WO2017203781A1 - Methane fermentation device - Google Patents
Methane fermentation device Download PDFInfo
- Publication number
- WO2017203781A1 WO2017203781A1 PCT/JP2017/008127 JP2017008127W WO2017203781A1 WO 2017203781 A1 WO2017203781 A1 WO 2017203781A1 JP 2017008127 W JP2017008127 W JP 2017008127W WO 2017203781 A1 WO2017203781 A1 WO 2017203781A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- tank
- methane fermentation
- methane
- gas
- processed material
- Prior art date
Links
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 title claims abstract description 302
- 238000000855 fermentation Methods 0.000 title claims abstract description 110
- 230000004151 fermentation Effects 0.000 title claims abstract description 110
- 238000012545 processing Methods 0.000 claims abstract description 29
- 239000007787 solid Substances 0.000 claims abstract description 15
- 239000000463 material Substances 0.000 claims description 53
- 239000000126 substance Substances 0.000 claims description 4
- 238000005063 solubilization Methods 0.000 description 44
- 230000007928 solubilization Effects 0.000 description 44
- 241000894006 Bacteria Species 0.000 description 30
- 239000010815 organic waste Substances 0.000 description 19
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 16
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 16
- 239000002994 raw material Substances 0.000 description 16
- 238000002156 mixing Methods 0.000 description 13
- 108091005804 Peptidases Proteins 0.000 description 12
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 12
- 239000004365 Protease Substances 0.000 description 11
- 239000002609 medium Substances 0.000 description 11
- 238000003756 stirring Methods 0.000 description 11
- 102100037486 Reverse transcriptase/ribonuclease H Human genes 0.000 description 10
- 229910002092 carbon dioxide Inorganic materials 0.000 description 8
- 239000001569 carbon dioxide Substances 0.000 description 8
- 238000006477 desulfuration reaction Methods 0.000 description 8
- 230000023556 desulfurization Effects 0.000 description 8
- 229910021529 ammonia Inorganic materials 0.000 description 7
- 238000001816 cooling Methods 0.000 description 6
- 238000000034 method Methods 0.000 description 4
- 230000008569 process Effects 0.000 description 4
- 238000010907 mechanical stirring Methods 0.000 description 3
- 230000004048 modification Effects 0.000 description 3
- 238000012986 modification Methods 0.000 description 3
- 238000010248 power generation Methods 0.000 description 3
- 238000001179 sorption measurement Methods 0.000 description 3
- 241000194110 Bacillus sp. (in: Bacteria) Species 0.000 description 2
- 108010059892 Cellulase Proteins 0.000 description 2
- 102000004190 Enzymes Human genes 0.000 description 2
- 108090000790 Enzymes Proteins 0.000 description 2
- 108010031186 Glycoside Hydrolases Proteins 0.000 description 2
- 102000005744 Glycoside Hydrolases Human genes 0.000 description 2
- 102000004882 Lipase Human genes 0.000 description 2
- 108090001060 Lipase Proteins 0.000 description 2
- 239000004367 Lipase Substances 0.000 description 2
- 102000035195 Peptidases Human genes 0.000 description 2
- 239000008186 active pharmaceutical agent Substances 0.000 description 2
- 238000005273 aeration Methods 0.000 description 2
- 150000001720 carbohydrates Chemical class 0.000 description 2
- 229940106157 cellulase Drugs 0.000 description 2
- 239000002361 compost Substances 0.000 description 2
- 238000001035 drying Methods 0.000 description 2
- 229940088598 enzyme Drugs 0.000 description 2
- 150000002484 inorganic compounds Chemical class 0.000 description 2
- 229910010272 inorganic material Inorganic materials 0.000 description 2
- 238000003780 insertion Methods 0.000 description 2
- 230000037431 insertion Effects 0.000 description 2
- 235000019421 lipase Nutrition 0.000 description 2
- 230000000813 microbial effect Effects 0.000 description 2
- 150000002894 organic compounds Chemical class 0.000 description 2
- 238000003825 pressing Methods 0.000 description 2
- 102000004169 proteins and genes Human genes 0.000 description 2
- 108090000623 proteins and genes Proteins 0.000 description 2
- 230000003381 solubilizing effect Effects 0.000 description 2
- 241000193830 Bacillus <bacterium> Species 0.000 description 1
- 239000002028 Biomass Substances 0.000 description 1
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 1
- 230000004913 activation Effects 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 239000012736 aqueous medium Substances 0.000 description 1
- 239000007900 aqueous suspension Substances 0.000 description 1
- 230000008901 benefit Effects 0.000 description 1
- 238000007664 blowing Methods 0.000 description 1
- 235000014633 carbohydrates Nutrition 0.000 description 1
- 235000010980 cellulose Nutrition 0.000 description 1
- 229920002678 cellulose Polymers 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 230000000593 degrading effect Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 230000029087 digestion Effects 0.000 description 1
- 230000001079 digestive effect Effects 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- 239000003925 fat Substances 0.000 description 1
- 235000019197 fats Nutrition 0.000 description 1
- 239000010794 food waste Substances 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 238000007654 immersion Methods 0.000 description 1
- 238000011065 in-situ storage Methods 0.000 description 1
- 244000144972 livestock Species 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 230000007246 mechanism Effects 0.000 description 1
- 230000037353 metabolic pathway Effects 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 239000010813 municipal solid waste Substances 0.000 description 1
- 150000007524 organic acids Chemical class 0.000 description 1
- 229920000642 polymer Polymers 0.000 description 1
- 238000003672 processing method Methods 0.000 description 1
- 230000035755 proliferation Effects 0.000 description 1
- 235000018102 proteins Nutrition 0.000 description 1
- 229940024999 proteolytic enzymes for treatment of wounds and ulcers Drugs 0.000 description 1
- 230000000630 rising effect Effects 0.000 description 1
- 239000010801 sewage sludge Substances 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 241000894007 species Species 0.000 description 1
Images
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/02—Biological treatment
- C02F11/04—Anaerobic treatment; Production of methane by such processes
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
Definitions
- the present invention relates to a methane fermentation apparatus.
