WO2020137986A1 - Deodorization device in treatment apparatus for organic matter-containing substance to be treated, and deodorization method for deodorization device - Google Patents

Deodorization device in treatment apparatus for organic matter-containing substance to be treated, and deodorization method for deodorization device Download PDF

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Publication number
WO2020137986A1
WO2020137986A1 PCT/JP2019/050390 JP2019050390W WO2020137986A1 WO 2020137986 A1 WO2020137986 A1 WO 2020137986A1 JP 2019050390 W JP2019050390 W JP 2019050390W WO 2020137986 A1 WO2020137986 A1 WO 2020137986A1
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Prior art keywords
chlorine
deodorizing
organic matter
cooler
water
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PCT/JP2019/050390
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French (fr)
Japanese (ja)
Inventor
眞一 下瀬
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株式会社下瀬微生物研究所
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Publication of WO2020137986A1 publication Critical patent/WO2020137986A1/en

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    • AHUMAN NECESSITIES
    • A61MEDICAL OR VETERINARY SCIENCE; HYGIENE
    • A61LMETHODS OR APPARATUS FOR STERILISING MATERIALS OR OBJECTS IN GENERAL; DISINFECTION, STERILISATION OR DEODORISATION OF AIR; CHEMICAL ASPECTS OF BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES; MATERIALS FOR BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES
    • A61L9/00Disinfection, sterilisation or deodorisation of air
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless

Definitions

  • the present invention relates to a deodorizing device and a deodorizing method thereof in a processing device for a processing object containing an organic substance.
  • Patent Document 1 stores an object to be treated containing an organic substance in a closed container such as a tank, and stirs it while heating it to a predetermined temperature range under reduced pressure, thereby improving efficiency.
  • a patent application has been filed for a reduced-pressure fermentation drying device capable of accelerating the fermentation of organic substances by adding predetermined microorganisms to an object to be treated containing organic substances while drying and removing water.
  • this vacuum fermentation drying device has the function of decomposing the microorganisms that are the source of the bad odor by using microorganisms, but the entire building where the processing equipment including the vacuum fermentation drying device is installed is installed. There is a problem that it does not have the ability to deodorize a bad odor, and a bad odor is generated from an object to be treated containing organic substances such as municipal solids scattered in the building.
  • the present invention has been made in consideration of the above-mentioned circumstances, and is an apparatus and a processing method for deodorizing a bad odor in an entire building in which a processing apparatus including a vacuum fermentation drying apparatus is installed.
  • the present invention has the following means for solving the above-mentioned problems. That is, the present invention is a method of accommodating an object to be treated containing an organic matter in a closed container and stirring while heating under a reduced pressure to a predetermined temperature range, decomposing the organic component of the organic matter by using a microorganism, and reducing the volume of the dried product.
  • a reduced pressure fermentation drying apparatus for obtaining a product, a cooler connected to the condenser of the closed container via a vacuum pump, and a cooling water circulation path for circulating cooling water between the condenser and the cooler via a cooling water pump.
  • a chlorine-based deodorizing gas diffusion mechanism attached to the cooler.
  • chlorine-based deodorized water can decompose malodorous components such as ammonia. Therefore, a bad odor is hardly generated from the building in which the apparatus for treating the object to be treated including the organic matter is installed.
  • the chlorine-based deodorant gas diffusion mechanism is a water-receiving tank of the cooler, a pipe having one end connected to the water-receiving tank, and a chlorine-based deodorant having the other end of the pipe connected via a chemical pump.
  • a deodorizing device in a treatment device for an object to be treated containing an organic substance which is composed of a water storage container, and sprays cooling water containing chlorine-based deodorizing water in a water receiving tank from a nozzle via a pump,
  • the cooling water flows down, the chlorine-based deodorized water dissolved in the cooling water is gasified (hereinafter, also referred to as "chlorine-based deodorizing gas"), and this chlorine-based deodorizing gas is blown from the fan of the cooler, thereby
  • the deodorizing gas is diffused throughout the building where the processing device is installed to decompose a malodorous component such as ammonia to deodorize the malodorous substance.
  • the chlorine-based deodorizing gas diffusion mechanism includes a spray nozzle arranged near an outside of the fan of the cooler, a pipe having one end connected to the spray nozzle, and the other end of the pipe being a chemical pump.
  • Chlorine deodorized water sprayed from the nozzle is gasified by the air blow of the fan of the cooler and these chlorine deodorized gases are diffused throughout the building in which the processing device is installed, and these chlorine deodorized gases are malodorous components, for example, It decomposes ammonia and deodorizes odors.
  • the chlorine-based deodorizing gas diffusion mechanism has a first pipe whose one end is opened near the outside of the fan of the cooler and the other end is opened above the inside of the chlorine-based deodorized water storage container, and one end is a compressor. And a second pipe connected to the other end so as to enter the inside of the chlorine-based deodorizing aqueous solution accommodated in the accommodating container. It is a deodorizing device, and when the compressor is driven, the chlorine deodorizing aqueous solution in the chlorine deodorizing water storage container is aerated, and the chlorine deodorizing gas generated here passes through the first pipe. Combined with the air blow of the fan, the chlorine-based deodorizing gas is diffused throughout the building where the processing device is installed to decompose a malodorous component such as ammonia to deodorize the malodor.
  • a malodorous component such as ammonia to deodorize the malodor.
  • the chlorine-based deodorant gas diffusion mechanism is a pan provided in the vicinity of the fan outside of the cooler, a chlorine-based deodorized water storage container connected to the pan via a chemical liquid pump, and the pan.
  • a deodorizing device in a treatment device for an object to be treated containing an organic substance characterized by comprising a heater arranged on the back surface of the bottom, and by heating the chlorine-based deodorized water supplied to the pan with the heater, chlorine is generated.
  • the system deodorizing water is gasified, and the chlorine-based deodorizing gas is diffused throughout the building by the fan of the cooler to decompose a malodorous component such as ammonia to deodorize the malodor.
  • the chlorine-based deodorant gas diffusion mechanism has a first pipe having one end opened near the fan of the cooler and the other end connected to the ejection port of the ejector, and one end connected to the chlorine-based deodorized water storage container. And a second pipe having the other end connected to the chlorine-based deodorized water supply port of the ejector, and a third pipe having one end connected to the compressor and the other end connected to the air introduction port of the ejector.
  • the fan of the cooler diffuses the chlorine-based deodorizing gas throughout the building to decompose a malodorous component such as ammonia to deodorize the malodor.
  • the concentration of the chlorine-based deodorized water is 50 to 5000 mg/L, and the chlorine-based deodorized water has a deodorizing effect. It also has a bactericidal action, and at this concentration, it has no effect on the human body and is harmless.
  • the object to be treated containing an organic matter is housed in a closed container and stirred while heating under a reduced pressure to a predetermined temperature range, and the organic component of the organic matter is decomposed by utilizing microorganisms to reduce the volume.
  • a reduced pressure fermentation drying step of obtaining a dried product a cooling step connected through a condensing step of the closed container, a cooling water circulation step of circulating cooling water between the condensing step and the cooling step, and a cooling step attached to the cooling step.
  • the deodorizing apparatus and its deodorizing method in the processing apparatus for treating an object containing an organic substance according to the present invention in addition to being able to deodorize the inside of the reduced pressure fermentation drying apparatus, in a building where a processing apparatus including the reduced pressure fermentation drying apparatus is installed. It is possible to decompose the malodorous components generated from the object to be treated including the scattered organic matter, such as ammonia, and to deodorize the malodors in the entire building.
  • FIG. 1 is a front view showing a charging device, a reduced pressure fermentation and drying device, a foreign matter sorter, and the like in a treatment device for a treatment object containing an organic substance according to the first embodiment of the present invention. It is a side view which shows the charging device of FIG. 1, a reduced pressure fermentation drying device, a foreign material sorter, etc. It is a figure which shows typically the schematic structure of the deodorizing apparatus of the reduced pressure fermentation drying apparatus of FIG. It is a perspective view which shows schematic structure of the foreign material selection machine of FIG. It is a figure which shows typically the schematic structure of the deodorizing apparatus of the reduced pressure fermentation drying apparatus in the processing apparatus of the to-be-processed object containing the organic substance which concerns on 2nd Embodiment of this invention.
  • FIG. 1 is a front view showing a charging device, a reduced pressure fermentation drying device, a foreign matter selector, and the like in a processing device for a processing object containing an organic substance according to an embodiment of the present invention
  • FIG. 2 is a charging device of the processing device.
  • FIG. 4 is a side view showing a reduced pressure fermentation drying apparatus, a foreign matter sorter, etc.
  • FIG. 3 is a diagram schematically showing a schematic configuration of a reduced pressure fermentation drying apparatus of the processing apparatus
  • FIG. 4 is a foreign matter of the processing apparatus. It is a perspective view showing a schematic structure of a sorting machine.
  • a treatment device 1 for an object to be treated containing an organic substance includes a charging device 2, a reduced pressure fermentation drying device 3, a foreign matter selector 4, and the like. ing.
  • a processing apparatus 1 for example, an object to be processed containing organic matter such as municipal solid waste is put into the reduced pressure fermentation and drying apparatus 3 by the inputting apparatus 2, and the input object to be processed is reduced pressure fermentation and drying by the reduced pressure fermentation and drying apparatus 3. The process is executed.
  • the dried product obtained by the reduced pressure fermentation and drying process of the reduced pressure fermentation drying device 3 is sent to the foreign matter selector 4 by the discharge conveyor 41, and the foreign matter mixed in the dried matter is removed by the foreign matter selector 4.
  • FIG. 2 for example, the processing apparatus 1 installed in the building A is shown, and a charging device 2, a reduced pressure fermentation drying device 3, a foreign matter selector 4, etc. are installed in predetermined positions in the building A. ..
  • a charging device 2 for example, the processing apparatus 1 installed in the building A is shown, and a charging device 2, a reduced pressure fermentation drying device 3, a foreign matter selector 4, etc. are installed in predetermined positions in the building A. ..
  • a charging device 2 for example, a reduced pressure fermentation drying device 3, a foreign matter selector 4, etc.
  • the charging device 2 supplies the processing target contained in the charging box 21 to the charging port 30 a of the reduced pressure fermentation and drying device 3.
  • the charging device 2 is configured as, for example, a reversing charging device.
  • the loading box 21 is transported from a storage warehouse or the like to a predetermined position of the loading device 2 by a not shown forklift or the like.
