法におい て, 有機物が溶解した液中に光合成微生物を懸濁させ、 First, in a method of growing photosynthetic microorganisms such as microalgae and photosynthetic bacteria, the photosynthetic microorganisms are suspended in a liquid in which organic matter is dissolved.

昼間は、 大気下に開放された気液接触面稍の大なる浅い平面池 pにお いて、 前記光合成微生物の懸濁液 sに太陽光を照射し,  In the daytime, the suspension s of the photosynthetic microorganisms is irradiated with sunlight in a shallow flat pond p slightly open to the gas-liquid contact surface opened to the atmosphere.

夜間は、 懸濁液 sを気液接触面積の小なる深い曝気槽 aに移し、 曝気 槽 a内の懸濁液 sに空気等酸素含有気体を曝気し、  At night, the suspension s is transferred to a deep aeration tank a with a small gas-liquid contact area, and the suspension s in the aeration tank a is aerated with oxygen-containing gas such as air.

光合成微生物を培養することを特徴とする光合成微生物の培養方法 であり、  A method for culturing a photosynthetic microorganism, which comprises culturing the photosynthetic microorganism,

第 2に、 微細藻類、 光合成細菌等光合成微生物を増殖させる方法におい て, 有機物が溶解した液中に光合成微生物を懸濁させ、 Second, in a method of growing photosynthetic microorganisms such as microalgae and photosynthetic bacteria, the photosynthetic microorganisms are suspended in a solution in which organic matter is dissolved.

昼間は、 大気下に開放された気液接触面積の大なる浅 ^平面池 pにお いて、 前記光合成微生物の懸濁液 Sに太陽光を照射し ·,  During the daytime, the suspension S of the photosynthetic microorganisms is irradiated with sunlight in a shallow ^ -plane pond p, which has a large gas-liquid contact area opened to the atmosphere.

夜間は、 懸濁液 sを気液接触面積の小なる深い曝気槽 aに移し、 曝気 槽 a内の懸濁液 sに空気等酸素含有気体を曝気するとともに、  At night, the suspension s is transferred to a deep aeration tank a with a small gas-liquid contact area, and the suspension s in the aeration tank a is aerated with oxygen-containing gas such as air.

昼間、 降雨時には懸濁液 sを気液接触面積の小なる深い曝気槽 aに移 し、 曝気槽 a内の懸濁液 sに空気等酸素含有気体を曝気し、 前記平面池 pに流入する雨水は平面池 p外へ排出し、 光合成微生物を培養すること を特徴とする光合成微生物の培養方法であり、  During the daytime and during rainfall, the suspension s is transferred to the deep aeration tank a with a small gas-liquid contact area, the suspension s in the aeration tank a is aerated with oxygen-containing gas such as air, and flows into the flat pond p. This is a method for culturing photosynthetic microorganisms, which comprises discharging rainwater out of a flat pond p and culturing photosynthetic microorganisms.

第 3に、 微細藻類、 光合成細菌等光合成微生物を増殖させる方法におい て, 有機物が溶解した液中に光合成微生物を懸濁させ、 昼間は、 大気下に開放された気液接触面積の大なる浅い平面池 Pにお いて、 前記光合成微生物の懸濁液 Sに太陽光を照射し、 Third, the method of growing photosynthetic microorganisms such as microalgae and photosynthetic bacteria In the daytime, the photosynthetic microorganisms are suspended in the liquid in which the organic matter is dissolved. In the daytime, the suspension S of the photosynthetic microorganisms is placed in the shallow flat pond P, which is open to the atmosphere and has a large gas-liquid contact area. Irradiate light,

夜間は、 懸濁液 Sを、 気液接触面積の小なる深い曝気槽に移し、 該曝 気槽内の懸濁液 sに空気等酸素含有気体を曝気する期間、 及び曝気を停 止し懸濁液 sを嫌気状態にする期間を設けて、  At night, the suspension S is transferred to a deep aeration tank with a small gas-liquid contact area, and the suspension s in the aeration tank is aerated with oxygen-containing gas such as air, and the aeration is stopped and suspended. With a period to make the suspension s anaerobic,

光合成微生物を培養することを特徴とする光合成微生物の培養方法で あり、 A method for culturing a photosynthetic microorganism, which comprises culturing the photosynthetic microorganism,

第 4に、 微細藻類、 光合成細菌等光合成微生物を増殖させる方法におい て, 有機物が溶解した液中に光合成微生物を懸濁させ、 Fourth, in a method of growing photosynthetic microorganisms such as microalgae and photosynthetic bacteria, the photosynthetic microorganisms are suspended in a liquid in which organic matter is dissolved.

昼間は、 大気下に開放された気液接触面積の大なる浅い平面池 pにお いて、 前記光合成微生物の懸濁液 sに太陽光を照射し、  In the daytime, the suspension s of the photosynthetic microorganisms is irradiated with sunlight in a shallow flat pond p having a large gas-liquid contact area opened to the atmosphere,

夜間は、 魅濁液 sを、 気液接触面積の小なる深い曝気槽に移し、 該曝 気槽内の懸濁液 sに空気を曝気する期間、 及び曝気を停止し嫌気状態に する期間を設けて、 光合成微生物を培養するとともに、  During the night, the suspension s is transferred to a deep aeration tank with a small gas-liquid contact area, and the suspension s in the aeration tank is aerated with air, and the aeration is stopped and the anaerobic state is stopped. To cultivate photosynthetic microorganisms,

昼間、 降雨時には懸濁液 sを前記曝気槽に移し、 該曝気槽內の懸濁液 sに空気等酸素含有気体を曝気して光合成微生物を培養し、 平面池 pに 流入する雨水は平面池 P外へ排出し、 光合成微生物を培養することを特 徴とする光合成微生物の培篓方法であ,り、  In the daytime, during rainfall, the suspension s is transferred to the aeration tank, and the suspension s in the aeration tank 內 is aerated with oxygen-containing gas such as air to culture photosynthetic microorganisms. P is a method for cultivating photosynthetic microorganisms, which is characterized by culturing the photosynthetic microorganisms to the outside,

第 5に、 微細藻類、 光合成細菌等光合成微生物を有機物が溶解した液中 で培養するための装置において, Fifth, in an apparatus for culturing photosynthetic microorganisms such as microalgae and photosynthetic bacteria in a solution in which organic matter is dissolved,

太陽光を前記有機物が溶解した液中の光合成微生物に照射し該光合 成微生物を増殖させるための、 大気下に開放された気液接触面積の大な る浅い平面池 p、  A shallow flat pond open to the atmosphere and having a large gas-liquid contact area for irradiating sunlight to the photosynthetic microorganisms in the liquid in which the organic matter is dissolved and allowing the photosynthetic microorganisms to proliferate;

前記光合成微生物を含む液を満たし、これに酸素含有気体を曝気し、 該光合成微生物を増殖させるための曝気装置を備えた、 気液接触面積の 小なる深い曝気槽 a  A deep aeration tank having a small gas-liquid contact area, which is filled with a liquid containing the photosynthetic microorganisms, aerated with an oxygen-containing gas, and provided with an aerator for growing the photosynthetic microorganisms.

及び平面池 pと曝気槽 aの間で液を移動させるための液移動機構 m を備えることを特徴とする光合成微生物の培養装置であり 第 6に、 微細藻類、 光合成細菌等光合成微生物を有機物が溶解した液中 で培養するための装箧において, And a liquid transfer mechanism m for transferring liquid between the flat pond p and the aeration tank a. Sixth, in a device for culturing photosynthetic microorganisms such as microalgae and photosynthetic bacteria in a solution in which organic matter is dissolved,

太陽光を前記有機物が溶解した液中の光合成微生物に照射し該光合 成微生物を増殖させるための、 大気下に開放された気液接触面積の大な る浅い平面池 p、  A shallow flat pond open to the atmosphere and having a large gas-liquid contact area for irradiating sunlight to the photosynthetic microorganisms in the liquid in which the organic matter is dissolved and allowing the photosynthetic microorganisms to proliferate;

前記光合成微生物を含む液を満たし、これに酸素含有気体を曝気し、 該光合成微生物を増殖させるための曝気装置を備え、 脱気のための管及 び開閉弁を備えた深い上部密閉曝気槽 b l  A liquid filled with the photosynthetic microorganisms, aerated with an oxygen-containing gas, provided with an aerator for growing the photosynthetic microorganisms, and a deep upper sealed aeration tank bl provided with a pipe for deaeration and an on-off valve.

及び平面池 Pと上部密閉曝気槽 b l の間で液を移動させるための液移 動機構 πχ  And the liquid transfer mechanism for transferring liquid between the flat pond P and the upper closed aeration tank b l

を備えることを特徴とする光合成微生物の培養装置であり、 A culture device for photosynthetic microorganisms, comprising:

第 7に、 微細藻類、 光合成細菌等光合成微生物を有機物が溶解した液中 で培養するための装置において, Seventh, in an apparatus for culturing photosynthetic microorganisms such as microalgae and photosynthetic bacteria in a solution in which organic matter is dissolved,

太陽光を前記有機物が溶解した液中の光合成微生物に照射し該光合 成微生物を増殖させるための、 大気下に開放された気液接触面積の大な る浅い平面池 p、  A shallow flat pond open to the atmosphere and having a large gas-liquid contact area for irradiating sunlight to the photosynthetic microorganisms in the liquid in which the organic matter is dissolved and allowing the photosynthetic microorganisms to proliferate;

前記光合成微生物を含む液を満たし、これに酸素含有気体を曝気して 該光合成微生物を増殖させるための曝気装置、及び液面を覆う浮遊体を 備えた深い.浮蓋付き曝気槽 b 2  A deep aeration tank with a floating lid b2 which is filled with a liquid containing the photosynthetic microorganisms, and is provided with an aerator for aerating an oxygen-containing gas to grow the photosynthetic microorganisms and a floating body covering the liquid surface.