- the present invention has been made in view of the above circumstances, and provides a methane fermentation apparatus capable of preventing the discharge of untreated materials and increasing the concentration of methane gas without requiring mechanical stirring.
- the purpose is to do.
- a methane fermentation apparatus comprises: A dry methane fermentation device, A methane fermentation tank that ferments the processed material to generate methane gas while the processed material that is divided into three or more processing tanks and is put into the uppermost tank is sequentially sent to the lower processing tank,
- the methane fermenter is The processing object which collects the processing thing in the bottom face in a tank, and is equipped with the processing thing circulation part which blows off the processing substance in the tank from the 1st outflow port provided in the solid upper edge formed by the processing thing in a tank, The first outflow port faces the center of the solid.
- the gas circulation part A cylindrical body that is erected on the bottom surface in the tank so as to surround the second outflow port, and whose lower side surface and upper surface are opened; It is good as well.
- the second outlet and the cylindrical body are: In the flow of the processed material formed in the tank by the processed material flowing out from the first outlet, it is disposed at a place where the processed material stays. It is good as well.
- the treated product circulation part is: A heat exchanger that transmits heat of a gas engine that generates power using methane gas generated in the methane fermentation tank to a processed product, It is good as well.
- the methane fermentation apparatus A dry methane fermentation device, A methane fermentation tank that ferments the processed material to generate methane gas while the processed material that is divided into three or more processing tanks and is put into the uppermost tank is sequentially sent to the lower processing tank,
- the methane fermenter is A gas circulation unit is provided that collects gas generated in the tank and blows out the gas from an outlet provided in the bottom of the tank.
- the gas circulation unit A cylindrical body that is erected on the bottom surface in the methane fermentation tank so as to surround the outlet and has a lower side surface and an upper surface opened, It is good as well.
- the methane fermentation tank is divided into three or more stages, and while the processed product is carried to the lower processing tank, there remains no unprocessed product that is not subjected to methane fermentation. It is possible to prevent the discharge of objects. Moreover, since the flow of the processed material can be created diagonally in the tank, the state of the processed material in the tank can be made uniform without requiring mechanical stirring. In addition, by passing the generated methane gas through the processed material, the processed material can absorb carbon dioxide, so that the concentration of methane gas can be increased.
- the Z axis is the vertical direction
- the XY plane is the horizontal plane.
- the methane fermentation apparatus generates methane gas by methane fermentation of organic waste, and uses the generated methane gas as biomass energy.
- the organic waste is a substance mainly composed of macromolecular organic compounds such as proteins, carbohydrates, fats and celluloses or compounds derived therefrom, and does not substantially contain solid inorganic compounds.
- some solid inorganic compounds may be contained as long as they can be easily solubilized and do not adversely affect the growth of microorganisms.
- organic waste examples include organic waste such as livestock sludge, sewage sludge, and garbage such as food waste. You may use these as a raw material which concentrated the solid concentration before the solubilization process. Moreover, you may add the organic substance of the metabolic pathway in the methane fermentation process which mixed saccharide
- the methane fermentation apparatus 1 includes a crusher 10, a mixing tank 20, a solubilization tank 30, a methane fermentation tank 40, a cooling tower 50, a desulfurization tower 60, a gas holder 70, and a gas engine. 80.
- the crusher 10 and the mixing tank 20 are connected by a pipe 11 that feeds a processed material (raw material), and a raw material pump 12 is inserted into the pipe 11.
- the mixing tank 20 and the solubilization tank 30 are connected by a pipe 21 for sending a processed material (raw material), and an electromagnetic three-way valve 22 is inserted into the pipe 21.
- the solubilization tank 30 and the methane fermentation tank 40 are connected by a pipe 31 for sending a processed material (raw material), and an electromagnetic three-way valve 32 is inserted into the pipe 31.
- the electromagnetic three-way valve 22 and the electromagnetic three-way valve 32 are connected by a pipe 23 for sending a processed material (raw material), and a raw material pump 24 is inserted into the pipe 23.
- the organic waste After the organic waste is put into the crusher 10, it is sent to the methane fermentation tank 40 through the pipe 11, the mixing tank 20, the pipe 21, the solubilization tank 30, and the pipe 31, and after methane fermentation, methane fermentation. It is discharged from the tank 40.
- the discharged processed material is used as compost.
- the methane fermentation tank 40 and the cooling tower 50 are connected by a pipe 51 for sending the generated methane gas.
- the cooling tower 50 and the desulfurization tower 60 are connected by a pipe 52 that sends methane gas.
- the desulfurization tower 60 and the gas holder 70 are connected by a pipe 61 that sends methane gas.
- the gas holder 70 and the gas engine 80 are connected by a pipe 71 that sends methane gas.
- Methane gas generated in the methane fermentation tank 40 is sent in the order of the pipe 51, the cooling tower 50, the pipe 52, the desulfurization tower 60, the pipe 61, the gas holder 70, the pipe 71, and the gas engine 80.