  • the loading box 21 set at a predetermined position of the loading device 2 is lifted upward along a pair of vertically extending rails 22, 22 by driving an electric motor or the like (not shown).
  • the loading box 21 rotates about a horizontal axis 23 provided between the pair of rails 22 and 22, and the loading box 21 is turned upside down.
  • the object to be treated contained in the loading box 21 is loaded into the loading port 30a of the reduced pressure fermentation drying apparatus 3, but here, the municipal solid waste.
  • the object to be treated containing organic substances may scatter and give off a bad odor.
  • the reduced-pressure fermentation drying device 3 is a known device as described in, for example, Patent Document 1, and agitates while heating the object to be treated to a predetermined temperature range under reduced pressure and utilizes microorganisms. Then, the organic component of the object to be treated is decomposed to obtain a reduced volume dried product.
  • the reduced-pressure fermentation drying apparatus 3 is a hermetically-sealed container for accommodating an object to be treated, which is supplied by the charging apparatus 2, and is formed in an airtight manner so as to keep the inside at atmospheric pressure or less.
  • a cylindrical tank (pressure resistant tank) 30 is provided.
  • a heating jacket 31 is provided on the peripheral wall of the tank 30, and heating steam is supplied from the steam boiler 7 to the heating jacket 31.
  • the temperature of the steam supplied from the steam boiler 7 is preferably about 140°C, for example.
  • a stirring shaft 32 extending in the longitudinal direction (left and right direction in FIG. 3) of the tank 30 is provided so as to be surrounded by the heating jacket 31.
  • the stirring shaft 32 is rotated at a predetermined rotation speed by the electric motor 32a.
  • the agitation shaft 32 is provided with a plurality of agitation plates 32b spaced apart in the axial direction thereof. The agitation plates 32b agitate the object to be treated, and after completion of the fermentation drying, organic substances are behind the tank 30. To be sent to.
  • An input port 30a for the organic material supplied from the input device 2 is provided in the upper part of the center of the tank 30 in the longitudinal direction.
  • the organic material input from the input port 30a is heated by the heating jacket 31, while being stirred. It is agitated by the rotation of 32. Then, after a lapse of a predetermined time, the treated organic matter (dried matter) is discharged from the discharge section 30b provided in the lower portion of the tank 30.
  • a hydraulic motor may be used instead of the electric motor 32a.
  • a guide part 30c for guiding the vapor generated from the heated organic matter to the condensing part 33 is provided on the upper part of the tank 30.
  • two guide portions 30c are provided, and each guide portion 30c is arranged on both sides of the tank 30 in the longitudinal direction with the charging port 30a interposed therebetween.
  • the condenser unit 33 includes a plurality of cooling pipes 33b supported by a pair of heads 33a, and a cooling water passage 80 is provided between the plurality of cooling pipes 33b and the cooler 8. ..
  • the condensing part 33 extends in parallel along the longitudinal direction of the tank 30, and the condensing part 33 is arranged on the rear side of the charging port 30a and the guide part 30c.
  • hypochlorite water (hereinafter, chlorine-based deodorizing water It will be described as chlorous acid water.) Connected to the container 104.
  • concentration of hypochlorous acid water contained in this container is 50 to 5000 mg/L, and the hypochlorous acid concentration in the water receiving tank 81 is adjusted to about 30 mg/L by adjusting the opening/closing valve 102 and the chemical liquid pump 103.
  • the hypochlorous acid water is supplied from the container 104.
  • the cooling water flowing through the cooling pipe 33b in the condensing unit 33 and having the temperature raised by heat exchange with the high temperature steam flows through the cooling water passage 80 to be cooled as schematically indicated by an arrow in FIG. It flows into the water receiving tank 81 of the container 8.
  • the cooler 8 is provided with a pumping pump 82 for pumping the cooling water containing hypochlorous acid water in the water receiving tank 81, and a nozzle 83 for injecting the pumped cooling water.
  • the cooling water jetted from the nozzle 83 receives the air blown from the fan 85 while flowing down the lower part 84, the temperature of the cooling water decreases, and the cooling water flows into the water receiving tank 81 again.
  • the cooling water containing the hypochlorous acid water is sprayed from the nozzle 83, and while the cooling water flows down in the lower part 84, the hypochlorous acid dissolved in the cooling water is gasified, and the fan 85 discharges the hypochlorous acid.
  • the chlorous acid gas is blown, and the hypochlorous acid concentration in the water receiving tank 81 is adjusted so that the hypochlorous acid gas concentration in the building A is set to 0.05 to 0.5 ppm.
  • ammonia which is a malodorous component, is decomposed by hypochlorous acid, and the malodor can be deodorized.
  • the cooling water cooled by the cooler 8 is sent by the cooling water pump 86, sent to the condensing unit 33 by the cooling water passage 80, and flows through the plurality of cooling pipes 33b again. Then, after the temperature rises due to the heat exchange with the steam generated inside the tank 30 as described above, it flows through the cooling water path 80 again and flows into the water receiving tank 81 of the cooler 8.
  • the condensed water obtained by condensing the vapor generated from the heated organic matter in the condensing unit 33 is also injected.
  • condensed water generated by exchanging heat with high-temperature steam is collected below the condenser 33.
  • a vacuum pump 36 is connected to the condenser 33 via a communication passage 35 so as to reduce the pressure in the tank 30.
  • the condensed water thus guided to the water receiving tank 81 of the cooler 8 mixes with the cooling water, is pumped up by the pumping pump 82 as described above, is jetted from the nozzle 83, and is then cooled while flowing down the lower stream portion 84. It Since the condensed water contains the same microorganisms as those added to the organic matter in the tank 30, and the malodorous components contained in this condensed water are decomposed, the malodor should not be emitted to the outside of the tank. It has become.
  • the organic matter contained in the tank 30 is stirred by the rotation of the stirring shaft 32 while being heated by the heating steam supplied to the heating jacket 31. Then, the organic matter contained in the tank 30 is effectively heated by receiving heat from the outside by the heating jacket 31 surrounding the inside of the tank 30 and heating from the inside by the stirring shaft 32 and the like. Organic matter is agitated by the shaft 32.
  • the pressure is reduced by the operation of the vacuum pump 36, the boiling point is lowered in the tank 30, and water is evaporated in a temperature range where the decomposition of the organic components of the organic matter is promoted by the microorganisms.
  • one step is preferably, for example, 2 hours, and first, it is a fermentation process for decomposing organic components of organic matter over 30 minutes.
  • the pressure inside the tank 30 is reduced to ⁇ 0.06 to ⁇ 0.07 MPa (gauge pressure; hereinafter, gauge pressure is omitted)
  • the water temperature in the tank 30 is maintained at 76 to 69° C. (saturated vapor temperature).
  • the organic matter during fermentation will be dried over 1.5 hours. Therefore, when the pressure in the tank 30 is further reduced to ⁇ 0.09 to ⁇ 0.10 MPa, the water temperature in the tank is maintained at 46 to 42° C. (saturated vapor temperature), and the drying of organic substances is sufficiently promoted. It becomes a process. Then, when performing such a drying treatment, as the microorganisms to be added to the organic matter in the tank 30, for example, as described in Patent Document 2, a plurality of types of indigenous bacteria are used as a base, and this is pre-cultured.
  • the complex effective microorganism group is preferable, and the common name is the SHIMOSE 1/2/3 group as the center of the colony.
  • SHIMOSE 1 was sent to FERM BP-7504 (Ministry of Economy, Trade and Industry, National Institute of Advanced Industrial Science and Technology, Institute of Biotechnology and Industrial Technology, Patent Microorganism Depositary Center (1-3, Higashi 1-3, Tsukuba, Ibaraki, Japan) on March 14, 2003. Internationally deposited).
  • SHIMOSE 2 is a microorganism belonging to FERM BP-7505 (an international deposit similar to SHIMOSE 1) and Pichiafarinosa, which is resistant to salt, and SHIMOSE 3 is called FERM BP-7506 (SHIMOSE 1). It is a microorganism belonging to Staphylococcus).
  • the atmosphere opening valve (not shown) is closed to seal the inside of the tank 30.
  • the inside of the tank 30 is heated under reduced pressure to promote the fermentation and drying of the organic component of the organic substance contained therein. That is, heating steam is supplied from the steam boiler 7 to heat the inside of the tank 30.
  • the stirring shaft 32 is rotated at a predetermined rotation speed (for example, about 8 rpm), and the inside of the tank 30 is depressurized by the operation of the vacuum pump 36.
  • the temperature in the tank 30 becomes an environment in which the activity of microorganisms is optimal, and the decomposition of organic components of organic substances by microorganisms is favorably promoted.
  • the rotation speed (8 rpm) of the stirring shaft 32 is an example, and may be another value as long as the organic components of the organic matter can be decomposed.
  • the dried material after being subjected to the reduced pressure fermentation drying processing by the reduced pressure fermentation drying apparatus 3 is conveyed to the foreign matter sorting machine 4 by the discharge conveyor 41. That is, the discharge conveyor 41 conveys the dry matter discharged from the discharge section 30b below the tank 30 of the reduced pressure fermentation drying apparatus 3 to the foreign matter selector 4 provided at a position higher than the discharge section 30b.
  • the foreign matter sorter 4 removes foreign matter that is not decomposed by the reduced pressure fermentation and drying process by the reduced pressure fermentation and drying apparatus 3, specifically, metals and plastics.
  • the foreign matter sorter 4 is provided with a magnetic separator 42 and a vibration sieving machine 43, as schematically shown in FIG.
  • the magnetic separator 42 is, for example, a suspension type, and is suspended on the discharge conveyor 41.
  • the magnetic separator 42 attracts magnetic materials such as metal fittings and iron pieces from the dried material conveyed by the discharge conveyor 41 by magnets and continuously discharges them to the discharge container 42c by the belt 42b moving between the pulleys 42a. Is configured.
  • the magnetic separator 42 removes metal such as metal fittings and iron pieces mixed in the dried material.
  • the vibrating and sieving machine 43 is for sieving large foreign matter from the dried material discharged from the reduced pressure fermentation drying device 3 and conveyed by the discharge conveyor 41.
  • the vibrating sieving machine 43 includes a wire net 43a having a mesh (opening) of a predetermined size, and a vibration motor 43b that vibrates the wire net 43a.
  • the vibrating sieving machine 43 is supported on the lower table 43d by a plurality (for example, four) of coil springs 43c.
  • the wire net 43a is provided in a state of being inclined obliquely downward, and one end side (the left end side in FIG. 4) of the wire net 43a is provided at a position lower than the other end side (the right end side in FIG. 4). ing.