及び平面池 pと浮藎付き曝気槽 b 2 の間で液を移動させるための液移 動機構 m -,  And a liquid transfer mechanism for transferring liquid between the flat pond p and the floating aeration tank b 2

を備えることを特徴とする光合成微生物の培養装置、 に構 してある。 このように本発明は、昼間の太陽光エネルギーを利用した増殖を浅い 平面池 pで行なわせ、太陽光のない夜間の酸素呼吸によるエネルギーを 利用した増殖を酸素溶解効率の高い深い曝気槽で行なわせるものであ り、それぞれの代謝に適する場を形成した方法及び装置である。 An apparatus for culturing photosynthetic microorganisms, comprising: As described above, the present invention allows daytime breeding using solar energy to be performed in a shallow flat pond p, and breeding using energy by nighttime oxygen respiration without sunlight in a deep aeration tank with high oxygen dissolving efficiency. This is a method and an apparatus for forming a field suitable for each metabolism.

図面の簡単な説明 BRIEF DESCRIPTION OF THE FIGURES

図 1は、 本発明の一実施例を示す平 ®図である。 FIG. 1 is a plan view showing one embodiment of the present invention.

図 2は、 図 1における A— A縦断面図であり、昼間作動中の状態を示し ている。 Fig. 2 is a vertical cross-sectional view taken along the line A-A in Fig. 1, showing the state during daytime operation. ing.

図 3は、 図 1における A— A縦断面図であり、 夜間曝気作動中の状態を 示している。 FIG. 3 is a vertical cross-sectional view taken along the line AA in FIG. 1 and shows a state during nighttime aeration.

図 4は、 本発明の別の一実施例を示す平面図である。 FIG. 4 is a plan view showing another embodiment of the present invention.

図 5は、 図 4における B— B縦断面図であり、昼間作動中の状態を示し ている。 FIG. 5 is a vertical cross-sectional view taken along line BB in FIG. 4, and shows a state during daytime operation.

図 6は、 図 4における B— B縦断面図であり、夜間曝気作動中の状態を 示している。 FIG. 6 is a vertical cross-sectional view taken along the line BB in FIG. 4, and shows a state during the night aeration operation.

図 7は、 図 4における B— B縦断面図であり、夜間曝気停止中の状態を 示している。 FIG. 7 is a vertical cross-sectional view taken along the line BB in FIG. 4, and shows a state in which night aeration is stopped.

図 8は、 平面池 pの態様を示す平面図である。 FIG. 8 is a plan view showing an embodiment of the plane pond p.

図 9は、平面池 pの態様を示す平面図である。 FIG. 9 is a plan view showing an embodiment of the plane pond p.

図 10は、平面池 pの態様を示す平面図である。 FIG. 10 is a plan view showing an embodiment of the plane pond p.

図 11は、 また別の実施例を示す縦断面図であり、 図 4乃至図 7に示し た実施例の図 5に対応するもので、 昼間作動中の状態を示している。 図 12は、図 11 と同じ装箧の縦断面図であり、図 6に対応するもので、夜 聞曝気作動中の状態を示している。 FIG. 11 is a longitudinal sectional view showing another embodiment, which corresponds to FIG. 5 of the embodiment shown in FIGS. 4 to 7 and shows a state during operation in the daytime. FIG. 12 is a vertical cross-sectional view of the same device as FIG. 11, and corresponds to FIG. 6, and shows a state during night aeration.

図 1 3は、図 11と同じ装置の縦断面図であり、図 7に対応するもので、夜 間曝気停止中の状態を示している。 FIG. 13 is a longitudinal sectional view of the same device as FIG. 11, and corresponds to FIG. 7, and shows a state in which night aeration is stopped.

図 14は、 また別の実施例を示す平面図である。 FIG. 14 is a plan view showing another embodiment.

図 15は、 図 1 4における D— D縦断面図であり、昼間作軌中の状態を示 している。 Fig. 15 is a vertical sectional view taken along the line DD in Fig. 14, showing the state during daytime operation.

図 16は、 図 1 4における D— D縦断面図であり、昼間作動中の状態を示 している。 FIG. 16 is a vertical cross-sectional view taken along the line DD in FIG. 14, and shows a state during operation in the daytime.

図 17は、 また別の実施例を示す平面図である。 FIG. 17 is a plan view showing another embodiment.

図 18は、図 1 7における E— E縦断面図であり、昼間作動中の状態を示 している。 FIG. 18 is a longitudinal sectional view taken along the line E--E in FIG. 17, and shows a state during operation in the daytime.

図 19は、 図 1 7における E—E縦断面図であり、昼間作動中の状態を示 している。 図 20は、また別の実施例を示す平面図である。図 14に対応する。 FIG. 19 is a longitudinal sectional view taken along the line EE in FIG. 17 and shows a state during daytime operation. FIG. 20 is a plan view showing another embodiment. Corresponds to Figure 14.

図 21は、また別の実施例を示す平面図である。図 17に対応する。 FIG. 21 is a plan view showing another embodiment. Corresponds to FIG.

図 22は、 また別の実施例を示す平面図である。 FIG. 22 is a plan view showing another embodiment.

図 23は、図 22における F—: F縦断面図であり、昼間作動中の状態を示し ている。 FIG. 23 is a vertical sectional view of F—: F in FIG. 22, showing a state during daytime operation.

図 24は、図 23における H— H横断面図であり、昼間作動中の状態を示し ている。 FIG. 24 is a cross-sectional view taken along the line HH in FIG. 23, and shows a state during daytime operation.

図 25.は、 図 22における G— G縦断面図であり、 昼間作動中の状態を示 している。 Fig. 25 is a vertical sectional view taken along the line GG in Fig. 22, showing the state during daytime operation.

図 26は、 図 22における I― I縦断面図であり、 夜間曝気中の状態を示 している。 FIG. 26 is a vertical sectional view taken along the line II in FIG. 22, and shows a state during nighttime aeration.

図 27は、 本発明の一実施例を示す平面図である。 FIG. 27 is a plan view showing one embodiment of the present invention.

図 28は、 図 27における J - J縦断面図であり、昼間作動中の状態を示 している。 FIG. 28 is a vertical sectional view taken along the line JJ in FIG. 27, and shows a state during operation during daytime.

図 29は、 図 27における J— J縦断面図であり、 夜間曝気作動中の状態 を示している。 Fig. 29 is a vertical sectional view taken along the line JJ in Fig. 27, showing the state during the night aeration operation.

符晉の説明 Shin's explanation

aは曝気槽、 pは平面池、 b l は上都密閉曝気槽、 b 2 は浮蓋付き曝気 槽, eは残液排出管、 f は雨水排出管, ¾は気泡、 kは空気層、 mは液 移動機構、 sは懸濁液、 tは液面、 2は弁、 3は散気装置、 4は流量調節弁、 δはブロワ—、 6はポンプ、 7は弁、 8は管、 9は管、 1CM 管、 11は弁、 13は弁、  a is an aeration tank, p is a flat pond, bl is a closed aeration tank in the capital, b 2 is an aeration tank with a floating lid, e is a residual liquid discharge pipe, f is a rainwater discharge pipe, ¾ is a bubble, k is an air layer, m Is a liquid transfer mechanism, s is a suspension, t is a liquid level, 2 is a valve, 3 is a diffuser, 4 is a flow control valve, δ is a blower, 6 is a pump, 7 is a valve, 8 is a pipe, 9 Is a pipe, 1CM pipe, 11 is a valve, 13 is a valve,

14は管、 15は弁、 16は撹拌ロータ—、 17は整流壁、 18は管、 19はポ ンプ、 20は撹拌装置、 21 は台車、 22は中心回転部、 24は導水管、 25 は散気装置、 27は返送管、 28は整流壁、 29は噴出用導水管、 30は吸込 用導水管、 31は吸込用導水管、 33は整流壁、 37は整流壁、 38は浮遊体、 39は支持体  14 is a pipe, 15 is a valve, 16 is a stirring rotor, 17 is a rectifying wall, 18 is a pipe, 19 is a pump, 20 is a stirring device, 21 is a bogie, 22 is a center rotating part, 24 is a water pipe, and 25 is a water pipe. A diffuser, 27 is a return pipe, 28 is a rectifying wall, 29 is a spout water pipe, 30 is a suction water pipe, 31 is a suction water pipe, 33 is a rectifying wall, 37 is a rectifying wall, 38 is a floating body, 39 is the support

破線矢印は懸濁液の流動方向を示す。 Dashed arrows indicate the flow direction of the suspension.

塞施例と作用 図 1乃至図 3は、 本発明の一実施例を示す図面である。 図 1は平面図、 図 2は昼間作動中の A— A縦断面図、 図 3は夜間作動中の A— A縦断面 図である。 本実施例は、 特に捕食生物の增殖抑制を必要としない培養、 すなわち、 高有機物澳度条件下の光合成細菌培養、 クロレラ等微細藻類 の回分培養 (ヮムシ発生前に収穫してしまう)、 殺虫剤添加培養等、 の 場合を示すものである。 Examples and actions 1 to 3 are views showing an embodiment of the present invention. Fig. 1 is a plan view, Fig. 2 is an A-A longitudinal section during daytime operation, and Fig. 3 is an A-A longitudinal section during night operation. This embodiment is particularly useful for cultures that do not require the suppression of the growth of predators, ie, culture of photosynthetic bacteria under conditions of high organic matter, batch culture of microalga such as chlorella (harvested before the occurrence of insects), insecticides This shows the case of 培養 such as addition culture.

装置は、 太陽光の照射を受ける浅い平面池 pと気液接触面積の小なる 深い曝気槽 aからなる。 曝気槽 aの底部には散気装置 3 が設けてある。 曝気槽 aから平面池 pへ有機物を含む栄赛液に光合成微生物を懸濁し た液 (以後懸濁液 S と略す) を送るためのポンプ 6及ぴ管 8、 平面池 p から曝気槽 aへ懸濁液 sを送るための管 9、 により液移動機構 mを構成 してある。 平面池 p底面は管 9設置部位に向けて低く設けられている。 管 9の近傍には残液排出管 e及び雨水排出管 f が設けられている。 The system consists of a shallow flat pond p that receives sunlight and a deep aeration tank a with a small gas-liquid contact area. A diffuser 3 is provided at the bottom of the aeration tank a. Pump 6 and pipe 8 for sending a liquid in which photosynthetic microorganisms are suspended in a nutrient solution containing organic matter (hereinafter referred to as suspension S ) from aeration tank a to plane pond p, and from plane pond p to aeration tank a The liquid transfer mechanism m is constituted by the tube 9 for sending the suspension s. Plane pond The bottom of p is set low toward the pipe 9 installation site. Near the pipe 9, a residual liquid discharge pipe e and a rainwater discharge pipe f are provided.