- Organic waste is input to the crusher 10 from the outside.
- the crusher 10 crushes the input organic waste into an appropriate size.
- the pulverized processed product is sent to the mixing tank 20 through the pipe 11 by the raw material pump 12.
- a stirrer is provided inside the mixing tank 20, and the thrown-in organic waste is stirred by the stirrer. Thereby, the organic waste accommodated in the mixing tank 20 is mixed and becomes a uniform state.
- the mixing tank 20 is provided with an ultraviolet irradiation unit.
- An ultraviolet irradiation part irradiates ultraviolet rays in the mixing tank 20 with a light emitting diode (LED), for example.
- the ultraviolet irradiation unit irradiates the processed material put into the mixing tank 20 with ultraviolet light to sterilize the processed material.
- the organic waste sterilized in the mixing tank 20 is sent to the solubilization tank 30 via the pipe 21.
- the solubilization tank 30 performs a solubilization process on the charged processed material.
- the solubilization tank 30 for example, high-temperature solubilization treatment using solubilizing bacteria such as protease-producing bacteria is performed.
- a culture tank 33 is attached to the solubilization tank 30.
- solubilized bacteria are cultured, and the solubilized bacteria are supplied from the culture tank 33 to the solubilization tank 30.
- the culture tank 33 and the UV-LED (ultraviolet irradiation device) 34 are inserted into a water supply pipe 35.
- the water sent from the water supply pipe 35 is sent to the culture tank 33 while being sterilized by the UV-LED 34.
- the culture tank 33 sends water containing the solubilized bacteria to the solubilization tank 30 through the water supply pipe 35.
- the solubilization tank 30 is provided with an inner container 30A for storing a processed product and an outer container 30B provided so as to surround the inner container 30A.
- the processed product to be solubilized is accommodated in the inner container 30A.
- a heat medium is accommodated between the outer container 30B and the inner container 30A. In the present embodiment, hot water is used as the heat medium.
- the temperature in the tank of the solubilization tank 30 is maintained at a high temperature by this heat medium.
- a stirrer and a motor for stirring the organic waste are attached in the tank of the solubilization tank 30, a stirrer and a motor for stirring the organic waste are attached. Further, the solubilization tank 30 is provided with an air insertion port for supplying air to the organic waste, and air pumps 36 and 37 are connected to the air insertion port. Air is sent to the solubilization tank 30 by the air pumps 36 and 37. In this way, in the solubilization tank 30, solubilization is promoted under high temperature aerobicity by performing stirring or aeration.
- High-temperature aerobic means a state in which organic waste is solubilized in a standard state (in an air atmosphere) at a temperature of 50 ° C. to 100 ° C., preferably without applying pressure.
- the solubilization treatment is a treatment for decomposing a normal polymer organic compound in a solid or water suspension into a low molecular state that can be dissolved in water.
- ultrahigh temperature solubilization is performed using protease-producing bacteria.
- protease-producing bacteria are bacteria that can produce and secrete proteolytic enzymes (proteases) outside the cells.
- protease-producing bacteria examples include Bacillus species, and in particular, Bacillus sp. MU3 (Microbial Patent Deposit Center NITE AP-156).
- Bacillus species and in particular, Bacillus sp. MU3 (Microbial Patent Deposit Center NITE AP-156).
- This heat-resistant protease-producing bacterium has an ultra-high temperature aerobic property that can sufficiently act even at 80 ° C.
- the enzyme produced by this bacterium has a molecular weight of about 57,000, excellent heat resistance, and high protein resolution in a wide pH range.
- the ultra-high temperature is 50 ° C. to 100 ° C., preferably 60 ° C. to 90 ° C., particularly preferably 70 ° C. to 80 ° C.
- Ultra-high temperature solubilization is carried out in an aqueous medium under an aerobic or anaerobic condition, preferably an aerobic condition, and the organic waste has an organic waste concentration of 50 wt% or less, preferably 5 to 40 wt%, particularly preferably. It is carried out in contact with a protease-producing bacterium in such an amount that it becomes 10 to 30 wt%.
- the solids concentration (DS) of the raw material can be increased to an organic waste concentration of 10 to 30 wt%, preferably at a DS of 20% or more, pH 5 to 8, preferably around 6.
- the solubilization tank atmosphere is optimally aerobic.
- the time for digestion with protease-producing bacteria is 12 to 72 hours, preferably 24 to 48 hours.
- it can be carried out under stirring and aeration conditions.
- ammonia can be removed in situ, solubilization of the raw material and ammonia removal can be performed simultaneously, and methane fermentation can be promoted.
- Bacillus sp. When MU3 is used as a protease-producing bacterium, since this bacterium is an aerobic thermostable bacterium, it can be solubilized with stirring while being aerated with air, and is optimal in terms of solubilization and ammonia removal.
- microbial cells producing various degrading enzymes such as lipase-producing bacteria, glycosidase-producing bacteria and / or cellulase-producing bacteria may be added alone or in combination. Is possible. These can be used in the same reaction tank as long as the growth and proliferation conditions are similar, but if the conditions are different, a plurality of solubilization tanks 30 are provided, and each solubilization tank 30 is provided under different conditions. Can be used.
- solubilize in a high-temperature solubilization tank using a protease-producing bacterium it is preferable to solubilize in a high-temperature solubilization tank using a protease-producing bacterium.
- An ammonia adsorption tank 38 is connected to the solubilization tank 30.