  • the mesh of the wire net 43a is set to a size of 5 mm ⁇ 5 mm. Note that the mesh size is an example, and may be another value.
  • the vibrating and sieving machine 43 sorts out plastics and the like mixed in the dried material.
  • the vibrating sieving machine 43 is supported by the coil spring 43c in a floating manner with respect to the lower table 43d, the dried product supplied from the discharge conveyor 41 to the wire net 43a is sieved by driving the vibrating motor 43b. Specifically, the dried material passes through the mesh of the wire net 43a, falls downward, and is stored in the storage container 44 arranged below the vibrating screener 43. On the other hand, since foreign matter larger than the dried product cannot pass through the mesh of the wire net 43a, it moves to one end side (front side) while sliding down or rolling along the inclined surface of the wire net 43a and vibrating and sieving machine 43. It is discharged to the discharge container 43e arranged in the front lower part of.
  • the dried product is fermented and dried by the reduced-pressure fermentation drying device 3 and reduced in volume, so that the dried product is suitable for sieving, and most of the dried product other than the foreign matter passes through the mesh of the wire net 43a. Then, it is stored in the storage container 44.
  • the dried product produced in the final step is used as an organic fertilizer as a valuable product.
  • the dried product is an organic feed for livestock that is a valuable product.
  • it may be used as an organic feed for aquaculture.
  • the second embodiment differs from the first embodiment only in the chlorine-based deodorizing gas diffusion mechanism 200.
  • differences from the first embodiment will be mainly described, and description of configurations common to the first embodiment will be omitted.
  • the chlorine-based deodorizing gas diffusion mechanism 200 has a pipe 202 whose one end is connected to a spray nozzle 201 arranged near the outside of the fan 85 of the cooler 8, and the other end of the pipe 202 has an opening/closing valve 203 and a chemical liquid pump. It is composed of a hypochlorous acid water storage container 205 connected via 204.
  • hypochlorous acid water is sprayed from the spray nozzle 201 in the same direction as the blowing direction of the fan 85.
  • the chloric acid water is mixed and gasified, and these hypochlorous acid gases are diffused throughout the building A in which the processing apparatus 1 is installed, and this hypochlorous acid gas decomposes a malodorous component such as ammonia to deodorize a malodorous substance. To do.
  • a third embodiment of the present invention will be described with reference to FIG.
  • the third embodiment also differs from the first embodiment only in the chlorine-based deodorizing gas diffusion mechanism 300.
  • differences from the first embodiment will be mainly described, and description of the configuration common to the first embodiment will be omitted.
  • one end of the pipe 301 is opened near the outside of the fan 85 of the cooler 8, and the other end is opened above the inside of the hypochlorous acid water storage container 303 via the opening/closing valve 302. Are connected in this way.
  • one end is connected to the compressor 304, and the other end is composed of a second pipe 305 connected so as to enter the hypochlorous acid aqueous solution stored in the hypochlorous acid water storage container 303. ..
  • the hypochlorous acid aqueous solution in the hypochlorous acid water storage container 303 is aerated, and the opening/closing valve 302 in which the hypochlorous acid gas generated here is opened, Combining with the blast of the fan 85 through the first pipe 301, the hypochlorous acid gas is diffused throughout the building A in which the processing device 1 is installed and decomposes a malodorous component such as ammonia to deodorize a malodorous substance. Is.
  • a fourth embodiment of the present invention will be described with reference to FIG.
  • the fourth embodiment also differs from the first embodiment only in the chlorine-based deodorizing gas diffusion mechanism 400.
  • differences from the first embodiment will be mainly described, and description of the configuration common to the first embodiment will be omitted.
  • the chlorine-based deodorizing gas diffusion mechanism 400 has a pan 401 provided near the outside of the fan 85 of the cooler 8, one end of which is connected to the pan 401, and the other end of which is connected via an opening/closing valve 403 and a chemical liquid pump 404. It is composed of a pipe 402 connected to a chlorite water storage container 405, and a heater 406 arranged on the bottom rear surface of the pan 401.
  • hypochlorous acid water is supplied to the pan 401 from the hypochlorous acid water storage container 405 through the pipe 402. Therefore, when power is supplied to the heater 406 provided on the back surface of the pan 401, the pan 401 is heated by the heater 406, and the hypochlorous acid water on the pan 401 is gasified to generate hypochlorous acid gas.
  • the hypochlorous acid gas joins with the air blown by the fan 85 of the cooler 8, and the hypochlorous acid gas is diffused throughout the building A to decompose a malodorous component such as ammonia to deodorize the malodorous substance.
  • the fifth embodiment of the present invention will be described with reference to FIG.
  • the fifth embodiment also differs from the first embodiment only in the chlorine-based deodorizing gas diffusion mechanism 500.
  • differences from the first embodiment will be mainly described, and description of configurations common to the first embodiment will be omitted.
  • the chlorine-based deodorizing gas diffusion mechanism 500 has a first pipe 502 having one end opened in the vicinity of the fan 85 of the cooler 8 and the other end connected to the discharge port of the ejector 501, and the open/close valve 503 at one end.
  • Second pipe 505 connected to the hypochlorous acid water storage container 504 through the other end and the other end connected to the hypochlorous acid water supply port of the ejector 501, and one end connected to the compressor 506 and the other end.
  • a third pipe 507 connected to the air introduction port 501.
  • the opening/closing valve 503 is opened so that hypochlorous acid water can be supplied from the hypochlorous acid water storage container 504 to the supply port of the ejector 501 through the second pipe 505, and the compressor 506 is driven to drive the compressor.
  • the hypochlorous acid water is sucked into the air flow inside the ejector 501, gasifies, and is ejected from the ejector 501 discharge port through the first pipe 502 to the hypochlorite gas.
  • the hypochlorous acid gas is diffused throughout the building A by the fan 85 of the cooler 8 and decomposes a malodorous component such as ammonia to deodorize the malodor.
  • hypochlorous acid water In the embodiment of the present invention, the chlorine-based deodorized water is described as hypochlorous acid water, but this hypochlorous acid water may be chlorine dioxide water, or, of course, chlorous acid water. Of course, chlorine-based deodorized water can be used.
  • the present invention can be used for a deodorizing device and a processing method thereof in a processing device for a processing object containing an organic substance.

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  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Epidemiology (AREA)
  • Life Sciences & Earth Sciences (AREA)
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Abstract

The present invention includes: a vacuum fermentation drying device in which an organic matter-containing substance to be treated is stored in a sealed container and stirred while being heated in a predetermined temperature range in a vacuum, organic components of the organic matter are dissolved using microorganisms, and a dry substance having a reduced volume is obtained; a cooler connected via a condenser section of the sealed container; a cooling water circulation passage through which cooling water is circulated between the condensation section and the cooler; and a chlorine deodorizing gas diffusion mechanism attached to the cooler.

Description

有機物を含む処理対象物の処理装置における脱臭装置及びその脱臭方法Deodorizing apparatus and method for deodorizing an object to be treated containing organic matter
 本発明は、有機物を含む処理対象物の処理装置における脱臭装置及びその脱臭方法に関するものである。 The present invention relates to a deodorizing device and a deodorizing method thereof in a processing device for a processing object containing an organic substance.
 本願出願人は、先に例えば特許文献1に記載するように、有機物を含む処理対象物をタンクなどの密閉容器に収容し、減圧下において所定の温度範囲に加熱しながら撹拌することによって、効率的に水分を除去し乾燥させるとともに、有機物を含む処理対象物に所定の微生物を添加し、有機物の発酵を促進させることができる減圧発酵乾燥装置を特許出願している。 The applicant of the present application, as described in, for example, Patent Document 1 above, stores an object to be treated containing an organic substance in a closed container such as a tank, and stirs it while heating it to a predetermined temperature range under reduced pressure, thereby improving efficiency. A patent application has been filed for a reduced-pressure fermentation drying device capable of accelerating the fermentation of organic substances by adding predetermined microorganisms to an object to be treated containing organic substances while drying and removing water.
 また、この減圧発酵乾燥装置には微生物を利用して悪臭のもととなっている微生物を分解する機能を有しているが、減圧発酵乾燥装置を含めた処理装置を設置した建屋内全体の悪臭を脱臭するだけの能力がなく、建屋内に飛散した都市ごみなどの有機物を含む処理対象物からは悪臭が発生するといった問題があった。 In addition, this vacuum fermentation drying device has the function of decomposing the microorganisms that are the source of the bad odor by using microorganisms, but the entire building where the processing equipment including the vacuum fermentation drying device is installed is installed. There is a problem that it does not have the ability to deodorize a bad odor, and a bad odor is generated from an object to be treated containing organic substances such as municipal solids scattered in the building.
特開2007-319738号公報JP, 2007-319738, A 特許第4153685号公報Japanese Patent No. 4153685
 本発明は、上述したような実情を考慮してなされたものであって、減圧発酵乾燥装置を含めた処理装置を設置した建屋内全体の悪臭を脱臭する装置及びその処理方法である。 The present invention has been made in consideration of the above-mentioned circumstances, and is an apparatus and a processing method for deodorizing a bad odor in an entire building in which a processing apparatus including a vacuum fermentation drying apparatus is installed.
 本発明は、上述の課題を解決するための手段を以下のように構成している。すなわち、本発明は有機物を含む処理対象物を密閉容器に収容し、減圧下において所定の温度範囲に加熱しながら撹拌するとともに、微生物を利用して有機物の有機成分を分解させ、減容した乾燥物を得る減圧発酵乾燥装置と、前記密閉容器の凝縮部と真空ポンプを介して接続された冷却器と、前記凝縮部と冷却器とを冷却水ポンプを介して冷却水を循環させる冷却水循環経路と、前記冷却器に付設された塩素系脱臭ガス拡散機構とを備えたことを特徴とする。 The present invention has the following means for solving the above-mentioned problems. That is, the present invention is a method of accommodating an object to be treated containing an organic matter in a closed container and stirring while heating under a reduced pressure to a predetermined temperature range, decomposing the organic component of the organic matter by using a microorganism, and reducing the volume of the dried product. A reduced pressure fermentation drying apparatus for obtaining a product, a cooler connected to the condenser of the closed container via a vacuum pump, and a cooling water circulation path for circulating cooling water between the condenser and the cooler via a cooling water pump. And a chlorine-based deodorizing gas diffusion mechanism attached to the cooler.