昼間 (図 2 )、 懸濁液 sを平面池 pに満たして太陽光照射を受けさせ る。 液中の光合成微生物は、 光を吸収し、 このエネルギーを利用して、 有機物を吸収资化し、 増殖する。 夜間 (図 3) には、 弁 7を開け、 管.9 を介して、 懸濁液 sを曝気槽 aへ流下させる。 曝気槽 aを充満させる以 上の懸濁液は平面池 Pに残る。この残液は、弁 2を開け、 残液排出管 eを 介して貯留槽等 (図示せず)へ排出する。次に、曝気槽 aに満たされた懸濁 液 sに、 プロワ 5により、 流量調節弁 4、 管 10、 散気装箧 3を介して、 空気を通気し (gは気泡を示す)、 酸素を供給する。 光.合减微生物は、 この酸素を利用した呼吸により、 有機物を分解かつ资化し、 増殖する。 昼間 (図 2 ) には、 ブロワ 5を停止し、弁 7を閉じ、 ポンプ 6により、 管 8を介して、 懸濁液を平面池 pへ送り、 懸濁液を平面池 pに満たして 太陽光照射を受けさせる。 以後上記工程を繰返し、 培養を行なう。  In the daytime (Fig. 2), the suspension s is filled in the flat pond p and exposed to sunlight. The photosynthetic microorganisms in the liquid absorb light and use this energy to absorb and degrade organic matter and proliferate. At night (Figure 3), valve 7 is opened and suspension s is allowed to flow down to aeration tank a via line .9. Suspension that fills aeration tank a remains in flat pond P. This residual liquid is discharged to a storage tank or the like (not shown) via the residual liquid discharge pipe e by opening the valve 2. Next, air is passed through the suspension s filled in the aeration tank a through the flow control valve 4, the pipe 10, and the air diffuser 3 by the purer 5 (g indicates bubbles), and oxygen Supply. Light and synthetic microorganisms decompose, degrade, and multiply organic matter by respiration using oxygen. In the daytime (Fig. 2), the blower 5 is stopped, the valve 7 is closed, and the pump 6 sends the suspension to the flat pond p via the pipe 8 and fills the suspension with the flat pond p. Subject to light irradiation. Thereafter, the above steps are repeated to perform the culture.

昼間降雨時には、弁 7を開け、 管 9を介して、 懸濁液 sを曝気槽 aへ 流下させる。次に、矚.気槽 aに満たされた懸濁液 sに、プロワ 5により、 流!:調節弁 4、 管 10、 散気装憧3を介して、 空気を通気し (gは気泡を 示す)、 酸素を供給する。 光合成微生物は、 この酸素を利用した呼吸に より、 有機物を分解かつ资化し、 増殖する。 平面池 P内に流入してくる 雨水は、弁 11 を開け、雨水排出管 f を介して排水路等 (図示せず) へ排 出する。 During daytime rainfall, the valve 7 is opened, and the suspension s flows down to the aeration tank a via the pipe 9. Next, flow into the suspension s filled in the a. : Air is supplied through control valve 4, pipe 10, and diffuser 3 (g indicates air bubbles), and oxygen is supplied. Photosynthetic microorganisms use this oxygen to breathe It decomposes, degrades, and proliferates organic matter. The rainwater flowing into the flat pond P is opened to the drainage channel (not shown) via the rainwater discharge pipe f by opening the valve 11.

実験室における純粋培養は例外として、屋外における大量培養では非 光合成微生物の混入 '増殖は必ず存在する。 平面池 pの水深は、光合成微 生物を優先的に増殖させるため、 20cm 以下が適当である。 水深 20 c m 以上では深くなるほど、光合成微生物の澳度が低下し、優先的に増殖さ せることが難しくなる。  With the exception of pure culture in the laboratory, large-scale outdoor cultures always contain contamination with non-photosynthetic microorganisms. The water depth of the flat pond p is appropriate to be less than 20 cm to preferentially grow photosynthetic microorganisms. At depths above 20 cm, the depth of the photosynthetic microorganisms decreases, making it difficult to grow preferentially.

夜間や降雨時に、平面池 pに通気し、 酸素を供給して、上記のように 光合成微生物を呼吸代謝により増殖させることも可能であるが、平面池 Pは浅いため、単位動力当りの酸素供給能が、極めて低く、費用の点から、 現実的に実施不可能である。 本発明では、懸濁液 sを深い曝気槽 aに導 き、ここで曝気するので、単位動力当りの酸素供給能が高く、 現実的に実 施可能である。 通常の活性汚泥法曝気槽で、曝気水深 3— 4 m で、 6— 8 %の酸素溶解効率が得られる。 本発明の曝気槽 a水深も 2.5— 4 m に 設定すればよい。 At night or during rainfall, it is possible to ventilate the flat pond p and supply oxygen to allow photosynthetic microorganisms to grow by respiratory metabolism as described above.However, since the flat pond P is shallow, oxygen supply per unit power Performance is extremely low and is not practically feasible in terms of cost. In the present invention, since the suspension s is guided to the deep aeration tank a where the suspension s is aerated, the oxygen supply capacity per unit power is high and the suspension s can be practically implemented. In a conventional activated sludge aeration tank, an oxygen dissolution efficiency of 6-8% can be obtained at an aeration water depth of 3-4m. The water depth of the aeration tank a of the present invention may be set to 2.5-4 m.

このように、 本発明では、夜間や降雨時にも、 光合成微生物を効率的 に増殖させることにより、 単位嗨設面積当りの増殖量を增加させること が可能となる。  As described above, according to the present invention, it is possible to increase the amount of proliferation per unit area by efficiently growing photosynthetic microorganisms even at night or during rainfall.

図 4乃至図 7は、 本発明の別の一実施例を示す (¾面である。 図 4は平 面.図、 図 5は昼間作動中の B— B縦断面図、 図 6は夜間暴気作動中の; B 一 B縦断面図,図 7は夜間曝気停止中の B— B縦断面図である。本実施例 は、 特に捕食生物の增殖抑制を必要とする培桊、 すなわち殺虫剤無添加 による光合成微生物の連続培桊、 の場合を示すものである。 本装置は、 曝気槽が上部密閉曝気槽 b l に構成され、 空気の出し入れをする管 14 及び弁 1 5を備える点が、 図 1乃至図 3に示した装置と學なる。  4 to 7 show another embodiment of the present invention (a side view. FIG. 4 is a plan view, FIG. 5 is a vertical sectional view taken along the line BB during daytime operation, and FIG. Fig. 7 is a vertical sectional view taken along the line B-B while the aeration is stopped during night operation, and this embodiment is particularly applicable to cultures that require suppression of the growth of predators, that is, insecticides. This device shows the case of continuous cultivation of photosynthetic microorganisms with no addition.This equipment has a point that the aeration tank is configured as an upper closed aeration tank bl, and is equipped with a pipe 14 for taking in and out air and a valve 15. This is similar to the device shown in FIGS.

昼間 (図 5)、 懸濁液を平面池!)に満たして太陽光照射を受けさせる。 液中の光合成微生物は、 光を吸収し、 このエネルギーを利用して、 有機 物を吸収资化し、増殖する。 夜間 (図 6) には、 弁 7及び弁 1 5を開け、 管 9を介して、 懸濁液を上部密閉曝気槽 b lへ流下させる。 上部密閉曝 気槽 b 1 を充満させる以上の懸濁液 sは平面池 pに残る。この平面池 p に残る残液中では、 残液が空気と接触しているため、 ヮムシ等光合成微 生物は生存、增殖できる。これを避けるため、 この残液は、収穫物として、 弁 2を開け、 残液排出管 eを介して貯留槽等 (図示せず)へ排出する。 次に、 上部密閉曝気槽 b lに満たされた懸濁液に、 ブロワ 5により、 流量調節弁 4、 管 10、 散気装置 3を介して、 空気を通気し、 酸素を供給 する。 光合成微生物は、 この酸素を利用した呼吸により、 有機物を分解 かつ资化し、 増殖する。 その後 (図 7 ) ブロワ 5を停止し、 弁 7、 弁 1 3及び弁 1 5を閉じる。 上部密閉曝気槽 b内の酸素は次第に消費されて 嫌気状態となる。 嫌気条件下ヮムシ等捕食生物は次第に死滅していく。 光合成微生物は、 1日から 2 3間程度であれば、 生存している。 In the daytime (Fig. 5), the suspension is a flat pond! ) And receive sunlight irradiation. The photosynthetic microorganisms in the liquid absorb light and use this energy to absorb and degrade organic matter and proliferate. At night (Figure 6), valves 7 and 15 are opened, The suspension flows down via pipe 9 into the upper closed aeration tank bl. Suspension s that fills upper closed aeration tank b 1 remains in flat pond p. In the residual liquid remaining in the flat pond p, the residual liquid is in contact with air, so that photosynthetic microorganisms such as insects can survive and grow. In order to avoid this, the residual liquid is discharged as a harvest into a storage tank or the like (not shown) through the residual liquid discharge pipe e by opening the valve 2. Next, air is supplied to the suspension filled in the upper closed aeration tank bl through the flow control valve 4, the pipe 10, and the air diffuser 3 by the blower 5 to supply oxygen. The photosynthetic microorganisms decompose, degrade, and multiply organic matter by respiration using this oxygen. After that (Fig. 7), blower 5 is stopped, and valves 7, 13 and 15 are closed. The oxygen in the upper closed aeration tank b is gradually consumed and becomes anaerobic. Under anaerobic conditions, predators such as worms gradually die. The photosynthetic microorganism is alive for about 1 to 23 days.

ヮムシは、 嫌気条件下 6時間程度で半数致死、 12時間程度で全数致死 となり、 半数致死のものを 48時間曝気すると元の状態に戻るという実 験結果が得られている。 上記夜間の曝気停止時間は、 8時間以上が適当 である。  It has been experimentally shown that ヮ worms can be killed in half under anaerobic conditions in about 6 hours, and all in about 12 hours, and return to their original state when a half of them are aerated for 48 hours. It is appropriate to stop the aeration at night for 8 hours or more.