- the ammonia adsorption tank 38 is provided for adsorbing and removing ammonia generated in the solubilization process in the solubilization tank 30.
- the processed product solubilized in the solubilization tank 30 is sent to the methane fermentation tank 40 via the pipe 31.
- the methane fermentation tank 40 performs a methane fermentation process on the stored processed product.
- Methane fermentation treatment uses methane bacteria that normally operate in an anaerobic atmosphere and uses its digestive action.
- the active temperature range of methane bacteria is usually from 0 to 70 ° C., and in higher temperature ranges there are some species that survive to about 90 ° C., but almost die. In the low temperature region, the limit is 3 ° C to 4 ° C.
- the methane gas production rate is greatly influenced by this activation temperature.
- the gas generation rate proceeds faster as the fermenter temperature is higher, and the amount of gas generated increases.
- the following three temperature regions where methane bacteria are actually liable to live have been confirmed.
- the temperature of the methane fermentation of the present invention can be any of low temperature, medium temperature and high temperature methane fermentation, but it is preferable to perform high temperature methane fermentation at 40 ° C to 70 ° C, and further methane fermentation at 50 ° C to 55 ° C. Is preferred.
- the solubilization treatment can be performed under high-temperature aerobic conditions and the methane fermentation treatment can be performed under anaerobic conditions
- methane fermentation can be performed using the high temperature of the solubilization treatment.
- the temperature of the soda can be increased, and the bacteria growth condition has the advantage that the bacteria in the solubilization treatment (aerobic condition) are inactivated in the methane fermentation process (anaerobic condition), so that the methane fermentation is not disturbed. .
- the high-temperature aerobic property means a state in which organic waste is solubilized in a standard state (in an air atmosphere) at a temperature of 50 to 100 ° C., preferably without applying pressure.
- the methane fermentation tank 40 is divided into a first tank 40A, a second tank 40B, and a third tank 40C.
- the processed material input from the outside is first input to the first tank 40A, where methane fermentation proceeds.
- the methane fermentation of about 95% of the processed product is completed.
- the specific gravity of the processed product becomes lighter, so it goes up and is sent to the second tank 40B over the side wall.
- the methane fermentation is also performed in the second tank 40B, and the processed product is sent to the third tank 40C to the extent that the remaining 1.2 to 2% of the untreated product remains, that is, the methane fermentation is almost completed.
- Methane fermentation is also performed in the third tank 40C. Methane fermentation is complete.
- the processed product for which methane fermentation has been completed is discharged from the third tank 40C to the outside.
- the methane fermentation tank 40 is provided with a gas circulation unit 40D that circulates gas by collecting gas (methane gas and carbon dioxide) generated by methane fermentation, taking it out and returning it to the inside.
- the gas circulation unit 40D is provided with a pipe 41 and a blower 42 for sending gas. The methane gas generated in the methane fermentation tank 40 by the blower 42 is sent to the pipe 41 and returned to the methane fermentation tank 40.
- a cylindrical body 4 is erected on the bottom surface of the methane fermentation tank 40.
- a plurality of openings 4 ⁇ / b> A are provided on the lower side surface of the cylindrical body 4, and an opening 4 ⁇ / b> B is provided on the upper end of the cylindrical body 4.
- the tip 41A of the pipe 41 extends to the center of the bottom surface in the cylindrical body 4, and the gas is discharged from the opening (first outlet) of the tip 41A.
- the gas discharged from the tip 41A of the pipe 41 rises in the cylindrical body 4. Due to the rising flow of the gas, the processed product 6 in the cylindrical body 4 also starts to rise. Then, the processed material 6 can flow from the outside to the inside of the cylindrical body 4 at the opening 4A, and the processed material can flow from the inside to the outside of the cylindrical body 4 at the opening 4B. Thereby, the flow of the upper and lower circulation of a processed material is formed inside the methane fermentation tank 40, and the processed material 6 is stirred.
- the gas discharged from the tip 41A of the pipe 41 is a mixed gas of methane gas and carbon dioxide.
- this gas is discharged into the treated product 6, carbon dioxide is absorbed by the treated product 6, so that the ratio of methane gas can be improved.
- the ratio of methane gas increases, the power generation efficiency in the gas engine 80 can be increased.
- ammonia gas can be suppressed by supplying carbon dioxide to the treated product 6. Since ammonia gas inhibits methane fermentation, methane fermentation can be promoted by supplying carbon dioxide to the treated product 6.
- the methane fermentation tank 40 is provided with a processed product circulation section 40E that circulates the processed product 6 by collecting the processed product 6 and returning it to the inside.
- the treated product circulation unit 40E includes a pipe 43, a raw material pump 44, and electromagnetic three-way valves 45 and 46.
- the raw material pump 44 is inserted into the pipe 43.
- the processed product 6 discharged from the methane fermentation tank 40 by the raw material pump 44 is returned to the methane fermentation tank 40 via the pipe 43.
- the electromagnetic three-way valve 45 branches the pipe 43.
- the electromagnetic three-way valve 46 connects the crusher 10 and the pipe 43 via the pipe 13.
- a heat exchanger 47 is inserted into the pipe 43.
- the outflow port 5 (2nd outflow port) which flows out the processed material 6 sent in the piping 43 is an upper surface of the processed material in the methane fermentation tank 40, Comprising: Methane fermentation It is attached to the upper corner of a solid (cuboid) formed by the processed product 6 in the tank 40. Furthermore, the outflow port 5 faces the direction of the diagonal line of the solid (cuboid) formed by the processed object 6, that is, the direction of the center point of the solid.