 本発明によれば、前記減圧発酵乾燥装置内に生息する微生物を利用して悪臭のもととなっている微生物を分解するほか、塩素系脱臭水で悪臭成分、例えばアンモニアを分解することができるので、有機物を含む処理対象物の処理装置を設置した建屋内からはほとんど悪臭が発生しないものである。 According to the present invention, in addition to decomposing microorganisms that are the source of malodor using microorganisms that live in the vacuum fermentation and drying device, chlorine-based deodorized water can decompose malodorous components such as ammonia. Therefore, a bad odor is hardly generated from the building in which the apparatus for treating the object to be treated including the organic matter is installed.
 本発明において、前記塩素系脱臭ガス拡散機構は、前記冷却器の受水槽と、前記受水槽に一端が接続された配管と、前記配管の他端が薬液ポンプを介して接続された塩素系脱臭水収容容器とで構成されたことを特徴とする有機物を含む処理対象物の処理装置における脱臭装置であり、受水槽の塩素系脱臭水を含む冷却水を汲み上げポンプを介してノズルから噴霧し、冷却水が流下する際、冷却水に溶け込んだ塩素系脱臭水がガス化し(以下、「塩素系脱臭ガス」とも言う)、この塩素系脱臭ガスが冷却器のファンから送風され、これにより塩素系脱臭ガスが処理装置を設置した建屋内全体に拡散されて悪臭成分、例えばアンモニアを分解して悪臭を脱臭するものである。 In the present invention, the chlorine-based deodorant gas diffusion mechanism is a water-receiving tank of the cooler, a pipe having one end connected to the water-receiving tank, and a chlorine-based deodorant having the other end of the pipe connected via a chemical pump. A deodorizing device in a treatment device for an object to be treated containing an organic substance, which is composed of a water storage container, and sprays cooling water containing chlorine-based deodorizing water in a water receiving tank from a nozzle via a pump, When the cooling water flows down, the chlorine-based deodorized water dissolved in the cooling water is gasified (hereinafter, also referred to as "chlorine-based deodorizing gas"), and this chlorine-based deodorizing gas is blown from the fan of the cooler, thereby The deodorizing gas is diffused throughout the building where the processing device is installed to decompose a malodorous component such as ammonia to deodorize the malodorous substance.
 本発明において、前記塩素系脱臭ガス拡散機構は、前記冷却器のファンの外方向近傍に配置された噴霧ノズルと、前記噴霧ノズルに一端が接続された配管と、前記配管の他端が薬液ポンプを介して接続された塩素系脱臭水収容容器とで構成されたことを特徴とする有機物を含む処理対象物の処理装置における脱臭装置であり、前記冷却器のファン外方向近傍に配置された噴霧ノズルから噴霧された塩素系脱臭水が、前記冷却器のファンの送風によりガス化してこれら塩素系脱臭ガスが処理装置を設置した建屋内全体に拡散され、これら塩素系脱臭ガスが悪臭成分、例えばアンモニアを分解して悪臭を脱臭するものである。 In the present invention, the chlorine-based deodorizing gas diffusion mechanism includes a spray nozzle arranged near an outside of the fan of the cooler, a pipe having one end connected to the spray nozzle, and the other end of the pipe being a chemical pump. A deodorizing device in a treatment device for an object to be treated containing an organic matter, which is constituted by a chlorine-based deodorized water storage container connected via a spray, which is arranged near a fan outside direction of the cooler. Chlorine deodorized water sprayed from the nozzle is gasified by the air blow of the fan of the cooler and these chlorine deodorized gases are diffused throughout the building in which the processing device is installed, and these chlorine deodorized gases are malodorous components, for example, It decomposes ammonia and deodorizes odors.
 本発明において、前記塩素系脱臭ガス拡散機構は、前記冷却器のファン外方向近傍に一端が開口され、その他端が塩素系脱臭水収容容器内部上方に開口された第1配管と、一端がコンプレッサーに接続され、その他端の開口が前記収容容器に収容された塩素系脱臭水溶液の内部に入るように接続された第2配管とで構成されて特徴とする有機物を含む処理対象物の処理装置における脱臭装置であり、ここで、前記コンプレッサーを駆動すると、塩素系脱臭水収容容器内の塩素系脱臭水溶液がばっ気されることになり、ここで発生した塩素系脱臭ガスが第1配管を通ってファンの送風に合流して、塩素系脱臭ガスが処理装置を設置した建屋内全体に拡散されて悪臭成分、例えばアンモニアを分解して悪臭を脱臭するものである。 In the present invention, the chlorine-based deodorizing gas diffusion mechanism has a first pipe whose one end is opened near the outside of the fan of the cooler and the other end is opened above the inside of the chlorine-based deodorized water storage container, and one end is a compressor. And a second pipe connected to the other end so as to enter the inside of the chlorine-based deodorizing aqueous solution accommodated in the accommodating container. It is a deodorizing device, and when the compressor is driven, the chlorine deodorizing aqueous solution in the chlorine deodorizing water storage container is aerated, and the chlorine deodorizing gas generated here passes through the first pipe. Combined with the air blow of the fan, the chlorine-based deodorizing gas is diffused throughout the building where the processing device is installed to decompose a malodorous component such as ammonia to deodorize the malodor.
 本発明において、前記塩素系脱臭ガス拡散機構は、前記冷却器のファン外方向近傍に設けられたパンと、前記パンに薬液ポンプを介して接続された塩素系脱臭水収容容器と、前記パンの底部裏面に配設されたヒータとで構成されたことを特徴とする有機物を含む処理対象物の処理装置における脱臭装置であり、パンに供給された塩素系脱臭水をヒータで加熱することにより塩素系脱臭水をガス化し、前記冷却器のファンにより塩素系脱臭ガスが建屋内全体に拡散されて悪臭成分、例えばアンモニアを分解して悪臭を脱臭するものである。 In the present invention, the chlorine-based deodorant gas diffusion mechanism is a pan provided in the vicinity of the fan outside of the cooler, a chlorine-based deodorized water storage container connected to the pan via a chemical liquid pump, and the pan. A deodorizing device in a treatment device for an object to be treated containing an organic substance, characterized by comprising a heater arranged on the back surface of the bottom, and by heating the chlorine-based deodorized water supplied to the pan with the heater, chlorine is generated. The system deodorizing water is gasified, and the chlorine-based deodorizing gas is diffused throughout the building by the fan of the cooler to decompose a malodorous component such as ammonia to deodorize the malodor.
 本発明において、前記塩素系脱臭ガス拡散機構は、前記冷却器のファン近傍に一端が開口し、他端がエジェクターの吐出口に接続した第1配管と、一端が塩素系脱臭水収容容器に接続され、他端がエジェクターの塩素系脱臭水供給口に接続された第2配管と、一端がコンプレッサーに接続され、他端がエジェクターの空気導入口に接続された第3配管とで構成されたことを特徴とする有機物を含む処理対象物の処理装置における脱臭装置であり、エジェクター内部でコンプレッサーから送風された気流に塩素系脱臭水供給口から塩素系脱臭水が吸い込まれ、ガス化して吐出口から塩素系脱臭ガスを噴射することで、前記冷却器のファンにより塩素系脱臭ガスが建屋内全体に拡散されて悪臭成分、例えばアンモニアを分解して悪臭を脱臭するものである。 In the present invention, the chlorine-based deodorant gas diffusion mechanism has a first pipe having one end opened near the fan of the cooler and the other end connected to the ejection port of the ejector, and one end connected to the chlorine-based deodorized water storage container. And a second pipe having the other end connected to the chlorine-based deodorized water supply port of the ejector, and a third pipe having one end connected to the compressor and the other end connected to the air introduction port of the ejector. Is a deodorizing device in a treatment device for an object to be treated containing organic matter, in which chlorine-based deodorized water is sucked into the air flow blown from the compressor inside the ejector from the chlorine-based deodorized water supply port, and gasifies from the discharge port. By injecting the chlorine-based deodorizing gas, the fan of the cooler diffuses the chlorine-based deodorizing gas throughout the building to decompose a malodorous component such as ammonia to deodorize the malodor.
 本発明において、前記塩素系脱臭水の濃度は50~5000mg/Lであることを特徴とする有機物を含む処理対象物の処理装置における脱臭装置であり、前記塩素系脱臭水は脱臭効果があるほか、殺菌作用もあり、またこの程度の濃度であれば人体に対しても何ら影響もなく、無害である。 In the present invention, the concentration of the chlorine-based deodorized water is 50 to 5000 mg/L, and the chlorine-based deodorized water has a deodorizing effect. It also has a bactericidal action, and at this concentration, it has no effect on the human body and is harmless.
 また、本発明は、有機物を含む処理対象物を密閉容器に収容し、減圧下において所定の温度範囲に加熱しながら撹拌するとともに、微生物を利用して有機物の有機成分を分解させ、減容した乾燥物を得る減圧発酵乾燥工程と、前記密閉容器の凝縮工程を介して接続された冷却工程と、前記凝縮工程と冷却工程間に冷却水を循環させる冷却水循環工程と、前記冷却工程に付設された塩素系脱臭ガス拡散工程と、を備えたことを特徴とする有機物を含む処理対象物の処理装置における脱臭方法あり、有機物を含む処理対象物の処理装置における脱臭装置と同じ効果が期待できるものである。 Further, the present invention, the object to be treated containing an organic matter is housed in a closed container and stirred while heating under a reduced pressure to a predetermined temperature range, and the organic component of the organic matter is decomposed by utilizing microorganisms to reduce the volume. A reduced pressure fermentation drying step of obtaining a dried product, a cooling step connected through a condensing step of the closed container, a cooling water circulation step of circulating cooling water between the condensing step and the cooling step, and a cooling step attached to the cooling step. There is a chlorine-based deodorizing gas diffusion step, and there is a deodorizing method in a treatment device for an object to be treated containing an organic substance, and the same effect as a deodorizing device in a treatment device for an object to be treated containing an organic substance can be expected. Is.
 本発明に係る有機物を含む処理対象物の処理装置における脱臭装置及びその脱臭方法によれば、前記減圧発酵乾燥装置内部を脱臭できるほか、前記減圧発酵乾燥機を含む処理装置を設置した建屋内で、飛散した有機物を含む処理対象物から発生した悪臭成分、例えばアンモニアなどを分解することができ、建屋内全体の悪臭を脱臭することができるものである。 According to the deodorizing apparatus and its deodorizing method in the processing apparatus for treating an object containing an organic substance according to the present invention, in addition to being able to deodorize the inside of the reduced pressure fermentation drying apparatus, in a building where a processing apparatus including the reduced pressure fermentation drying apparatus is installed. It is possible to decompose the malodorous components generated from the object to be treated including the scattered organic matter, such as ammonia, and to deodorize the malodors in the entire building.