昼間 (図 5) には、 ブロワ 5を停止し、 弁 7を閉じ、 弁 1 3及び弁 1 5を開け、 ポンプ 6により、 管 8を介して、 懸濁液を平面池 pへ送り、 懸濁液を平面池 pに満たして太陽光照射を受けさせる。 以後上記工程を 繰返し、 培養を行なう。  During the daytime (Fig. 5), the blower 5 is stopped, the valve 7 is closed, the valves 13 and 15 are opened, and the suspension is sent by the pump 6 through the pipe 8 to the flat pond p. Fill the suspension pond p with the suspended liquid and irradiate it with sunlight. Thereafter, the above steps are repeated to perform the culture.

昼間降雨時には、上記夜間の場合と同様に、 曝気槽 a .に満たされた懸 濁液 sを曝気するとともに、 平面池 p内に流入してくる雨水は、排水路 等 (図示せず) へ排出する。  During daytime rainfall, the suspended liquid s filled in the aeration tank a. Is aerated as in the case of the nighttime above, and the rainwater flowing into the flat pond p is discharged to drainage channels (not shown). Discharge.

夜間懸濁液 sが平面池 p内に残存しないよう、 丰面池 p底面は管 9設 置部位に向けて低く設けられ、 管 9の近傍には残液排出管 eが設けられ ている。これは、必須条件ではなく、平面池 p底面はほぼ水平でも良い。 ほぼ水平であれば、懸濁液 sが黄変し連続培養が不可能となることはな い。  In order to prevent the night suspension s from remaining in the flat pond p, the bottom of the pond p is set low toward the pipe 9 installation site, and a residual liquid discharge pipe e is provided near the pipe 9. This is not an essential condition, and the p-bottom of the flat pond may be almost horizontal. If it is almost horizontal, the suspension s does not turn yellow and continuous culturing is not possible.

このように本発明の方法及び装置によれば、 夜間や昼間降雨時にも、 光合成微生物を効率的に増殖させることにより、 単位面積当りの増殖量 を增加させることが可能となるとともに、 ヮムシ等の増殖が抑制される ので、毎日懸濁液 sを収穫し、この収穫分と同量の栄養液を添加す.る、レ、 わゆる連続培養が可能となる。 また、毎日排出される有機性廃水を栄赛 液として用いる場合、光合成微生物の収穫量増加とともに、これを毎日 連統して効率的に浄化処理できる。 As described above, according to the method and apparatus of the present invention, even at night or during daytime rainfall, By efficiently growing photosynthetic microorganisms, it is possible to increase the amount of growth per unit area and to suppress the growth of worms. By adding the same amount of nutrient solution, continuous culture is possible. In addition, when organic wastewater discharged daily is used as a nutrient solution, the yield of photosynthetic microorganisms increases, and this can be continuously and efficiently purified daily.

本実施例では、夜間、曝気した後、 曝気を停止し嫌気状態 したが、順 序を逆にして、 嫌気状態に保持した後、 曝気を行なう方式でも、同様の 効果がある。  In the present embodiment, the aeration is stopped at night after the aeration, and then the anaerobic state is achieved. However, the same effect can be obtained by performing the aeration after the order is reversed and the anaerobic state is maintained.

図 1乃至図' 7に示した平面池 pは、特に撹拌機構を設けていないが、曝 気槽 a又は上部密閉曝気槽 b l へ懸濁液 sを毎日移動させる際の流動で 光合成微生物の沈穣はほとんど防止できる。 また、添加した栄養液との 混合は曝気槽 a又は上部密閉曝気槽 b 1 で毎曰行なわれるので、平面池 Pで栄養分の濃度が不均一になることも防止している。 しかし、增殖を さらに速めるには、撹拌機構は必要である。  The flat pond p shown in Fig. 1 to Fig. 7 does not have a specific stirring mechanism, but the flow when the suspension s is moved daily to the aeration tank a or the upper closed aeration tank bl. Harvest can be almost prevented. In addition, since the mixing with the added nutrient solution is performed in the aeration tank a or the upper closed aeration tank b1, the concentration of nutrients in the flat pond P is also prevented from becoming uneven. However, a stirrer is needed to speed up breeding.

平面池 pに関する実施例を、平面図で図 8乃至図 10に示した。 いずれ も水深 10— 40cmの浅い平面池 pである。 図 8の平面池 pは、整流壁 17 で区画された 1 つの無終端水路に、矢印の方向に懸濁液 sを流動させる ための撹拌ロータ— 16が設けられ、撹拌機構が構成されている。 図 9の 平面池 pは、整流壁 17で区画された 1つの水路の下流端から上流端へポ ンプ 1 9により管 1 8を介して懸濁液 sを送ることによ-.. H、矢印の方向 に懸濁液 sを流動させ、撹拌機構を構成している。 図 1 0は、円形の平面 池 pの中心回転部 2 2から円周側壁上端上の台車 21にかけて、下方にプ ラシのついた撹拌装置 2 0を設け、矢印の方向に、台車 21を動かし、池内 を搅拌する。  Examples of the plane pond p are shown in plan views in FIGS. Each is a shallow flat pond with a depth of 10-40 cm. In the flat pond p in Fig. 8, a stirring rotor 16 for flowing the suspension s in the direction of the arrow is provided in one endless water channel defined by the rectifying wall 17, and a stirring mechanism is configured. . The flat pond p in Fig. 9 is obtained by sending the suspension s via the pipe 18 by the pump 19 from the downstream end to the upstream end of one waterway defined by the rectifying wall 17-.. H, The suspension s is caused to flow in the direction of the arrow to form a stirring mechanism. Fig. 10 shows that a stirrer 20 with a brush is provided from the center rotating part 22 of the circular flat pond p to the bogie 21 on the upper end of the circumferential side wall, and the bogie 21 is moved in the direction of the arrow. And stir the pond.

図 8乃至図 1 0に示した撹拌機構を有する平面池 pは、撹拌装置の分 だけ施設费 '運転費が高価となる力 本発明にも利用できる。  The plane pond p having the stirring mechanism shown in FIGS. 8 to 10 can be used also in the present invention because of the power required to increase the operating cost of the facility by the amount of the stirring device.

図 11乃至図 13は、 また別の実施例を示す図面であり、 図 4乃至図 7 に示した実施例に対応するものである。 図 5に対応する図 11は昼間作 動中の縦断面図、 図 6に対応する図 12は夜間曝気作動中の縦断面図,図 7に対応する図 13は夜間曝気停止中の縦断面図である。 図 4乃至図 7 に示した実施例と異なる点は、管 9 が上部密閉曝気槽 b 1底部に開口し ている点である。 FIGS. 11 to 13 show another embodiment, and correspond to the embodiments shown in FIGS. 4 to 7. FIG. Fig. 11, which corresponds to Fig. 5, is a daytime crop. A longitudinal sectional view during operation, FIG. 12 corresponding to FIG. 6 is a longitudinal sectional view during night aeration operation, and FIG. 13 corresponding to FIG. 7 is a longitudinal sectional view during night aeration stop. The difference from the embodiment shown in FIGS. 4 to 7 is that the pipe 9 opens at the bottom of the upper sealed aeration tank b1.

昼間 (図 11)、 弁 15閉弁 7開の状態で、ブロワ 5により管 10を介し て散気装置 3 より空気を送る。 懸濁液 sは、管 9を介して平面池 pへ押 し出される。 その後、弁 7を閉じ、ブロワ 5 を停止し、懸濁液 sを平面池 pに満たして太陽光照射を受けさせ、 光合成微生物を増殖せしめる。 夜 間 (図 12) には、 弁 7及ぴ弁 1 5を開け、 管 9を介して、 懸濁液 sを上 部密閉曝気槽 b 1 へ流下させる。 次に、 上部密閉曝気槽 b 1 に満たされ た懸濁液 sに、 ブロワ 5により、 流量調節弁 4、 管 10、 散気装置 3を介 して、 空気を通気し、 酸素を供給する。 光合成微生物は、 この酸素を利 用した呼吸により、有機物を分解かつ资化し、増殖する。その後(図 13) ブロワ 5を停止し、 弁 7、 流量調節弁 4及び弁 1 5を閉じ、 上部密閉曝 気槽 b内懸濁液 sを嫌気状態にする。 昼間 (図 11) には、 弁 7及び弁 4 を開け、 ブロワ 5を作動させ、 懸濁液を平面池 pへ送る。 以後上記工程 を繰返し、 培養を行なう。 昼間降雨時等他の操作は、前記実施例と同様 に行なう。  During the daytime (Fig. 11), with the valve 15 closed and the valve 7 open, air is sent from the air diffuser 3 through the pipe 10 by the blower 5. The suspension s is extruded through a pipe 9 into a flat pond p. Thereafter, the valve 7 is closed, the blower 5 is stopped, and the suspension s is filled in the flat pond p and is irradiated with sunlight to allow the photosynthetic microorganisms to grow. At night (Fig. 12), the valve 7 and the valve 15 are opened, and the suspension s is allowed to flow through the pipe 9 into the upper closed aeration tank b1. Next, air is supplied to the suspension s filled in the upper closed aeration tank b 1 through the flow control valve 4, the pipe 10, and the air diffuser 3 by the blower 5 to supply oxygen. The photosynthetic microorganisms decompose, degrade, and proliferate organic substances by respiration using oxygen. Thereafter (Fig. 13), the blower 5 is stopped, the valve 7, the flow control valve 4 and the valve 15 are closed, and the suspension s in the upper sealed aeration tank b is made anaerobic. During the daytime (Fig. 11), the valves 7 and 4 are opened, the blower 5 is operated, and the suspension is sent to the flat pond p. Thereafter, the above steps are repeated to perform the culture. Other operations such as rain during the day are performed in the same manner as in the above-described embodiment.

本実施例では、ポンプは不必要となり、ブロワ 5の o n— o f f により、 簡単に懸濁液 sを移動することができる。  In this embodiment, the pump is not required, and the suspension s can be easily moved by the on-off of the blower 5.