- the processed product 6 in the methane fermentation tank 40 forms a flow as shown in FIGS. 3A and 3B, so that the entire processed product 6 is stirred. become.
- the stirring by the gas was stirring in the vertical direction, but the stirring by the flow of the processed product 6 includes a horizontal flow.
- the treated product 6 is generally stirred by the flow of FIGS. 3A and 3B, but a place where the treated product 6 stays appears in a part of the tank. Therefore, in the present embodiment, as shown in FIG. 4, if a mechanism for blowing out the gas composed of the cylindrical body 4 shown in FIGS. Uneven processing due to retention of 6 can be prevented.
- the gas generated in the methane fermentation tank 40 is sent to the cooling tower 50 to be cooled and output to the desulfurization tower 60.
- the desulfurization tower 60 performs a desulfurization process on the input gas, and outputs the extracted methane gas to the gas holder 70.
- the gas holder 70 stores methane gas.
- the gas engine 80 generates electricity by turning a gas turbine with methane gas sent from the gas holder 70.
- the electric power generated by the gas engine 80 is sent to a cubicle (power receiving facility) via the power line 81.
- the gas engine 80 generates heat by power generation. For this reason, a pipe 82 for flowing hot water and a cold / hot water pump 83 are provided between the gas engine 80 and the heat exchanger 84 so that the heat of the gas engine 80 is sent to the heat exchanger 84. It has become.
- the heat exchanger 84 is connected to the throwing heater 90 and the pipe 85. Thereby, the heat of the gas engine 80 is transmitted to the throwing heater 90 via the heat exchanger 84.
- a piping path for the heat medium is constructed between the throwing heater 90, the solubilization tank 30, and the heat exchanger 47.
- the heat medium heated by the throwing heater 90 is sent from the solubilization tank 30 to the heat exchanger 47 while returning to a throwing heater 90 from the heat exchanger 47 while keeping the temperature in the solubilization tank 30 constant.
- This heat medium circulation path is defined as a heat medium circulation section.
- the heat exchanger 47 performs heat exchange between the heat medium circulating in the heat medium circulation unit and the processed material circulating in the processed material circulation unit 40E.
- the processed product 6 heated by the heat exchanger 47 returns to the methane fermentation tank 40, and further methane fermentation is performed at a temperature with high fermentation efficiency.
- the temperature of the processed material fermented in the methane fermentation tank 40 is kept uniform, and is maintained so that the methane fermentation efficiency by the fermenting bacteria does not decrease.
- the processed product is pulverized by the crusher 10, stirred and sterilized in the mixing tank 20, solubilized in the solubilizing tank 30, and then subjected to methane fermentation in the methane fermentation tank 40.
- the methane fermentation tank 40 is divided into a first tank 40A, a second tank 40B, and a third tank 40C, and unprocessed products disappear while being sent to the lower processing tank.
- the processed product is stirred and the carbon dioxide is adsorbed by the gas circulating unit 40D and the processed product circulating unit 40E, methane fermentation is performed, and methane gas is generated. Methane gas is accumulated in the gas holder 70 and used for power generation in the gas engine 80.
- the heat generated in the gas engine 80 is used to keep the solubilization tank 30 through the heat exchanger 84 ⁇ the throwing heater 90, and is further used to keep the processed material 6 through the heat exchanger 47.
- the processed product that has been processed in the methane fermentation tank 40 is discharged from the methane fermentation tank 40.
- the discharged processed material can be used as compost. Since all processed products are processed, they do not smell rotten.
- the methane fermentation tank 40 is divided into three or more stages, and the methane fermentation is performed while the processed products are being conveyed to the lower processing tanks 40B and 40C. Since there is no unprocessed unprocessed material left, discharge of unprocessed material can be prevented. Moreover, since the flow of a processed material can be created on the diagonal in the methane fermentation tank 40, the processed material 6 in a tank can be equalize
- processing tank of the methane fermentation tank 40 was made into 3 steps
- each processing tank 40A, 40B, 40C of the methane fermentation tank 40 was made into the rectangular parallelepiped, this invention is not limited to this, For example, a cylindrical shape may be sufficient. In this case, what is necessary is just to make the outflow port 5 face the center of the processed material 6.
- FIG. 1 is a diagrammatic representation of the methane fermentation tank 40.
- the outlet 5 does not have to face the center of the processed product 6.
- the outlet 5 ′ is directed to the circumferential direction of the inner wall of the cylindrical methane fermentation tank (first tank) 40A ′. May be.
- the opening of the tip 41A of the pipe 41 and the cylindrical body 4 may be arranged at the center of the bottom surface of the methane fermentation tank (first tank) 40A '.
- the cylindrical body 4 is installed in the first tank 40A, but the cylindrical body 4 may be installed in the second tank 40B and the third tank 40C.
- the gas circulation unit 40D and the processed product circulation unit 40E are illustrated as circulating gas or processed material from the third tank 40C to the first tank 40A, but the first tank 40A, Gas and processed material may be circulated in the second tank 40B and the third tank 40C, respectively.
- the present invention can be applied to a methane fermentation apparatus that performs methane fermentation.