本発明の第1実施形態に係る有機物を含む処理対象物の処理装置における投入装置、減圧発酵乾燥装置、異物選別機等を示す正面図である。FIG. 1 is a front view showing a charging device, a reduced pressure fermentation and drying device, a foreign matter sorter, and the like in a treatment device for a treatment object containing an organic substance according to the first embodiment of the present invention. 図1の投入装置、減圧発酵乾燥装置、異物選別機等を示す側面図である。It is a side view which shows the charging device of FIG. 1, a reduced pressure fermentation drying device, a foreign material sorter, etc. 図1の減圧発酵乾燥装置の脱臭装置の概略構成を模式的に示す図である。It is a figure which shows typically the schematic structure of the deodorizing apparatus of the reduced pressure fermentation drying apparatus of FIG. 図1の異物選別機の概略構成を示す斜視図である。It is a perspective view which shows schematic structure of the foreign material selection machine of FIG. 本発明の第2実施形態に係る有機物を含む処理対象物の処理装置における減圧発酵乾燥装置の脱臭装置の概略構成を模式的に示す図である。It is a figure which shows typically the schematic structure of the deodorizing apparatus of the reduced pressure fermentation drying apparatus in the processing apparatus of the to-be-processed object containing the organic substance which concerns on 2nd Embodiment of this invention. 本発明の第3実施形態に係る有機物を含む処理対象物の処理装置における減圧発酵乾燥装置の脱臭装置の概略構成を模式的に示す図である。It is a figure which shows typically the schematic structure of the deodorizing apparatus of the reduced pressure fermentation drying apparatus in the processing apparatus of the to-be-processed object containing the organic substance which concerns on 3rd Embodiment of this invention. 本発明の第4実施形態に係る有機物を含む処理対象物の処理装置における減圧発酵乾燥装置の脱臭装置の概略構成を模式的に示す図である。It is a figure which shows typically the schematic structure of the deodorizing apparatus of the reduced pressure fermentation drying apparatus in the processing apparatus of the to-be-processed object containing the organic substance which concerns on 4th Embodiment of this invention. 本発明の第5実施形態に係る有機物を含む処理対象物の処理装置における減圧発酵乾燥装置の脱臭装置の概略構成を模式的に示す図である。It is a figure which shows typically the schematic structure of the deodorizing apparatus of the reduced pressure fermentation drying apparatus in the processing apparatus of the to-be-processed object containing the organic substance which concerns on 5th Embodiment of this invention.
 <第1実施形態>
 以下、本発明の第1実施形態について図面を参照しながら説明する。図1は、本発明の実施形態に係る有機物を含む処理対象物の処理装置における投入装置、減圧発酵乾燥装置、異物選別機等を示す正面図であり、図2は、前記処理装置の投入装置、減圧発酵乾燥装置、異物選別機等を示す側面図であり、図3は、前記処理装置の減圧発酵乾燥装置の概略構成を模式的に示す図であり、図4は、前記処理装置の異物選別機の概略構成を示す斜視図である。
<First Embodiment>
Hereinafter, a first embodiment of the present invention will be described with reference to the drawings. FIG. 1 is a front view showing a charging device, a reduced pressure fermentation drying device, a foreign matter selector, and the like in a processing device for a processing object containing an organic substance according to an embodiment of the present invention, and FIG. 2 is a charging device of the processing device. FIG. 4 is a side view showing a reduced pressure fermentation drying apparatus, a foreign matter sorter, etc., FIG. 3 is a diagram schematically showing a schematic configuration of a reduced pressure fermentation drying apparatus of the processing apparatus, and FIG. 4 is a foreign matter of the processing apparatus. It is a perspective view showing a schematic structure of a sorting machine.
 図1~図4に示すように、有機物を含む処理対象物の処理装置(以下、「処理装置」とも言う。)1は、投入装置2、減圧発酵乾燥装置3、異物選別機4等を備えている。前記処理装置1においては、例えば都市ごみなどの有機物を含む処理対象物が投入装置2によって減圧発酵乾燥装置3に投入され、投入された処理対象物に対して減圧発酵乾燥装置3によって減圧発酵乾燥処理が実行される。減圧発酵乾燥装置3の減圧発酵乾燥処理により得られた乾燥物が排出コンベア41により異物選別機4へ送られ、異物選別機4によって乾燥物に混入している異物が除去される。 As shown in FIGS. 1 to 4, a treatment device (hereinafter, also referred to as a “treatment device”) 1 for an object to be treated containing an organic substance includes a charging device 2, a reduced pressure fermentation drying device 3, a foreign matter selector 4, and the like. ing. In the processing apparatus 1, for example, an object to be processed containing organic matter such as municipal solid waste is put into the reduced pressure fermentation and drying apparatus 3 by the inputting apparatus 2, and the input object to be processed is reduced pressure fermentation and drying by the reduced pressure fermentation and drying apparatus 3. The process is executed. The dried product obtained by the reduced pressure fermentation and drying process of the reduced pressure fermentation drying device 3 is sent to the foreign matter selector 4 by the discharge conveyor 41, and the foreign matter mixed in the dried matter is removed by the foreign matter selector 4.
 図2では、例えば建屋A内に設置された状態の処理装置1を示しており、建屋A内の所定位置に、投入装置2、減圧発酵乾燥装置3、異物選別機4等が設置されている。以下、処理装置1に備えられる各機器について説明する。 In FIG. 2, for example, the processing apparatus 1 installed in the building A is shown, and a charging device 2, a reduced pressure fermentation drying device 3, a foreign matter selector 4, etc. are installed in predetermined positions in the building A. .. Hereinafter, each device included in the processing device 1 will be described.
 投入装置2は、投入用箱21に収容された処理対象物を減圧発酵乾燥装置3の投入口30aに供給するものである。投入装置2は、例えば反転式の投入装置として構成されている。投入用箱21は、例えば保管倉庫などから、図示しないフォークリフト等によって投入装置2の所定位置まで搬送される。投入装置2の所定位置にセットされた投入用箱21は、図示しない電動モータ等の駆動によって、上下方向に延びる1対のレール22,22に沿って上方へ持ち上げられる。投入用箱21は、1対のレール22,22の上端部まで上昇すると、1対のレール22,22間に設けられた水平軸23まわりに回転し、投入用箱21が上下反転する。この投入用箱21の反転動作に伴って、投入用箱21内に収容された処理対象物が、減圧発酵乾燥装置3の投入口30aに投入されるようになっているが、ここで都市ごみなど有機物を含む処理対象物が飛散して悪臭を漂う恐れがあった。 The charging device 2 supplies the processing target contained in the charging box 21 to the charging port 30 a of the reduced pressure fermentation and drying device 3. The charging device 2 is configured as, for example, a reversing charging device. The loading box 21 is transported from a storage warehouse or the like to a predetermined position of the loading device 2 by a not shown forklift or the like. The loading box 21 set at a predetermined position of the loading device 2 is lifted upward along a pair of vertically extending rails 22, 22 by driving an electric motor or the like (not shown). When the loading box 21 rises to the upper ends of the pair of rails 22 and 22, the loading box 21 rotates about a horizontal axis 23 provided between the pair of rails 22 and 22, and the loading box 21 is turned upside down. Along with the reversing operation of the loading box 21, the object to be treated contained in the loading box 21 is loaded into the loading port 30a of the reduced pressure fermentation drying apparatus 3, but here, the municipal solid waste. There is a possibility that the object to be treated containing organic substances may scatter and give off a bad odor.
 減圧発酵乾燥装置3は、例えば特許文献1などに記載されているように公知のものであり、処理対象の処理対象物を減圧下において所定の温度範囲に加熱しながら撹拌するとともに、微生物を利用して処理対象物の有機成分を分解させ、減容した乾燥物を得るものである。 The reduced-pressure fermentation drying device 3 is a known device as described in, for example, Patent Document 1, and agitates while heating the object to be treated to a predetermined temperature range under reduced pressure and utilizes microorganisms. Then, the organic component of the object to be treated is decomposed to obtain a reduced volume dried product.
 減圧発酵乾燥装置3は、図3に模式的に示すように、投入装置2によって供給される処理対象物を収容する密閉容器として、内部を大気圧以下に保持するように気密に形成された略円筒状のタンク(耐圧タンク)30を備えている。このタンク30の周壁部には、加熱ジャケット31が設けられ、蒸気ボイラー7から加熱用蒸気が加熱ジャケット31に供給されるようになっている。なお、蒸気ボイラー7から供給される蒸気の温度は、例えば140℃程度が好ましい。 As shown schematically in FIG. 3, the reduced-pressure fermentation drying apparatus 3 is a hermetically-sealed container for accommodating an object to be treated, which is supplied by the charging apparatus 2, and is formed in an airtight manner so as to keep the inside at atmospheric pressure or less. A cylindrical tank (pressure resistant tank) 30 is provided. A heating jacket 31 is provided on the peripheral wall of the tank 30, and heating steam is supplied from the steam boiler 7 to the heating jacket 31. The temperature of the steam supplied from the steam boiler 7 is preferably about 140°C, for example.
 また、加熱ジャケット31に取り囲まれるようにして、タンク30の内部にはその長手方向(図3の左右方向)に延びる撹拌シャフト32が設けられている。撹拌シャフト32は、電動モータ32aによって所定の回転速度で回転される。撹拌シャフト32には、その軸方向に離間して複数の撹拌板32bが設けられており、これら撹拌板32bによって、処理対象物が撹拌されるとともに、発酵乾燥終了後には有機物がタンク30の後方に送られるようになっている。 Further, a stirring shaft 32 extending in the longitudinal direction (left and right direction in FIG. 3) of the tank 30 is provided so as to be surrounded by the heating jacket 31. The stirring shaft 32 is rotated at a predetermined rotation speed by the electric motor 32a. The agitation shaft 32 is provided with a plurality of agitation plates 32b spaced apart in the axial direction thereof. The agitation plates 32b agitate the object to be treated, and after completion of the fermentation drying, organic substances are behind the tank 30. To be sent to.