図 14乃至図 16は、 また別の実施例を示す図面であり- ^図 14は平面 図、 図 15及ぴ図 16は昼間作動中の D— D縦断面図である。 図 1乃至図 13に示した実施例と異なる点は、上部密閉曝気槽 b 1が、平面池 pの中央 下方に設けられ、導水管 24により平面池 p底部と上部密閉曝気槽 b 1底 部が連絡されている点である。 昼間 (図 15、 16)、 弁 15閉、 弁 4開の 状態で、プロワ 5により管 10を介して散気装置 25より空気を送る。 懸 濁液 sは、導水管. 24 を介して平面池 pへ押し出される。 その後、上部密 閉曝気槽 b内の液面 tが下降し導水管 24 の下端に達する。 さらに液面 は、水の表面張力により、 下降し、やがて、空気 kがー気に導水路 24内に 噴出する。 そして、導水路 24内の懸濁液 sは、空気 kとともに上昇し、平 面池 P内に噴出する(図 15)。噴出が終わると、平面池 p内の懸濁液 sは、 導水路 24内を下降して、上部密閉曝気槽 b l内に流入する (図 16)。 こ の一連の動作により平面池 p内には、波動が生じ、 懸濁液 sは撹拌され る。 懸濁液 sは、撹拌を受けながら、太陽光の照射を受け、光合成微生物 が増殖する。 夜間 (図示せず) には、 弁 1 5を開け、 導水管 24 を介し て、 滕濁液 sを上部密閉曝気槽 b lへ流下させる。 次に、 流量調節弁 4 を開け、 上部密閉曝気槽 b l内に満たされた懸濁液 sに、 ブロワ 5によ り、 流量調節弁 4、 管 10、 散気装置 25を介して、 空気を通気し、 酸素 を供給する。 光合成微生物は、 この酸素を利用した呼吸により、 有機物 を分解かつ资化し、 增殖する。 その後ブロワ 5を停止し、 流量調節弁 4 及び弁 1 5を閉じ、上部密閉曝気槽 b l内を嫌気状態にする。昼間には、 弁 4を開け、 ブロワ 5を作動させ、 懸濁液を平面池 pへ送る。 以後上記 工程を繰返し培養を行なう。 昼間降雨時等他の操作は、前記実施例と同 様に行なう。 14 to 16 are views showing still another embodiment. FIG. 14 is a plan view, and FIGS. 15 and 16 are vertical sectional views taken along the line DD during daytime operation. The difference from the embodiment shown in FIGS. 1 to 13 is that the upper sealed aeration tank b1 is provided below the center of the flat pond p, and the bottom of the flat pond p and the bottom of the upper sealed aeration tank b1 are connected by the water pipe 24. Has been contacted. In the daytime (Figs. 15 and 16), air is sent from the air diffuser 25 through the pipe 10 by the blower 5 with the valve 15 closed and the valve 4 open. The suspension s is pushed out to the flat pond p via the conduit. Then, the liquid level t in the upper closed aeration tank b descends and reaches the lower end of the water pipe 24. Further, the liquid surface descends due to the surface tension of the water, and the air k eventually flows into the water conduit 24. Gushing. Then, the suspension s in the headrace channel 24 rises with the air k and jets into the flat pond P (FIG. 15). When the jetting ends, the suspension s in the flat pond p descends in the headrace 24 and flows into the upper closed aeration tank bl (Fig. 16). By this series of operations, a wave is generated in the plane pond p, and the suspension s is stirred. The suspension s is irradiated with sunlight while being stirred, and the photosynthetic microorganisms proliferate. At night (not shown), the valve 15 is opened, and the turbid liquid s is allowed to flow down to the upper closed aeration tank bl via the water pipe 24. Next, the flow control valve 4 is opened, and air is supplied to the suspension s filled in the upper sealed aeration tank bl via the flow control valve 4, the pipe 10, and the air diffuser 25 by the blower 5. Ventilate and supply oxygen. The photosynthetic microorganisms decompose, degrade, and grow organic matter by respiration using this oxygen. Thereafter, the blower 5 is stopped, the flow control valve 4 and the valve 15 are closed, and the inside of the upper sealed aeration tank bl is made anaerobic. In the daytime, the valve 4 is opened, the blower 5 is operated, and the suspension is sent to the flat pond p. Thereafter, the above steps are repeated for culturing. Other operations such as rain during the day are performed in the same manner as in the above embodiment.

本実施例では、ブロワ 5の o n— o f f により、簡単に懸濁液を移動で きるとともに、撹拌装置を新たに設置せずに平面池 p内懸濁液を簡単に 撹拌できる。  In the present embodiment, the suspension can be easily moved by the on-off of the blower 5, and the suspension in the flat pond p can be easily stirred without newly installing a stirring device.

図 17乃至図 19は、 また別の実施例を示す図面であり、 図 17は平面 図、 図 18は昼間作動中の E— E縦断面図、 図 19は昼間作動中の E— E 縦断面図である。 図 14乃至図 16に示した実施例と異な..る点は、平面池 p端部と上部密閉曝気槽 b l 底部を連絡する返送管 27 が設けられてい る点である。 返送管 27は、上部密閉曝気槽 b l内の導水管 24の下端よ りも下方に開口するよう配備する。 本実施例では、空気が導水管 24から 平面池 pへ喷出した場合 (図 18) 、返送管 27 より速やかに懸濁液 sが 上部密閉曝気槽 b 1内に流入するので、懸濁液 sの混合も行なえる。他の 運転操作は、図 14乃至図 16に示した実施例と同様に行なえばよい。 図 20は、図 14乃至図 16に示した実施例の図 14に対応する平面図で ある。 平面池 pは、長い水路に構成され、その端部下方に上部密閉曝気槽 b 1が設けられている。図 21は、図 17乃至図 19に示した実施例の図 17 に対応する平面図である。 平面池 pは、長い水路に構成され、その端部下 方に上部密閉曝気槽 b lが設けられている。 返送管 27は、平面池 pの端 部と上部密閉曝気槽 b底部を連絡している。 平面池 pの形状は、上記実 施例に限定されるものではなく、敷地の形状、施設予算等いろいろな条 件を考慮して決定すればよい。 17 to 19 are diagrams showing still another embodiment. FIG. 17 is a plan view, FIG. 18 is a longitudinal sectional view of E-E during daytime operation, and FIG. 19 is a longitudinal sectional view of E-E during daytime operation. FIG. The difference from the embodiment shown in FIGS. 14 to 16 is that a return pipe 27 is provided to connect the end of the flat pond p and the bottom of the upper closed aeration tank bl. The return pipe 27 is provided so as to open below the lower end of the water pipe 24 in the upper closed aeration tank bl. In this embodiment, when the air flows out of the water pipe 24 to the flat pond p (FIG. 18), the suspension s flows into the upper closed aeration tank b1 promptly from the return pipe 27, Mixing of s is also possible. Other driving operations may be performed in the same manner as in the embodiment shown in FIGS. FIG. 20 is a plan view corresponding to FIG. 14 of the embodiment shown in FIGS. Plane pond p is composed of a long water channel and an upper closed aeration tank below its end. b 1 is provided. FIG. 21 is a plan view corresponding to FIG. 17 of the embodiment shown in FIGS. The flat pond p is composed of a long waterway, and an upper closed aeration tank bl is provided below its end. The return pipe 27 connects the end of the flat pond p and the bottom of the upper closed aeration tank b. The shape of the flat pond p is not limited to the above embodiment, but may be determined in consideration of various conditions such as the shape of the site and the budget for the facility.

図 22乃至図 26は、 本発明のまた別の実施例を示す図面であり、図 22 は平面図、図 23は昼間作動中の F— F縦断面図、図 25は昼間作動中の G —G縦断面図、図 24は昼間作動中の H— H横断面図、図 26は夜間曝気中 の I一 I縦断面図である。 本実施例は、図 2 1に示した装置と同様の機 能を有するものである。図 2 1の装置においては、上部密閉曝気槽 b 1内 導水管 2 4、水路状平面池 p、返送管 2 7、上部密閉曝気槽 b内の順に懸 濁液 sが流動するよう構成されている。 本実施例の装置においても、平 面池 pを整流壁 28で区画し、上流端と下流端が上部密閉曝気槽 b上で隣 接する 1本の水路に構成し、 この上流端に噴出用導水管 29、下流端に吸 込み用導水管 30 , 3 1を設け、喷出用導水管 29、平面池 p、 吸込み用導 水管 3 0, 3 1、 上部密閉曝気槽 b l の順に懸濁液が循環的に流動する よう構成してある。 37は整流壁である。 図 2 1においては、水路状平面 池 Pの流積に見合う返送管 27を設けるには、費用が高価となる。 本実施 例では、平面池 pを整流壁 28で区画し、上流端と下流端が上部密閉曝気 槽 b 1上で隣接する 1本の水路に構成し、こ.の上流端に噴-出用導水管 29、 下流端に吸込み用導水管 3 0 , 3 1を設けてあるので、費用も安く、平面 池 P内の流動もよく、混合 ·撹拌が効率よく行なえる。  FIGS. 22 to 26 are views showing another embodiment of the present invention. FIG. 22 is a plan view, FIG. 23 is a longitudinal sectional view taken along the line FF during daytime operation, and FIG. G longitudinal section, Fig. 24 is H-H transverse section during daytime operation, and Fig. 26 is I-I longitudinal section during night aeration. This embodiment has the same function as the device shown in FIG. In the device shown in Fig. 21, the suspension s is configured to flow in the order of the water pipe 24 in the upper closed aeration tank b1, the channel-shaped flat pond p, the return pipe 27, and the upper closed aeration tank b. I have. Also in the apparatus of the present embodiment, the flat pond p is divided by the rectifying wall 28, and the upstream end and the downstream end are configured as one adjacent water channel on the upper closed aeration tank b. A water pipe 29, suction water pipes 30 and 31 are provided at the downstream end, and a suspension water pipe 29, a flat pond p, a suction water pipe 30 and 31 and an upper closed aeration tank bl in this order. It is configured to flow cyclically. 37 is a rectifying wall. In FIG. 21, it is expensive to provide the return pipe 27 corresponding to the flow product of the channel-shaped flat pond P. In the present embodiment, the flat pond p is divided by the rectifying wall 28, and the upstream end and the downstream end are formed as one adjacent water channel on the upper closed aeration tank b1, and the upstream end of the pond is used for jetting. Since the water supply pipe 29 and the suction water supply pipes 30 and 31 are provided at the downstream end, the cost is low, the flow in the flat pond P is good, and the mixing and stirring can be performed efficiently.