Landscapes
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Health & Medical Sciences (AREA)
- Molecular Biology (AREA)
- Hydrology & Water Resources (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Processing Of Solid Wastes (AREA)
- Treatment Of Sludge (AREA)
Abstract
Description
乾式のメタン発酵装置であって、
3つ以上の処理槽に分割され、最上槽に投入された処理物が、より下段の処理槽に順次送られる間に、前記処理物を発酵させてメタンガスを発生させるメタン発酵槽を備え、
前記メタン発酵槽は、
槽内底面にある処理物を回収し、槽内の処理物によって形づくられる立体の上側縁部に設けられた第1の流出口から槽内に処理物を吹き出す処理物循環部を備え、
前記第1の流出口が、前記立体の中心を向いている。 In order to achieve the above object, a methane fermentation apparatus according to the first aspect of the present invention comprises:
A dry methane fermentation device,
A methane fermentation tank that ferments the processed material to generate methane gas while the processed material that is divided into three or more processing tanks and is put into the uppermost tank is sequentially sent to the lower processing tank,
The methane fermenter is
The processing object which collects the processing thing in the bottom face in a tank, and is equipped with the processing thing circulation part which blows off the processing substance in the tank from the 1st outflow port provided in the solid upper edge formed by the processing thing in a tank,
The first outflow port faces the center of the solid.
槽内で発生したガスを回収し、槽内底部に設けられた第2の流出口から槽内に吹き出すガス循環部を備える、
こととしてもよい。 In this case, in the methane fermentation tank,
A gas circulation part that recovers the gas generated in the tank and blows out into the tank from the second outlet provided in the bottom of the tank,
It is good as well.
前記第2の流出口を囲むように槽内底面に立設され、下部側面及び上面が開放された円筒体を備える、
こととしてもよい。 The gas circulation part
A cylindrical body that is erected on the bottom surface in the tank so as to surround the second outflow port, and whose lower side surface and upper surface are opened;
It is good as well.
前記第1の流出口から流出する処理物により槽内に形成される処理物の流れにおいて、前記処理物が滞留する場所に配置されている、
こととしてもよい。 The second outlet and the cylindrical body are:
In the flow of the processed material formed in the tank by the processed material flowing out from the first outlet, it is disposed at a place where the processed material stays.
It is good as well.
前記メタン発酵槽で発生したメタンガスを用いて発電を行うガスエンジンの熱を処理物に伝える熱交換器を備える、
こととしてもよい。 The treated product circulation part is:
A heat exchanger that transmits heat of a gas engine that generates power using methane gas generated in the methane fermentation tank to a processed product,
It is good as well.
乾式のメタン発酵装置であって、
3つ以上の処理槽に分割され、最上槽に投入された処理物が、より下段の処理槽に順次送られる間に、前記処理物を発酵させてメタンガスを発生させるメタン発酵槽を備え、
前記メタン発酵槽は、
槽内で発生したガスを回収し、槽内底部に設けられた流出口から槽内に吹き出すガス循環部を備える。 The methane fermentation apparatus according to the second aspect of the present invention,
A dry methane fermentation device,
A methane fermentation tank that ferments the processed material to generate methane gas while the processed material that is divided into three or more processing tanks and is put into the uppermost tank is sequentially sent to the lower processing tank,
The methane fermenter is
A gas circulation unit is provided that collects gas generated in the tank and blows out the gas from an outlet provided in the bottom of the tank.
前記流出口を囲むように前記メタン発酵槽内の底面に立設され、下部側面及び上面が開放された円筒体を備える、
こととしてもよい。 In this case, the gas circulation unit
A cylindrical body that is erected on the bottom surface in the methane fermentation tank so as to surround the outlet and has a lower side surface and an upper surface opened,
It is good as well.
Claims (7)
- 乾式のメタン発酵装置であって、
3つ以上の処理槽に分割され、最上槽に投入された処理物が、より下段の処理槽に順次送られる間に、前記処理物を発酵させてメタンガスを発生させるメタン発酵槽を備え、
前記メタン発酵槽は、
槽内底面にある処理物を回収し、槽内の処理物によって形づくられる立体の上側縁部に設けられた第1の流出口から槽内に処理物を吹き出す処理物循環部を備え、
前記第1の流出口が、前記立体の中心を向いている、
メタン発酵装置。 A dry methane fermentation device,
A methane fermentation tank that ferments the processed material to generate methane gas while the processed material that is divided into three or more processing tanks and is put into the uppermost tank is sequentially sent to the lower processing tank,
The methane fermenter is
The processing object which collects the processing thing in the bottom face in a tank, and is equipped with the processing thing circulation part which blows off the processing substance in the tank from the 1st outflow port provided in the solid upper edge formed by the processing thing in a tank,
The first outlet faces the center of the solid;
Methane fermentation equipment. - 前記メタン発酵槽は、
槽内で発生したガスを回収し、槽内底部に設けられた第2の流出口から槽内に吹き出すガス循環部を備える、
請求項1に記載のメタン発酵装置。 The methane fermenter is
A gas circulation part that recovers the gas generated in the tank and blows out into the tank from the second outlet provided in the bottom of the tank,
The methane fermentation apparatus according to claim 1. - 前記ガス循環部は、
前記第2の流出口を囲むように槽内底面に立設され、下部側面及び上面が開放された円筒体を備える、
請求項2に記載のメタン発酵装置。 The gas circulation part
A cylindrical body that is erected on the bottom surface in the tank so as to surround the second outflow port, and whose lower side surface and upper surface are opened;
The methane fermentation apparatus according to claim 2. - 前記第2の流出口及び前記円筒体は、
前記第1の流出口から流出する処理物により槽内に形成される処理物の流れにおいて、前記処理物が滞留する場所に配置されている、
請求項3に記載のメタン発酵装置。 The second outlet and the cylindrical body are:
In the flow of the processed material formed in the tank by the processed material flowing out from the first outlet, it is disposed at a place where the processed material stays.