 タンク30の長手方向中央の上部には、投入装置2から供給される有機物の投入口30aが設けられており、この投入口30aから投入された有機物が、加熱ジャケット31によって加熱されながら、撹拌シャフト32の回転によって撹拌される。そして、所定時間経過した後、処理後の有機物(乾燥物)がタンク30の下部に設けられた排出部30bから排出される。なお、電動モータ32aの代わりに、油圧モータを用いてもよい。 An input port 30a for the organic material supplied from the input device 2 is provided in the upper part of the center of the tank 30 in the longitudinal direction. The organic material input from the input port 30a is heated by the heating jacket 31, while being stirred. It is agitated by the rotation of 32. Then, after a lapse of a predetermined time, the treated organic matter (dried matter) is discharged from the discharge section 30b provided in the lower portion of the tank 30. A hydraulic motor may be used instead of the electric motor 32a.
 タンク30の上部には、加熱された有機物から発生する蒸気を凝縮部33へ案内する案内部30cが突設されている。本実施形態では、案内部30cが2つ設けられており、各案内部30cは、投入口30aを挟んでタンク30の長手方向の両側に1つずつ配置されている。凝縮部33は、1対のヘッド33aによって支持された複数の冷却管33bを備えており、これら複数の冷却管33bと、冷却器8との間には、冷却水経路80が設けられている。本実施形態では、凝縮部33は、タンク30の長手方向に沿って平行に延びており、投入口30a及び案内部30cの後方側に凝縮部33が配置されている。 A guide part 30c for guiding the vapor generated from the heated organic matter to the condensing part 33 is provided on the upper part of the tank 30. In the present embodiment, two guide portions 30c are provided, and each guide portion 30c is arranged on both sides of the tank 30 in the longitudinal direction with the charging port 30a interposed therebetween. The condenser unit 33 includes a plurality of cooling pipes 33b supported by a pair of heads 33a, and a cooling water passage 80 is provided between the plurality of cooling pipes 33b and the cooler 8. .. In the present embodiment, the condensing part 33 extends in parallel along the longitudinal direction of the tank 30, and the condensing part 33 is arranged on the rear side of the charging port 30a and the guide part 30c.
 次に、第1実施形態における塩素系脱臭ガス拡散機構100を説明する。前記冷却器8の受水槽81には、薬液配管101の一端が接続されており、開閉弁102及び薬液ポンプ103を介して、その他端は次亜塩素酸水(以下、塩素系脱臭水は次亜塩素酸水として説明する。)収容容器104に接続されている。この収容容器に収容された次亜塩素酸水の濃度は50~5000mg/Lであり、開閉弁102や薬液ポンプ103を調整して受水槽81の次亜塩素酸濃度が略30mg/Lとなるように収容容器104から次亜塩素酸水が供給される。 Next, the chlorine-based deodorant gas diffusion mechanism 100 in the first embodiment will be described. One end of a chemical liquid pipe 101 is connected to the water receiving tank 81 of the cooler 8, and a hypochlorite water (hereinafter, chlorine-based deodorizing water It will be described as chlorous acid water.) Connected to the container 104. The concentration of hypochlorous acid water contained in this container is 50 to 5000 mg/L, and the hypochlorous acid concentration in the water receiving tank 81 is adjusted to about 30 mg/L by adjusting the opening/closing valve 102 and the chemical liquid pump 103. Thus, the hypochlorous acid water is supplied from the container 104.
 そして、凝縮部33において冷却管33b内を流通し、高温の蒸気との熱交換によって温度が上昇した冷却水は、図3に模式的に矢印で示すように冷却水経路80を流通して冷却器8の受水槽81に流入する。冷却器8には、受水槽81で次亜塩素酸水が含まれた冷却水を汲み上げる汲み上げポンプ82と、汲み上げられた冷却水を噴射するノズル83とが設けられている。このノズル83から噴射された冷却水は、流下部84を流下する間にファン85からの送風を受けて温度が低下し、再び受水槽81に流入するようになっている。 Then, the cooling water flowing through the cooling pipe 33b in the condensing unit 33 and having the temperature raised by heat exchange with the high temperature steam flows through the cooling water passage 80 to be cooled as schematically indicated by an arrow in FIG. It flows into the water receiving tank 81 of the container 8. The cooler 8 is provided with a pumping pump 82 for pumping the cooling water containing hypochlorous acid water in the water receiving tank 81, and a nozzle 83 for injecting the pumped cooling water. The cooling water jetted from the nozzle 83 receives the air blown from the fan 85 while flowing down the lower part 84, the temperature of the cooling water decreases, and the cooling water flows into the water receiving tank 81 again.
 この間、前記次亜塩素酸水を含む冷却水がノズル83から噴霧され、冷却水が流下部84で流下しながら、冷却水に溶け込んでいる次亜塩素酸がガス化し、ファン85からは次亜塩素酸ガスが送風され、建屋A内の次亜塩素酸ガス濃度が0.05~0.5ppmに設定されるように、受水槽81の次亜塩素酸濃度を調整されている。その結果、悪臭成分である例えばアンモニアが次亜塩素酸で分解され、悪臭を脱臭することができる。 During this time, the cooling water containing the hypochlorous acid water is sprayed from the nozzle 83, and while the cooling water flows down in the lower part 84, the hypochlorous acid dissolved in the cooling water is gasified, and the fan 85 discharges the hypochlorous acid. The chlorous acid gas is blown, and the hypochlorous acid concentration in the water receiving tank 81 is adjusted so that the hypochlorous acid gas concentration in the building A is set to 0.05 to 0.5 ppm. As a result, for example, ammonia, which is a malodorous component, is decomposed by hypochlorous acid, and the malodor can be deodorized.
 冷却器8で冷却された冷却水は、冷却水ポンプ86によって送水され、冷却水経路80によって凝縮部33に送られて、再び複数の冷却管33b内を流通する。そして、上述のようにタンク30の内部で発生した蒸気との熱交換によって温度が上昇した後に、再び冷却水経路80を流通して、冷却器8の受水槽81に流入する。 The cooling water cooled by the cooler 8 is sent by the cooling water pump 86, sent to the condensing unit 33 by the cooling water passage 80, and flows through the plurality of cooling pipes 33b again. Then, after the temperature rises due to the heat exchange with the steam generated inside the tank 30 as described above, it flows through the cooling water path 80 again and flows into the water receiving tank 81 of the cooler 8.
 上述のように循環する冷却水の他に、冷却器8では、加熱された有機物から発生する蒸気が凝縮部33において凝縮した凝縮水も注水される。なお、図示しないが凝縮部33の下方に、高温の蒸気と熱交換することによって生成した凝縮水が集められるようになっている。また、凝縮部33には連通路35を介して真空ポンプ36が接続され、タンク30内を減圧するようになっている。 In addition to the circulating cooling water as described above, in the cooler 8, the condensed water obtained by condensing the vapor generated from the heated organic matter in the condensing unit 33 is also injected. Although not shown, condensed water generated by exchanging heat with high-temperature steam is collected below the condenser 33. A vacuum pump 36 is connected to the condenser 33 via a communication passage 35 so as to reduce the pressure in the tank 30.
 すなわち、真空ポンプ36の作動によって、連通路35を介して凝縮部33から空気及び凝縮水が吸い出され、さらに連通路34及び案内部30cを介してタンク30内の空気及び蒸気が吸い出される。こうして、凝縮部33からは凝縮水が真空ポンプ36に吸い出され、この真空ポンプ36から導水管によって、冷却器8の受水槽81に導かれる。 That is, by the operation of the vacuum pump 36, air and condensed water are sucked from the condenser 33 through the communication passage 35, and further, air and steam in the tank 30 are sucked through the communication passage 34 and the guide portion 30c. .. In this way, the condensed water is sucked from the condenser 33 to the vacuum pump 36, and is guided from the vacuum pump 36 to the water receiving tank 81 of the cooler 8 by the water guiding pipe.
 こうして冷却器8の受水槽81に導かれた凝縮水は、冷却水と混ざり合って上述のように汲み上げポンプ82に汲み上げられ、ノズル83から噴射された後に、流下部84を流下しながら冷却される。なお、凝縮水には、タンク30内の有機物に添加されたものと同じ微生物が含まれており、この凝縮水に含まれる悪臭成分等が分解されているので、悪臭はタンク外部へ発散しないようになっている。 The condensed water thus guided to the water receiving tank 81 of the cooler 8 mixes with the cooling water, is pumped up by the pumping pump 82 as described above, is jetted from the nozzle 83, and is then cooled while flowing down the lower stream portion 84. It Since the condensed water contains the same microorganisms as those added to the organic matter in the tank 30, and the malodorous components contained in this condensed water are decomposed, the malodor should not be emitted to the outside of the tank. It has become.
 上記構成の減圧発酵乾燥装置3の作動について説明すると、タンク30内に収容された有機物は、加熱ジャケット31に供給される加熱用蒸気によって加熱されながら、撹拌シャフト32の回転に伴い撹拌される。そして、タンク30内を取り囲む加熱ジャケット31による外側からの加熱と、撹拌シャフト32などによる内側からの加熱とを受けて、タンク30内に収容された有機物が効果的に昇温されるとともに、撹拌シャフト32によって有機物が撹拌される。加えて、真空ポンプ36の作動によって減圧されているため、タンク30内では沸点が低下し、微生物によって有機物の有機成分の分解が促進される温度領域で水分が蒸発する。 Explaining the operation of the reduced pressure fermentation drying apparatus 3 having the above-described configuration, the organic matter contained in the tank 30 is stirred by the rotation of the stirring shaft 32 while being heated by the heating steam supplied to the heating jacket 31. Then, the organic matter contained in the tank 30 is effectively heated by receiving heat from the outside by the heating jacket 31 surrounding the inside of the tank 30 and heating from the inside by the stirring shaft 32 and the like. Organic matter is agitated by the shaft 32. In addition, since the pressure is reduced by the operation of the vacuum pump 36, the boiling point is lowered in the tank 30, and water is evaporated in a temperature range where the decomposition of the organic components of the organic matter is promoted by the microorganisms.
 なお、減圧発酵乾燥装置3による減圧発酵乾燥工程では1工程(1サイクル)が、例えば2時間であることが好ましく、まず30分かけて有機物の有機成分を分解させる発酵工程となる。タンク30内を-0.06~-0.07MPa(ゲージ圧;以下、ゲージ圧は省略する)に減圧すると、タンク30内の水分温度は76~69℃(飽和蒸気温度)に維持される。その結果、有機物は、後述する微生物によって、発酵、分解が促進される。 Note that, in the reduced pressure fermentation and drying process by the reduced pressure fermentation and drying device 3, one step (one cycle) is preferably, for example, 2 hours, and first, it is a fermentation process for decomposing organic components of organic matter over 30 minutes. When the pressure inside the tank 30 is reduced to −0.06 to −0.07 MPa (gauge pressure; hereinafter, gauge pressure is omitted), the water temperature in the tank 30 is maintained at 76 to 69° C. (saturated vapor temperature). As a result, fermentation and decomposition of the organic matter are promoted by the microorganisms described below.