図 27乃至図 29は、 また別の実施例を示す図面であり、 図 4乃至図 7 に示した実施例に対応するものである。図 4に対応する図 27は平面図、 図 5に対応する図 28は昼間作動中の J― J縦断面図,図 6に対応する図 29は夜間曝気作動中の J一 J縦断面図である。 図 4乃至図 7に示した 実施例と異なる点は、曝気槽が液面を耰ぅ浮遊体 38を備えた深い浮蓋付 き曝気槽 b 2に構成されている点である。昼間には浮遊体 38は支持体 39 上に静止する。夜間には浮遊体 38は液面の大部分を覆い液面上に浮遊す る。 夜間曝気停止時、 浮遊体 38 と槽壁面等との間隙部分の液面には酸 素が供給されるが、その供給量は少なく、 有機物存在下では浮蓋付き曝 気槽 b 2 内の懸濁液 sは缣気状態となり、 ヮムシ等微小動物の增殖は抑 制され、 光合成微生物の連続培養が可能である。浮遊体 38としては合成 樹脂発泡板等を用いればよい。 FIG. 27 to FIG. 29 are views showing still another embodiment, and correspond to the embodiment shown in FIG. 4 to FIG. Fig. 27 corresponding to Fig. 4 is a plan view, Fig. 28 corresponding to Fig. 5 is a J-J vertical cross-section during daytime operation, and Fig. 29 corresponding to Fig. 6 is a J-J vertical cross-section during night aeration operation. is there. The difference from the embodiment shown in FIGS. 4 to 7 is that the aeration tank is configured as an aeration tank b2 with a deep floating lid having a liquid surface and a floating body 38. In the daytime, the floating body 38 is the support 39 Rest on top. At night, the floating body 38 covers most of the liquid level and floats on the liquid level. When aeration is stopped at night, oxygen is supplied to the liquid level in the gap between the floating body 38 and the tank wall, etc., but the supply amount is small, and in the presence of organic substances, the oxygen in the aeration tank b2 with a floating lid is supplied. The suspension s is in an air state, the growth of small animals such as stink bugs is suppressed, and continuous culture of photosynthetic microorganisms is possible. As the floating body 38, a synthetic resin foam plate or the like may be used.

本実施例の場合、上部密閉曝気槽 b 1 と比べて安価となるが、上部密閉 曝気槽 b lのような空気の圧入による懸濁液 sの効率的な移動や撹拌は 行なえなレ、。また、曝気時には、衝撃も激しく、浮遊体 38の破損も生じる。 本実施例の装置は小規模の培養に適する。  In the case of the present embodiment, although the cost is lower than that of the upper sealed aeration tank b1, efficient movement and stirring of the suspension s by press-in of air as in the upper sealed aeration tank b1 cannot be performed. Also, during aeration, the impact is severe and the floating body 38 may be damaged. The device of this example is suitable for small-scale culture.

本発明の方法及び装置による運転結果を示せば、下記のようである。 (実施例)  The operation results of the method and apparatus of the present invention are as follows. (Example)

平成 13年 2月 6日より、図 11乃至図 13に示す装置で Chlorella sp. の回分培養を行なった。 平面池 pは、平均水深 15.5cm、受光面積 3.6m2 (2.0m * 1.8m) のコンクリー トブロック側壁水槽、上部密閉曝気槽 b 1 は塩ビパイプ ν υ φ 500 (内径 490mm) で作製し、高さ 3.05m、水深 2.95mとした。 上記装置を A , B 2基作製した。 豚尿と生ゴミ浸出水を 混合し、これに水を加え、 1週間放篋した上澄液に、さらに水を加え、これ に種株液を加えた液を等分し、 A、Bそれぞれの平面池 pに投入し、培養 を開始した。 Aには、 午後 4時 30分から 8時間、およそ 10L Z分の空 気を、上部密閉曝気槽 b 1水深 2.8mの位置から、通気した Bは、通気を 行なわない。 A、 Bともに朝 8時 30分から午後 4時 30分まで、平面池 pにて培桊し、その後上部密閉曝気槽 b l に戻した。 実験期間中、水を添 加し水量を調節し、また弁 15 は夜間開とした。 また、実験は透明ビニー ルハウス內で行なった。 午後 4 時 30分の水温は、 平均で A ll.5 、 B 11.0°Cであった。 培養の結果を下表に示した。 培養日数 A:夜間曝気有り B :夜間曝気無し 曰 PCV B O D (ppm) PCV B O D (ppm)From February 6, 2001, batch culture of Chlorella sp. Was performed using the apparatus shown in FIGS. The flat pond p is made of a concrete block side wall water tank with an average water depth of 15.5 cm and a light receiving area of 3.6 m2 (2.0 m * 1.8 m), and the upper sealed aeration tank b1 is made of a PVC pipe ν υ φ500 (inner diameter of 490 mm). The depth was 3.05m and the water depth was 2.95m. A and B units were prepared. Pig urine and garbage leachate were mixed, water was added to the mixture, water was added to the supernatant that had been removed for one week, and water was added. Into the flat pond p, and the culture was started. A ventilated about 10 LZ for 8 hours from 4:30 pm to A from the upper closed aeration tank b 1 at a depth of 2.8 m. B does not ventilate. From 8:30 a.m. to 4:30 p.m., both A and B were cultivated in a flat pond p and then returned to the upper closed aeration tank bl. During the experiment, water was added to adjust the amount of water, and valve 15 was opened at night. The experiment was performed in Transparent Vinyl House II. At 4:30 pm, the average water temperature was All.5 and B at 11.0 ° C. The results of the culture are shown in the table below. Culture days A: Night aeration B: No night aeration PCV BOD (ppm) PCV BOD (ppm)

0 2.6 1980 2.6 19800 2.6 1980 2.6 1980

8 7.4 73 4.9 600 表より、本発明の夜間曝気の効果が認められる。 8 7.4 73 4.9 600 From the table, the effect of night aeration of the present invention is recognized.

その後 4月に、 P C V 5の懸濁液に、 ヮムシが発生し黄色がかった液を 添加混合し、 Α、Β'それぞれの平面池 ρに投入し、培養を再開した。 Αの 装置に用いる弁は電磁弁を用い、その開閉は自動的に行なった。 Aでの 培桊は、朝 8時 30分から午後 4時 30分まで、平面池 pにて培養し、その 後 6時間曝気し、その後 10時間曝気を停止し嫌気状態を保った。 Bでの 培養は、平面池 pで 1 日中行なった。期間中は、上記と同様に調整した栄 養液を適宜添加した。実験開始後、 5 日目に Bの平面池 pは、黄色に変化 し、ヮムシの大量発生が観察された。 Aの装置では、その後 2 ヶ月間濃い 緑色の状態が実験終了まで続いた。 Then, in April, the yellowish liquid, which produced pests, was added to the PCV5 suspension, and the mixture was added to the flat ponds Α and Β ', and the culture was resumed. A solenoid valve was used for the device of (1), and its opening and closing were performed automatically. The culture in A was carried out from 8:30 in the morning to 4:30 in the afternoon in a flat pond p, followed by aeration for 6 hours, followed by stopping the aeration for 10 hours and maintaining an anaerobic state. The cultivation in B was performed in a flat pond p throughout the day. During the period, the nutrient solution prepared as described above was appropriately added. On the 5th day after the start of the experiment, the flat pond p of B turned yellow, and a large number of devils were observed. In the device A, the dark green state continued for 2 months until the end of the experiment.

本発明は、上記のク口レラの培桊だけでなく、呼吸機能を有する他の 光合成微生物 (緑藻類、紅色非硫黄細菌、ケィ藻等)の培養にも利用できる。 また、これら光合成微生物による有機廃水の浄化にも本発明は利用でき ることは言うまでもない。  The present invention can be used not only for cultivation of the above-mentioned cloaca, but also for cultivation of other photosynthetic microorganisms having a respiratory function (green algae, red non-sulfur bacteria, kaya algae, etc.). Needless to say, the present invention can also be used for purification of organic wastewater by these photosynthetic microorganisms.

発明の効果 The invention's effect

以上のように、本発明の方法及び装置は、  As described above, the method and apparatus of the present invention

第 1 に、昼間の太陽光エネルギーを利用した増殖を浅い平面池 pで行 なわせ、太陽光のない夜間の酸素呼吸によるエネルギーを利用した増殖 を酸素溶解効率の高い深い曝気槽で行なわせるものであり、それぞれの 代謝に適する場を形成したことを特徴とし、温度が低下する冬期に夜間 の曝気量、曝気時間を増加させることにより、光合成微生物の增殖速度 を高めることができる。  First, daytime breeding using solar energy is performed in a shallow flat pond p, and breeding using nighttime oxygen respiration without sunlight is performed in a deep aeration tank with high oxygen dissolution efficiency. It is characterized by forming a field suitable for each metabolism, and can increase the growth rate of photosynthetic microorganisms by increasing the amount of aeration and the aeration time at night in winter when the temperature decreases.

第 2に、特願平 8—282146 (微細藻類培養装置)では、上部密閉槽は、 保温とヮムシ抑制の役割しかなかったが、 本発明は、 この夜間に缣気状 態に保つ期間と曝気する期間を設けたことを特徴とするものである。こ れによれば、保温、 ヮムシ抑制に加えて夜間の効果的増殖が可能となる。 すなわち、温度が低下する冬期に夜間の曝気量、曝気時間を増加させる ことにより、光合成微生物の增殖速度を高めることができるとともに、 ヮムシ等微小動物の大量発生も防止できる。 Secondly, in Japanese Patent Application No. 8-282146 (Microalgae cultivation device), the upper closed tank only played a role of keeping the heat and suppressing the worms. This is characterized in that a period is set for the operation. This According to this, in addition to keeping warm and suppressing stink bugs, effective propagation at night becomes possible. That is, by increasing the amount of aeration and the aeration time at night in winter when the temperature decreases, the growth rate of photosynthetic microorganisms can be increased, and the occurrence of a large number of small animals such as insects can be prevented.