The methane fermentation apparatus according to claim 3. - 前記処理物循環部は、
前記メタン発酵槽で発生したメタンガスを用いて発電を行うガスエンジンの熱を処理物に伝える熱交換器を備える、
請求項1から4のいずれか一項に記載のメタン発酵装置。 The treated product circulation part is:
A heat exchanger that transmits heat of a gas engine that generates power using methane gas generated in the methane fermentation tank to a processed product,
The methane fermentation apparatus as described in any one of Claim 1 to 4. - 乾式のメタン発酵装置であって、
3つ以上の処理槽に分割され、最上槽に投入された処理物が、より下段の処理槽に順次送られる間に、前記処理物を発酵させてメタンガスを発生させるメタン発酵槽を備え、
前記メタン発酵槽は、
槽内で発生したガスを回収し、槽内底部に設けられた流出口から槽内に吹き出すガス循環部を備える、
メタン発酵装置。 A dry methane fermentation device,
A methane fermentation tank that ferments the processed material to generate methane gas while the processed material that is divided into three or more processing tanks and is put into the uppermost tank is sequentially sent to the lower processing tank,
The methane fermenter is
The gas generated in the tank is collected, and a gas circulation part that blows out into the tank from the outlet provided in the bottom of the tank is provided.
Methane fermentation equipment. - 前記ガス循環部は、
前記流出口を囲むように前記メタン発酵槽内の底面に立設され、下部側面及び上面が開放された円筒体を備える、
請求項6に記載のメタン発酵装置。 The gas circulation part
A cylindrical body that is erected on the bottom surface in the methane fermentation tank so as to surround the outlet and has a lower side surface and an upper surface opened,
The methane fermentation apparatus according to claim 6.
Priority Applications (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR1020187032435A KR20180128060A (en) | 2016-05-24 | 2017-03-01 | Methane fermentation device |
CN201780025113.9A CN109071292A (en) | 2016-05-24 | 2017-03-01 | Methane fermentation device |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2016-103446 | 2016-05-24 | ||
JP2016103446A JP2017209614A (en) | 2016-05-24 | 2016-05-24 | Methane fermentation apparatus |
Publications (1)
Publication Number | Publication Date |
---|---|
WO2017203781A1 true WO2017203781A1 (en) | 2017-11-30 |
Family
ID=60412311
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
PCT/JP2017/008127 WO2017203781A1 (en) | 2016-05-24 | 2017-03-01 | Methane fermentation device |
Country Status (5)
Country | Link |
---|---|
JP (1) | JP2017209614A (en) |
KR (1) | KR20180128060A (en) |
CN (1) | CN109071292A (en) |
TW (1) | TW201741449A (en) |
WO (1) | WO2017203781A1 (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108359595A (en) * | 2018-04-20 | 2018-08-03 | 郑晓梅 | A kind of biofermentation reaction unit |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
TWM591523U (en) * | 2019-07-10 | 2020-03-01 | 業興環境科技股份有限公司 | Anaerobic fermentation system |
Citations (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS56108593A (en) * | 1980-01-31 | 1981-08-28 | Matsushita Electric Works Ltd | Methane fermentation apparatus |
JPS57127499A (en) * | 1981-01-26 | 1982-08-07 | Takuma Sogo Kenkyusho:Kk | Anaerobic digestion tank device |
JPS60150900A (en) * | 1984-01-17 | 1985-08-08 | Shinryo Air Conditioning Co Ltd | Anaerobic digester |
JPS60202798A (en) * | 1984-03-27 | 1985-10-14 | Agency Of Ind Science & Technol | Methane fermentation apparatus utilizing composite local recirculation |
JP2003088840A (en) * | 2001-09-20 | 2003-03-25 | Nobuhiko Kato | Fermentation equipment for organic waste |
JP2004017024A (en) * | 2002-06-20 | 2004-01-22 | Kurita Water Ind Ltd | Dry type methane fermentation method and dry type methane fermentation apparatus |
JP2011083761A (en) * | 2009-10-19 | 2011-04-28 | Nagasaki Institute Of Applied Science | Methane fermentation treatment method of organic waste |
JP2012510264A (en) * | 2008-12-01 | 2012-05-10 | ベーコン・エナジー・テクノロジーズ・ジーエムビーエイチ・アンド・シーオー.ケージー | Method for reducing methane slack at the start and stop of a biogas fermenter, and biogas system for carrying out this method |
JP2012236115A (en) * | 2011-05-09 | 2012-12-06 | Eco Power Corp | Methane fermentation system |
JP2015217322A (en) * | 2014-05-14 | 2015-12-07 | 活水プラント株式会社 | Methane fermentation apparatus and treatment method of water-containing organic waste |
Family Cites Families (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2007130510A (en) * | 2002-03-12 | 2007-05-31 | Toshiro Sekine | Stirring method for methane fermentation tank and methane fermentation apparatus |
EP1818315A1 (en) * | 2006-02-07 | 2007-08-15 | Reinhart Dr.-Ing. Von Nordenskjöld | Dynamic micromixer |
CN202440509U (en) * | 2012-03-01 | 2012-09-19 | 许鉴峰 | Gas stripping convective circulation anaerobic digestion reactor |
KR101908723B1 (en) * | 2014-03-27 | 2018-12-19 | 대한민국 | cell type anerobic digestion system using dry and wet wast |
CN104277968A (en) * | 2014-10-22 | 2015-01-14 | 山东宝力生物质能源股份有限公司 | Large-scale biogas hydraulic-circulating even mixing device |
-
2016
- 2016-05-24 JP JP2016103446A patent/JP2017209614A/en active Pending
-
2017
- 2017-03-01 CN CN201780025113.9A patent/CN109071292A/en active Pending