 次に、1.5時間かけて発酵中の有機物を乾燥させることになる。そのために、タンク30内を-0.09~-0.10MPaにさらに減圧すると、タンク内の水分温度は46~42℃(飽和蒸気温度)に維持され、有機物の乾燥が十分に促進される乾燥工程となる。そして、そのような乾燥処理を行う際に、タンク30内の有機物に添加する微生物としては、例えば特許文献2に記載されているように、複数種類の土着菌をベースとし、これを予め培養した複合有効微生物群が好ましく、通称、SHIMOSE 1/2/3群がコロニーの中心になる。 Next, the organic matter during fermentation will be dried over 1.5 hours. Therefore, when the pressure in the tank 30 is further reduced to −0.09 to −0.10 MPa, the water temperature in the tank is maintained at 46 to 42° C. (saturated vapor temperature), and the drying of organic substances is sufficiently promoted. It becomes a process. Then, when performing such a drying treatment, as the microorganisms to be added to the organic matter in the tank 30, for example, as described in Patent Document 2, a plurality of types of indigenous bacteria are used as a base, and this is pre-cultured. The complex effective microorganism group is preferable, and the common name is the SHIMOSE 1/2/3 group as the center of the colony.
 なお、SHIMOSE 1は、FERM BP-7504(経済産業省産業技術総合研究所生命工学工業技術研究所特許微生物寄託センター(日本国茨城県つくば市東1丁目1-3)に、2003年3月14日に国際寄託されたもの)である。また、SHIMOSE 2は、FERM BP-7505(SHIMOSE 1と同様に国際寄託されたもの)、塩に耐性を有するピチアファリノサ(Pichiafarinosa)に属する微生物であり、SHIMOSE 3は、FERM BP-7506(SHIMOSE 1と同様に国際寄託されたもの)、スタフィロコッカス(Staphylococcus)に属する微生物である。 In addition, SHIMOSE 1 was sent to FERM BP-7504 (Ministry of Economy, Trade and Industry, National Institute of Advanced Industrial Science and Technology, Institute of Biotechnology and Industrial Technology, Patent Microorganism Depositary Center (1-3, Higashi 1-3, Tsukuba, Ibaraki, Japan) on March 14, 2003. Internationally deposited). SHIMOSE 2 is a microorganism belonging to FERM BP-7505 (an international deposit similar to SHIMOSE 1) and Pichiafarinosa, which is resistant to salt, and SHIMOSE 3 is called FERM BP-7506 (SHIMOSE 1). It is a microorganism belonging to Staphylococcus).
 ここで、減圧発酵乾燥装置3による有機物の減圧発酵乾燥処理の手順について説明する。まず、有機物を含む処理対象物を減圧発酵乾燥装置3に投入する。この際、減圧発酵乾燥装置3のタンク30の投入口30aの蓋を開いて、投入装置2によって投入用箱21に収容された有機物を投入口30aから投入する。そして、投入口30aの蓋を閉じて、タンク30内を大気圧状態で密閉する。 Here, the procedure of the vacuum fermentation drying process of organic substances by the vacuum fermentation drying device 3 will be described. First, an object to be treated containing an organic substance is put into the vacuum fermentation and drying apparatus 3. At this time, the lid of the charging port 30a of the tank 30 of the reduced pressure fermentation drying apparatus 3 is opened, and the organic substances stored in the charging box 21 by the charging device 2 are charged from the charging port 30a. Then, the lid of the charging port 30a is closed to seal the inside of the tank 30 under atmospheric pressure.
 その次に、タンク30内の有機物に所定の微生物を添加した後に、図示しない大気開放バルブを閉じてタンク30内を密閉する。そして、タンク30内を減圧下で加熱して、その内部に収容した有機物の有機成分の発酵、乾燥を促進する。すなわち、蒸気ボイラー7から加熱用蒸気を供給し、タンク30内を加熱する。 Next, after adding a predetermined microorganism to the organic matter in the tank 30, the atmosphere opening valve (not shown) is closed to seal the inside of the tank 30. Then, the inside of the tank 30 is heated under reduced pressure to promote the fermentation and drying of the organic component of the organic substance contained therein. That is, heating steam is supplied from the steam boiler 7 to heat the inside of the tank 30.
 そうして加熱用蒸気によってタンク30内を加熱するとともに、撹拌シャフト32を所定の回転速度(例えば、8rpm程度)で回転させ、さらに、真空ポンプ36の作動によってタンク30内を減圧し、これにより、タンク30内の温度が微生物の活動至適環境となり、微生物による有機物の有機成分の分解が好適に促進される。なお、撹拌シャフト32の回転速度(8rpm)は一例であって、有機物の有機成分の分解が可能であれば他の値であってもよい。 Then, the inside of the tank 30 is heated by the heating steam, the stirring shaft 32 is rotated at a predetermined rotation speed (for example, about 8 rpm), and the inside of the tank 30 is depressurized by the operation of the vacuum pump 36. The temperature in the tank 30 becomes an environment in which the activity of microorganisms is optimal, and the decomposition of organic components of organic substances by microorganisms is favorably promoted. The rotation speed (8 rpm) of the stirring shaft 32 is an example, and may be another value as long as the organic components of the organic matter can be decomposed.
 このようにしてタンク30内の温度及び圧力を維持しつつ、所定の時間(例えば2時間くらい)が経過した場合、真空ポンプ36及び蒸気ボイラー7の運転を停止し、大気開放バルブを開放して大気圧状態とする。一方、撹拌シャフト32を逆回転させ、タンク30の排出部30bの蓋を開いて、タンク30から乾燥物を排出する。このとき、タンク30から排出される乾燥物は減容されている。 When a predetermined time (for example, about 2 hours) elapses while maintaining the temperature and pressure in the tank 30 in this way, the vacuum pump 36 and the steam boiler 7 are stopped, and the atmosphere release valve is opened. Set to atmospheric pressure. On the other hand, the stirring shaft 32 is rotated in the reverse direction, the lid of the discharge portion 30b of the tank 30 is opened, and the dried material is discharged from the tank 30. At this time, the dry matter discharged from the tank 30 is reduced in volume.
 そして、減圧発酵乾燥装置3によって減圧発酵乾燥処理された処理後の乾燥物は、排出コンベア41によって、異物選別機4へ向けて搬送される。つまり、排出コンベア41によって、減圧発酵乾燥装置3のタンク30下部の排出部30bから排出される乾燥物を、排出部30bよりも高い位置に設けられた異物選別機4まで搬送する。異物選別機4によって、減圧発酵乾燥装置3による減圧発酵乾燥処理では分解されない異物、具体的には、金属やプラスチック等を取り除くようにしている。 Then, the dried material after being subjected to the reduced pressure fermentation drying processing by the reduced pressure fermentation drying apparatus 3 is conveyed to the foreign matter sorting machine 4 by the discharge conveyor 41. That is, the discharge conveyor 41 conveys the dry matter discharged from the discharge section 30b below the tank 30 of the reduced pressure fermentation drying apparatus 3 to the foreign matter selector 4 provided at a position higher than the discharge section 30b. The foreign matter sorter 4 removes foreign matter that is not decomposed by the reduced pressure fermentation and drying process by the reduced pressure fermentation and drying apparatus 3, specifically, metals and plastics.
 異物選別機4は、図4に概略を示すように、磁選機42と振動ふるい機43とを備えている。磁選機42は、例えば吊り下げ式のもので、排出コンベア41上に吊り下げられている。磁選機42は、排出コンベア41によって搬送される乾燥物の中から金具や、鉄片等の磁性物を磁石によって吸着し、プーリ42a間を移動するベルト42bによって連続的に排出容器42cへ排出するように構成されている。磁選機42によって、乾燥物に混入している金具や、鉄片等の金属が除去される。 The foreign matter sorter 4 is provided with a magnetic separator 42 and a vibration sieving machine 43, as schematically shown in FIG. The magnetic separator 42 is, for example, a suspension type, and is suspended on the discharge conveyor 41. The magnetic separator 42 attracts magnetic materials such as metal fittings and iron pieces from the dried material conveyed by the discharge conveyor 41 by magnets and continuously discharges them to the discharge container 42c by the belt 42b moving between the pulleys 42a. Is configured. The magnetic separator 42 removes metal such as metal fittings and iron pieces mixed in the dried material.
 振動ふるい機43は、減圧発酵乾燥装置3から排出され、排出コンベア41によって搬送された乾燥物から、大きい異物をふるい分けるものである。振動ふるい機43には、所定の大きさの網目(開口部)を有する金網43aと、金網43aを振動させる振動モータ43bとを備えている。振動ふるい機43は、複数(例えば4つ)のコイルばね43cによって下台43dに支持されている。また、金網43aが斜め下方に向けて傾斜した状態で設けられており、金網43aの一端側(図4の左端側)が、他端側(図4の右端側)よりも低い位置に設けられている。本実施形態では、金網43aの網目が、5mm×5mmの大きさに設定されている。なお、網目のサイズは一例であって、他の値であってもよい。振動ふるい機43によって、乾燥物に混入しているプラスチック等が選別される。 The vibrating and sieving machine 43 is for sieving large foreign matter from the dried material discharged from the reduced pressure fermentation drying device 3 and conveyed by the discharge conveyor 41. The vibrating sieving machine 43 includes a wire net 43a having a mesh (opening) of a predetermined size, and a vibration motor 43b that vibrates the wire net 43a. The vibrating sieving machine 43 is supported on the lower table 43d by a plurality (for example, four) of coil springs 43c. Further, the wire net 43a is provided in a state of being inclined obliquely downward, and one end side (the left end side in FIG. 4) of the wire net 43a is provided at a position lower than the other end side (the right end side in FIG. 4). ing. In this embodiment, the mesh of the wire net 43a is set to a size of 5 mm×5 mm. Note that the mesh size is an example, and may be another value. The vibrating and sieving machine 43 sorts out plastics and the like mixed in the dried material.