第 3に、昼間降雨時には、 平面池 pに流入する雨水を排出し、曝気槽に て光合成微生物に酸素呼吸によるエネルギーを利用した増殖を行なわ せる特徴がある。 iのため、日照不足期の増殖低下、降雨による懸濁液の 希釈を防止できる。温暖地域においては、透明フィルム上屋が必要ない。 また上屋を設けない場合の過度に高い側壁の建設が必要ない。  Thirdly, during rainfall during the daytime, rainwater flowing into the flat pond p is drained, and the photosynthetic microorganisms are propagated in the aeration tank using energy from oxygen respiration. Because of i, it is possible to prevent the growth of the suspension during the period of lack of sunshine and dilution of the suspension due to rainfall. Transparent film sheds are not required in warm regions. In addition, there is no need to construct an excessively high side wall when no shed is provided.

以上まとめれば、本発明によって、日照不足期や低温期の增殖速度を 高めることができ、年間を通して気象条件により左右されないほぼ一定 の僂れた培養成練をあげることができ、 結果的に敷地面積及びそれに伴 う施設費の減少につながる。 また、ヮムシ等微小動物の大量発生も防止 でき、年間を通して、効率的な高濃度連続培養が可能となる。  In summary, according to the present invention, it is possible to increase the cultivation speed during periods of insufficient sunshine and low temperatures, and to achieve almost constant cultivation and cultivation that is not affected by weather conditions throughout the year. This leads to a reduction in facility costs. In addition, mass production of small animals such as pests can be prevented, and efficient high-concentration continuous culture can be performed throughout the year.

Claims

請求の範囲 The scope of the claims 【請求項 1】 微細藻類、 光合成細菌等光合成微生物を増殖させる方法に おいて, 有機物が溶解した液中に光合成微生物を懸濁させ、  Claims: 1. A method for growing photosynthetic microorganisms such as microalgae and photosynthetic bacteria, wherein the photosynthetic microorganisms are suspended in a liquid in which organic matter is dissolved. 昼間は、 大気下に開放された気液接触面積の大なる浅い平面池 pにお いて、 前記光合成微生物の懸濁液 sに太陽光を照射し,  In the daytime, the suspension s of the photosynthetic microorganisms is irradiated with sunlight in a shallow flat pond p open to the atmosphere and having a large gas-liquid contact area, 夜間は、 懸濁液 sを気液接触面積の小なる深い曝気槽 aに移し、 曝気 槽 a内の懸濁液 sに空気等酸素含有気体を曝気し、  At night, the suspension s is transferred to a deep aeration tank a with a small gas-liquid contact area, and the suspension s in the aeration tank a is aerated with oxygen-containing gas such as air. 光合成微生物を培養することを特徴とする光合成微生物の培養方法。  A method for culturing a photosynthetic microorganism, comprising culturing the photosynthetic microorganism. 【請求項 2】 微細藻類、 光合成細菌等光合成微生物を増殖させる方法に おいて, 有機物が溶解した液中に光合成微生物を懸濁させ、 2. A method for growing photosynthetic microorganisms such as microalgae and photosynthetic bacteria, wherein the photosynthetic microorganisms are suspended in a liquid in which organic substances are dissolved. 昼間は、 大気下に開放された気液接触面積の大なる浅い平面池 pにお いて、 前記光合成微生物の懸濁液 sに太陽光を照射し,  In the daytime, the suspension s of the photosynthetic microorganisms is irradiated with sunlight in a shallow flat pond p open to the atmosphere and having a large gas-liquid contact area, 夜間は、 懇濁液 sを気液接触面積の小なる深い曝気槽 aに移し、 曝気 槽 a内の懸濁液 sに空気等酸素含有気体を曝気するとともに、  At night, the suspension s is transferred to a deep aeration tank a having a small gas-liquid contact area, and the suspension s in the aeration tank a is aerated with oxygen-containing gas such as air. 昼間降雨時には、 懸濁液 sを気液接触面積の小なる深い曝気槽 aに移 し、 曝気槽 a内の懸濁液 sに空気等酸素含有気体を曝気し、 平面池 pに 流入する雨水は平面池 p外へ排出し、 光合成微生物を培養することを特 徴.とする光合成微生物の培養方法。  During daytime rainfall, the suspension s is transferred to the deep aeration tank a with a small gas-liquid contact area, the suspension s in the aeration tank a is aerated with oxygen-containing gas such as air, and the rainwater flowing into the flat pond p Is a method for cultivating photosynthetic microorganisms, which is characterized by discharging photosynthetic microorganisms out of a flat pond. 【請求項 3】 微細藻類、 光合成細菌等光合成微生物を増殖させる方法に おいて, 有機物が溶解した液中に光合成微生物を懸濁させ、  3. A method for growing photosynthetic microorganisms such as microalgae and photosynthetic bacteria, wherein the photosynthetic microorganisms are suspended in a liquid in which organic substances are dissolved. 昼間は、 大気下に開放された気液接触面積の大なる浅 、平面池 pにお いて、 前記光合成微生物の懸濁液 sに太陽光を照射し、  In the daytime, the suspension s of the photosynthetic microorganisms is irradiated with sunlight in a flat pond p having a large gas-liquid contact area opened to the atmosphere, 夜間は、 懸濁液 sを気液接触面積の小なる深い曝気槽に移し、 該曝気 槽内の懸濁液 sに空気等酸素含有気体を曝気する期間、 及び曝気を停止 し懸濁液 sを嫌気状態にする期間を設けて、  At night, the suspension s is transferred to a deep aeration tank having a small gas-liquid contact area, the suspension s in the aeration tank is aerated with oxygen-containing gas such as air, and the aeration is stopped to stop the suspension s. With a period of anaerobic 光合成微生物を培赛することを特徴とする光合成微生物の培養方法。A method for culturing a photosynthetic microorganism, comprising culturing the photosynthetic microorganism. 【請求項 4】 微細藻類、 光合成細菌等光合成微生物を増殖させる方法に おいて, 有機物が溶解した液中に光合成微生物を懸濁させ、 4. A method for growing photosynthetic microorganisms such as microalgae and photosynthetic bacteria, wherein the photosynthetic microorganisms are suspended in a liquid in which organic matter is dissolved. 昼間は、 大気下に開放された気液接触面積の大なる浅い平面池 pにお いて、 前記光合成微生物の懸濁液 sに太陽光を照射し、 夜間は、 懸濁液 sを、 気液接触面積の小なる深い曝気槽に移し、 該曝 気槽内の懸濁液 Sに空気を曝気する期間、 及ぴ曝気を停止し懸濁液 Sを 嫌気状態にする期間を設けて、 光合成微生物を培養するとともに、 昼間降雨時には、 懸濁液 sを前記曝気槽に移し、 該曝気槽内の懸濁液 sに空気等酸素含有気体を曝気して光合成微生物を培養し、 平面池 pに 流入する雨水は平面池 P外へ排出し、 光合成微生物を培養することを特 徴とする光合成微生物の培養方法。 In the daytime, the flat pond p, which is open to the atmosphere and has a large gas-liquid contact area, is Then, the suspension s of the photosynthetic microorganisms is irradiated with sunlight, and at night, the suspension s is transferred to a deep aeration tank having a small gas-liquid contact area, and the suspension S in the aeration tank is A period for aerating the air and a period for stopping the aeration and bringing the suspension S into an anaerobic state are provided to culture the photosynthetic microorganisms, and at the time of daytime rainfall, the suspension s is transferred to the aeration tank and the aeration is performed. A photosynthetic microorganism is cultured by aerating oxygen-containing gas such as air to the suspension s in the tank, and rainwater flowing into the flat pond p is discharged out of the flat pond P to culture the photosynthetic microorganism. A method for culturing photosynthetic microorganisms. 【請求項 5】 前記曝気槽が、 脱気のための管及び開閉弁を備え、上部が 隔壁で密閉された上部密閉曝気槽 b l であることを特徴とする請求項 3 又は請求項 4記載の光合成微生物の培養方法。  5. The aeration tank according to claim 3 or 4, wherein the aeration tank is provided with a pipe for deaeration and an on-off valve, and is an upper sealed aeration tank bl having an upper part sealed with a partition wall. A method for culturing photosynthetic microorganisms. 【請求項 6】 前記曝気槽が、 液面を覆う浮遊体を備えた、浮蓋付き曝気 槽 b 2であることを特徴とする請求項 3又は請求項 4記載の光合成微生 物の培養方法。  6. The method for culturing photosynthetic microorganisms according to claim 3, wherein the aeration tank is an aeration tank b2 with a floating lid provided with a floating body covering a liquid surface. . 【請求項 7】 微細藻類、 光合成細菌等光合成微生物を有機物が溶解した 液中で培養するための装置において,  7. An apparatus for culturing photosynthetic microorganisms such as microalgae and photosynthetic bacteria in a solution in which organic matter is dissolved, 太陽光を前記有機物が溶解した液中の光合成微生物に照射し、 該光合 成微生物を増殖させるための、 大気下に開放された気液接触面積の大な る浅い平面池 p、  A shallow flat pond open to the atmosphere and having a large gas-liquid contact area for irradiating sunlight to the photosynthetic microorganisms in the liquid in which the organic matter is dissolved, and allowing the photosynthetic microorganisms to proliferate; 前記光合成微生物を含む液を満たし、これに酸素含有気体を曝気し、 該光合成微生物を増殖させるための曝気装置を備えた、-氮液接触面積の 小なる深い曝気槽 a  A deep aeration tank with a small liquid-contact area, comprising an aerator for filling the liquid containing the photosynthetic microorganisms, aerating the oxygen-containing gas with the liquid, and growing the photosynthetic microorganisms. 及び平面池 pと曝気槽 aの間で液を移動させるための液移動機構 m を備えることを特徴とする光合成微生物の培養装置。  And a liquid transfer mechanism m for moving a liquid between a flat pond p and an aeration tank a. 【請求項 8】 微細藻類、 光合成細菌等光合成微生物を有機物が溶解した 液中で培養するための装置において,  8. An apparatus for culturing photosynthetic microorganisms such as microalgae and photosynthetic bacteria in a solution in which organic matter is dissolved, 太陽光を前記有機物が溶解した液中の光合成微生物に照射し、 該光合 成微生物を増殖させるための、 大気下に開放された気液接触面積の大な る浅い平面池 p、 前記光合成微生物を含む液を満たし、これに酸素含有気体を曝気し、 該光合成微生物を増殖させるための曝気装置を備え、 脱気のための管及 ぴ開閉弁を備えた深い上部密閉曝気槽 b l A shallow flat pond open to the atmosphere and having a large gas-liquid contact area for irradiating sunlight to the photosynthetic microorganisms in the liquid in which the organic matter is dissolved, and allowing the photosynthetic microorganisms to proliferate; A liquid containing the photosynthetic microorganisms is filled, oxygen-containing gas is aerated there, an aerator for growing the photosynthetic microorganisms is provided, a pipe for deaeration and a deep upper sealed aeration tank bl 及び平面池 pと上部密閉曝気槽 b 1 の間で液を移動させるための液移 動機構 m、 を備えることを特徴とする光合成微生物の培養装置。  And a liquid transfer mechanism m for transferring a liquid between the flat pond p and the upper closed aeration tank b 1. 【請求項 9】平面池 p底部と上部密閉曝気槽 b 1底部を連絡する導水管、 前記脱気のため管及び開閉弁、及び上部密閉曝気槽 b 1 に気体を圧入す るための気体圧入機により、前記液移動機構 mを形成したことを特徴と する請求項 8記載の光合成微生物の培養装置。  9. A water pipe connecting the bottom of the flat pond p and the bottom of the upper sealed aeration tank b1, the pipe and the on-off valve for deaeration, and the gas injection for injecting gas into the upper sealed aeration tank b1. 9. The culture apparatus for photosynthetic microorganisms according to claim 8, wherein the liquid transfer mechanism m is formed by a machine. 【請求項 10】微細藻類、光合成細菌等光合成微生物を有機物が溶解した 液中で培養するための装置において,  10. An apparatus for culturing photosynthetic microorganisms such as microalgae and photosynthetic bacteria in a solution in which organic matter is dissolved, 太陽光を前記有機物が溶解した液中の光合成微生物に照射し該光合 成微生物を増殖させるための、 大気下に開放された気液接触面積の大な る浅い平面池 p、  A shallow flat pond open to the atmosphere and having a large gas-liquid contact area for irradiating sunlight to the photosynthetic microorganisms in the liquid in which the organic matter is dissolved and allowing the photosynthetic microorganisms to proliferate; 前記光合成微生物を含む液を満たし、これに酸素含有気体を曝気して 該光合成微生物を増殖させるための曝気装置、及び液面を覆う浮遊体を. 備えた深い浮蓋付き曝気槽 b 2  An aeration tank for filling a liquid containing the photosynthetic microorganisms, aerating the oxygen-containing gas therewith to grow the photosynthetic microorganisms, and a floating body covering the liquid surface with a deep floating lid b 2. 及び平面池 pと浮蓋付き曝気槽 b 2の間で液を移動させるための液移 動機構 m、 を備えることを特徴とする光合成微生物の培赛装置。  And a liquid transfer mechanism m for transferring a liquid between the flat pond p and the aeration tank b2 with a floating lid. 【請求項 11】平面池 p底部又は液移動機構 mを構成する導水路に、平面 池 Pに流入する雨水を排出するための、 雨水排出管 f を備、えることを特 徴とする請求項 5又は請求項 6又は請求項 7又は請求項 8又は請求項 9 又は請求項 10記載の光合成微生物の培養装置。  11. The rainwater discharge pipe f for discharging rainwater flowing into the flat pond P is provided at the bottom of the flat pond p or the headrace channel constituting the liquid moving mechanism m. 11. The photosynthetic microorganism culturing apparatus according to claim 5, claim 6, claim 7, claim 7, claim 8, claim 9, or claim 10. 【請求項 12】平面池 p底部又は液移動機構 mを構成する導水路に、曝気 槽 a又は上部密閉曝気槽 b l又は浮蓋付き曝気槽 b 2 を充満させる以上 の平面池 p内懸濁液 sを排出するための、 残液排出管 eを備えることを 特徴とする請求項 5又は請求項 6又は請求項 7又は請求項 8又は請求項 9又は請求項 10又は請求項 11記載の光合成微生物の培桊装置。  [12] A suspension in the flat pond p which fills the bottom of the flat pond p or the headrace channel forming the liquid transfer mechanism m with the aeration tank a, the upper closed aeration tank bl or the aeration tank b2 with a floating lid. A photosynthetic microorganism according to claim 5, characterized in that it has a residual liquid discharge pipe (e) for discharging s. 5.The photosynthetic microorganism according to claim 5, 6, 7, 8, 7, 8, 9, 10, or 11. Cultivation equipment.
PCT/JP2002/007043 2001-07-11 2002-07-11 Culturing method and device for photosynthetic microbes Ceased WO2003006629A1 (en)