- 2017-03-01 WO PCT/JP2017/008127 patent/WO2017203781A1/en active Application Filing
- 2017-03-01 KR KR1020187032435A patent/KR20180128060A/en not_active Application Discontinuation
- 2017-05-12 TW TW106115788A patent/TW201741449A/en unknown
Patent Citations (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS56108593A (en) * | 1980-01-31 | 1981-08-28 | Matsushita Electric Works Ltd | Methane fermentation apparatus |
JPS57127499A (en) * | 1981-01-26 | 1982-08-07 | Takuma Sogo Kenkyusho:Kk | Anaerobic digestion tank device |
JPS60150900A (en) * | 1984-01-17 | 1985-08-08 | Shinryo Air Conditioning Co Ltd | Anaerobic digester |
JPS60202798A (en) * | 1984-03-27 | 1985-10-14 | Agency Of Ind Science & Technol | Methane fermentation apparatus utilizing composite local recirculation |
JP2003088840A (en) * | 2001-09-20 | 2003-03-25 | Nobuhiko Kato | Fermentation equipment for organic waste |
JP2004017024A (en) * | 2002-06-20 | 2004-01-22 | Kurita Water Ind Ltd | Dry type methane fermentation method and dry type methane fermentation apparatus |
JP2012510264A (en) * | 2008-12-01 | 2012-05-10 | ベーコン・エナジー・テクノロジーズ・ジーエムビーエイチ・アンド・シーオー.ケージー | Method for reducing methane slack at the start and stop of a biogas fermenter, and biogas system for carrying out this method |
JP2011083761A (en) * | 2009-10-19 | 2011-04-28 | Nagasaki Institute Of Applied Science | Methane fermentation treatment method of organic waste |
JP2012236115A (en) * | 2011-05-09 | 2012-12-06 | Eco Power Corp | Methane fermentation system |
JP2015217322A (en) * | 2014-05-14 | 2015-12-07 | 活水プラント株式会社 | Methane fermentation apparatus and treatment method of water-containing organic waste |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108359595A (en) * | 2018-04-20 | 2018-08-03 | 郑晓梅 | A kind of biofermentation reaction unit |
Also Published As
Publication number | Publication date |
---|---|
JP2017209614A (en) | 2017-11-30 |
TW201741449A (en) | 2017-12-01 |
KR20180128060A (en) | 2018-11-30 |
CN109071292A (en) | 2018-12-21 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Ahring | Perspectives for anaerobic digestion | |
KR100845614B1 (en) | Concept for slurry separation and biogas production | |
JP2009254341A (en) | Device of sterilizing mushroom culture medium, and production system for producing mushroom culture medium | |
JP4221617B2 (en) | Animal and plant residue dry fermented feed, dry fertilizer, etc. | |
WO2019044995A1 (en) | Apparatus and method for treating organic matter including harmful microorganisms | |
WO2017203781A1 (en) | Methane fermentation device | |
WO2017163602A1 (en) | Methane fermentation system | |
JP2012050917A (en) | Ammonia removing device | |
JP5491046B2 (en) | Methane fermentation system and fertilizer production equipment using the same | |
JP5030722B2 (en) | Methane fermentation method | |
US9670106B2 (en) | Pressurised recirculation of organic material | |
JP2016203153A (en) | Method for manufacturing methane from organic waste | |
JP2008023450A (en) | Apparatus and method for decomposing organic waste | |
CN112955410A (en) | Livestock excrement treatment device and treatment method thereof | |
JP2011031217A (en) | Organic waste treatment method, method for culturing compound microbe colony having organic matter decomposition activity, and culture medium containing compound microbe colony cultured therein | |
JP2011083761A (en) | Methane fermentation treatment method of organic waste | |
Fubin et al. | Performance of alkaline pretreatment on pathogens inactivation and sludge solubilization | |
JP7083160B2 (en) | Digestive juice processing device and its processing method in methane fermentation of organic matter | |
CN107074600A (en) | Solubilized device | |
KR102597101B1 (en) | Treating organic waste apparatus being eco-friendly adn treating method thereof | |
JP4557541B2 (en) | Organic waste accumulation-free treatment system and treatment method thereof | |
JP2004230250A (en) | Treatment system for organic waste | |
JP5761922B2 (en) | Methane fermentation system | |
JP5284324B2 (en) | Ammonia removal equipment | |
JP2001321799A (en) | Organic matter liquefying fermentation treatment apparatus |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
ENP | Entry into the national phase |
Ref document number: 20187032435 Country of ref document: KR Kind code of ref document: A |
|
NENP | Non-entry into the national phase |
Ref country code: DE |
|
121 | Ep: the epo has been informed by wipo that ep was designated in this application |
Ref document number: 17802383 Country of ref document: EP Kind code of ref document: A1 |
|
32PN | Ep: public notification in the ep bulletin as address of the adressee cannot be established |
Free format text: NOTING OF LOSS OF RIGHTS PURSUANT TO RULE 112(1) EPC (EPO FORM 1205 DATED 22/02/2019) |
|
122 | Ep: pct application non-entry in european phase |
Ref document number: 17802383 Country of ref document: EP Kind code of ref document: A1 |