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Cited By (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2009122905A1 (en) * 2008-03-12 2009-10-08 Sekine Toshirou Culturing method for photosynthetic microorganisms such as microalgae
EP2151235A1 (en) 2008-07-21 2010-02-10 Dr. Falk Pharma Gmbh Pharmaceutical formulation for treating the upper digestive tract
NL2002309C2 (en) * 2008-12-10 2010-06-11 Newplant B V PHOTOBIOREACTOR AND METHOD FOR GROWING ALGAE.
WO2010038912A3 (en) * 2008-10-03 2010-06-17 Sekine Toshirou Microalgae culture method and device
EP2245936A1 (en) 2009-04-27 2010-11-03 Bayer CropScience AG Use of 4-aza indole derivatives for the reduction of mycotoxin contamination
WO2011036517A1 (en) * 2009-09-28 2011-03-31 Harshvardhan Jaiswal System and method for growing photosynthetic micro-organism
WO2012050220A1 (en) * 2010-10-13 2012-04-19 Sekine Toshirou Culturing method and device for photosynthetic microorganism
WO2012050221A3 (en) * 2010-10-13 2012-06-21 Sekine Toshirou Culturing method and device for photosynthetic microorganism
AU2009200346B2 (en) * 2008-02-01 2015-01-29 Pan Pacific Technologies Pty Ltd Planar bioreactor
WO2022159989A1 (en) 2021-01-25 2022-07-28 Avails Medical, Inc. Apparatus, systems, and methods for preparing an output sample with aeration
JPWO2023281569A1 (en) * 2021-07-05 2023-01-12
WO2024246039A1 (en) * 2023-05-31 2024-12-05 L'air Liquide, Societe Anonyme Pour L'etude Et L'exploitation Des Procedes Georges Claude Method for injecting co2 in the absence of light, in spirulina culture

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5329981A (en) * 1976-09-01 1978-03-20 Takashi Tokanehara Cultivating apparatus for photosynthesis microorganism
JPH0690735A (en) * 1992-09-08 1994-04-05 Toshiro Sekine Cultivation apparatus for photosynthetic microorganism and its operation
JPH06133757A (en) * 1992-10-26 1994-05-17 Mitsubishi Heavy Ind Ltd Device for photosynthetic reaction of fine alga
US6037170A (en) * 1996-12-30 2000-03-14 Sekine; Toshirou Apparatus for culturing microalgae

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5329981A (en) * 1976-09-01 1978-03-20 Takashi Tokanehara Cultivating apparatus for photosynthesis microorganism
JPH0690735A (en) * 1992-09-08 1994-04-05 Toshiro Sekine Cultivation apparatus for photosynthetic microorganism and its operation
JPH06133757A (en) * 1992-10-26 1994-05-17 Mitsubishi Heavy Ind Ltd Device for photosynthetic reaction of fine alga
US6037170A (en) * 1996-12-30 2000-03-14 Sekine; Toshirou Apparatus for culturing microalgae

Cited By (16)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
AU2009200346B2 (en) * 2008-02-01 2015-01-29 Pan Pacific Technologies Pty Ltd Planar bioreactor
WO2009122905A1 (en) * 2008-03-12 2009-10-08 Sekine Toshirou Culturing method for photosynthetic microorganisms such as microalgae
EP2151235A1 (en) 2008-07-21 2010-02-10 Dr. Falk Pharma Gmbh Pharmaceutical formulation for treating the upper digestive tract
WO2010038912A3 (en) * 2008-10-03 2010-06-17 Sekine Toshirou Microalgae culture method and device
NL2002309C2 (en) * 2008-12-10 2010-06-11 Newplant B V PHOTOBIOREACTOR AND METHOD FOR GROWING ALGAE.
EP2245936A1 (en) 2009-04-27 2010-11-03 Bayer CropScience AG Use of 4-aza indole derivatives for the reduction of mycotoxin contamination
WO2010124793A1 (en) 2009-04-27 2010-11-04 Bayer Cropscience Ag Use of 4-aza indole derivatives for the reduction of mycotoxin contamination
WO2011036517A1 (en) * 2009-09-28 2011-03-31 Harshvardhan Jaiswal System and method for growing photosynthetic micro-organism
WO2012050221A3 (en) * 2010-10-13 2012-06-21 Sekine Toshirou Culturing method and device for photosynthetic microorganism
WO2012050220A1 (en) * 2010-10-13 2012-04-19 Sekine Toshirou Culturing method and device for photosynthetic microorganism
WO2022159989A1 (en) 2021-01-25 2022-07-28 Avails Medical, Inc. Apparatus, systems, and methods for preparing an output sample with aeration
JPWO2023281569A1 (en) * 2021-07-05 2023-01-12
WO2023281569A1 (en) * 2021-07-05 2023-01-12 日本電信電話株式会社 Utility pole and method for generating oxygen using same
JP7687398B2 (en) 2021-07-05 2025-06-03 日本電信電話株式会社 Electric pole and method for generating oxygen using the same
WO2024246039A1 (en) * 2023-05-31 2024-12-05 L'air Liquide, Societe Anonyme Pour L'etude Et L'exploitation Des Procedes Georges Claude Method for injecting co2 in the absence of light, in spirulina culture
FR3149326A1 (en) * 2023-05-31 2024-12-06 L'air Liquide, Societe Anonyme Pour L'etude Et L'exploitation Des Procedes Georges Claude CO2 injection process in the absence of light, in spirulina culture

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