 このように、振動ふるい機43は、コイルばね43cによって下台43dに対しフローティング支持されているので、振動モータ43bの駆動により、排出コンベア41から金網43aに供給された乾燥物がふるい分けられる。具体的には、乾燥物は、金網43aの網目を通過して、下方に落下し、振動ふるい機43の下方に配置された貯留容器44に貯留される。一方、乾燥物よりも大きい異物は、金網43aの網目を通過できないため、金網43aの傾斜面に沿って滑り落ちたり、転がり落ちたりしながら一端側(前方側)へ移動し、振動ふるい機43の前方下方に配置された排出容器43eに排出される。この際、プラスチック等の異物だけでなく、金網43aの網目よりも大きいサイズの乾燥物も排出容器43eに排出される。しかし、上述したように、減圧発酵乾燥装置3により発酵乾燥され、減容されることによって乾燥物は、ふるい分けに適したものになっており、異物以外の乾燥物がほとんど金網43aの網目を通過して、貯留容器44に貯留されるようになっている。 Thus, since the vibrating sieving machine 43 is supported by the coil spring 43c in a floating manner with respect to the lower table 43d, the dried product supplied from the discharge conveyor 41 to the wire net 43a is sieved by driving the vibrating motor 43b. Specifically, the dried material passes through the mesh of the wire net 43a, falls downward, and is stored in the storage container 44 arranged below the vibrating screener 43. On the other hand, since foreign matter larger than the dried product cannot pass through the mesh of the wire net 43a, it moves to one end side (front side) while sliding down or rolling along the inclined surface of the wire net 43a and vibrating and sieving machine 43. It is discharged to the discharge container 43e arranged in the front lower part of. At this time, not only foreign matter such as plastic, but also a dried product having a size larger than the mesh of the wire net 43a is discharged to the discharge container 43e. However, as described above, the dried product is fermented and dried by the reduced-pressure fermentation drying device 3 and reduced in volume, so that the dried product is suitable for sieving, and most of the dried product other than the foreign matter passes through the mesh of the wire net 43a. Then, it is stored in the storage container 44.
 このように、乾燥物から金属片やプラスチックなどの異物が除去され、貯留容器44には良質な有機肥料が貯留される。なお、本発明の実施例では最終工程で製造される乾燥物を有価物としての有機肥料として利用しているが、添加物を配合することにより、乾燥物を有価物である家畜用の有機飼料や、養殖用の有機飼料として利用してもよい。 In this way, foreign materials such as metal pieces and plastics are removed from the dried product, and high-quality organic fertilizer is stored in the storage container 44. In the examples of the present invention, the dried product produced in the final step is used as an organic fertilizer as a valuable product. However, by adding an additive, the dried product is an organic feed for livestock that is a valuable product. Alternatively, it may be used as an organic feed for aquaculture.
 <第2実施形態>
 次に、本発明の第2実施形態について図5を参照しながら説明する。第2実施形態は塩素系脱臭ガス拡散機構200のみが、第1実施形態と相違する。以下の第2実施形態の説明では、主に第1実施形態との相違点を中心に説明し、第1実施形態との共通する構成については説明を省略する。
<Second Embodiment>
Next, a second embodiment of the present invention will be described with reference to FIG. The second embodiment differs from the first embodiment only in the chlorine-based deodorizing gas diffusion mechanism 200. In the following description of the second embodiment, differences from the first embodiment will be mainly described, and description of configurations common to the first embodiment will be omitted.
 前記塩素系脱臭ガス拡散機構200は、冷却器8のファン85の外方向近傍に配置された噴霧ノズル201に一端が接続された配管202と、前記配管202の他端が開閉弁203及び薬液ポンプ204を介して接続された次亜塩素酸水収容容器205とで構成されている。 The chlorine-based deodorizing gas diffusion mechanism 200 has a pipe 202 whose one end is connected to a spray nozzle 201 arranged near the outside of the fan 85 of the cooler 8, and the other end of the pipe 202 has an opening/closing valve 203 and a chemical liquid pump. It is composed of a hypochlorous acid water storage container 205 connected via 204.
 したがって、前記開閉弁203を開にして薬液ポンプ204を駆動することにより、噴霧ノズル201からファン85の送風方向と同じ方向に次亜塩素酸水を噴霧することにより、ファン85の送風と次亜塩素酸水が混じり合ってガス化し、これら次亜塩素酸ガスが処理装置1を設置した建屋A内全体に拡散され、この次亜塩素酸ガスが悪臭成分、例えばアンモニアを分解して悪臭を脱臭するものである。 Therefore, by opening the on-off valve 203 and driving the chemical liquid pump 204, the hypochlorous acid water is sprayed from the spray nozzle 201 in the same direction as the blowing direction of the fan 85. The chloric acid water is mixed and gasified, and these hypochlorous acid gases are diffused throughout the building A in which the processing apparatus 1 is installed, and this hypochlorous acid gas decomposes a malodorous component such as ammonia to deodorize a malodorous substance. To do.
 <第3実施形態>
 同様に、本発明の第3実施形態について図6を参照しながら説明する。第3実施形態も塩素系脱臭ガス拡散機構300のみが、第1実施形態と相違する。以下の第3実施形態の説明では、主に第1実施形態との相違点を中心に説明し、第1実施形態との共通する構成については説明を省略する。
<Third Embodiment>
Similarly, a third embodiment of the present invention will be described with reference to FIG. The third embodiment also differs from the first embodiment only in the chlorine-based deodorizing gas diffusion mechanism 300. In the following description of the third embodiment, differences from the first embodiment will be mainly described, and description of the configuration common to the first embodiment will be omitted.
 前記塩素系脱臭ガス拡散機構300は、冷却器8のファン85外方向近傍に配管301の一端が開口され、その他端が開閉弁302を介して次亜塩素酸水収容容器303内部上方に開口されるようにして接続されている。一方、一端がコンプレッサー304に接続され、その他端が前記次亜塩素酸水収容容器303に収容された次亜塩素酸水溶液の内部に入るように接続された第2配管305とで構成されている。 In the chlorine-based deodorizing gas diffusion mechanism 300, one end of the pipe 301 is opened near the outside of the fan 85 of the cooler 8, and the other end is opened above the inside of the hypochlorous acid water storage container 303 via the opening/closing valve 302. Are connected in this way. On the other hand, one end is connected to the compressor 304, and the other end is composed of a second pipe 305 connected so as to enter the hypochlorous acid aqueous solution stored in the hypochlorous acid water storage container 303. ..
 ここで、前記コンプレッサー304を駆動すると、次亜塩素酸水収容容器303内の次亜塩素酸水溶液がばっ気されることになり、ここで発生した次亜塩素酸ガスが開動した開閉弁302、第1配管301を通ってファン85の送風に合流して、次亜塩素酸ガスが処理装置1を設置した建屋A内全体に拡散されて悪臭成分、例えばアンモニアを分解して悪臭を脱臭するものである。 Here, when the compressor 304 is driven, the hypochlorous acid aqueous solution in the hypochlorous acid water storage container 303 is aerated, and the opening/closing valve 302 in which the hypochlorous acid gas generated here is opened, Combining with the blast of the fan 85 through the first pipe 301, the hypochlorous acid gas is diffused throughout the building A in which the processing device 1 is installed and decomposes a malodorous component such as ammonia to deodorize a malodorous substance. Is.
 <第4実施形態>
 また同様に、本発明の第4実施形態について図7を参照しながら説明する。第4実施形態も塩素系脱臭ガス拡散機構400のみが、第1実施形態と相違する。以下の第4実施形態の説明では、主に第1実施形態との相違点を中心に説明し、第1実施形態との共通する構成については説明を省略する。
<Fourth Embodiment>
Similarly, a fourth embodiment of the present invention will be described with reference to FIG. The fourth embodiment also differs from the first embodiment only in the chlorine-based deodorizing gas diffusion mechanism 400. In the following description of the fourth embodiment, differences from the first embodiment will be mainly described, and description of the configuration common to the first embodiment will be omitted.
 前記塩素系脱臭ガス拡散機構400は、冷却器8のファン85外方向近傍に設けられたパン401と、一端が前記パン401に接続され、他端が開閉弁403及び薬液ポンプ404を介して次亜塩素酸水収容容器405に接続された配管402と、前記パン401底部裏面に配設されたヒータ406とで構成されている。 The chlorine-based deodorizing gas diffusion mechanism 400 has a pan 401 provided near the outside of the fan 85 of the cooler 8, one end of which is connected to the pan 401, and the other end of which is connected via an opening/closing valve 403 and a chemical liquid pump 404. It is composed of a pipe 402 connected to a chlorite water storage container 405, and a heater 406 arranged on the bottom rear surface of the pan 401.
 前記開閉弁403を開にして薬液ポンプ404を駆動すると、次亜塩素酸水収容容器405から配管402を経て少量の次亜塩素酸水がパン401に供給される。そこで、前記パン401裏面に設けられたヒータ406に給電すると、パン401がヒータ406で加熱され、パン401上の次亜塩素酸水がガス化して次亜塩素酸ガスが発生する。この次亜塩素酸ガスが冷却器8のファン85の送風と合流し、次亜塩素酸ガスが建屋A内全体に拡散されて悪臭成分、例えばアンモニアを分解して悪臭を脱臭するものである。 When the on-off valve 403 is opened and the chemical pump 404 is driven, a small amount of hypochlorous acid water is supplied to the pan 401 from the hypochlorous acid water storage container 405 through the pipe 402. Therefore, when power is supplied to the heater 406 provided on the back surface of the pan 401, the pan 401 is heated by the heater 406, and the hypochlorous acid water on the pan 401 is gasified to generate hypochlorous acid gas. The hypochlorous acid gas joins with the air blown by the fan 85 of the cooler 8, and the hypochlorous acid gas is diffused throughout the building A to decompose a malodorous component such as ammonia to deodorize the malodorous substance.
 <第5実施形態>
 さらに前記同様に、本発明の第5実施形態について図8を参照しながら説明する。第5実施形態も塩素系脱臭ガス拡散機構500のみが、第1実施形態と相違する。以下の第5実施形態の説明では、主に第1実施形態との相違点を中心に説明し、第1実施形態との共通する構成については説明を省略する。
<Fifth Embodiment>
Further, similarly to the above, the fifth embodiment of the present invention will be described with reference to FIG. The fifth embodiment also differs from the first embodiment only in the chlorine-based deodorizing gas diffusion mechanism 500. In the following description of the fifth embodiment, differences from the first embodiment will be mainly described, and description of configurations common to the first embodiment will be omitted.
 本発明において、前記塩素系脱臭ガス拡散機構500は、前記冷却器8のファン85近傍に一端が開口し、他端がエジェクター501の吐出口に接続した第1配管502と、一端が開閉弁503を介して次亜塩素酸水収容容器504に接続され、他端がエジェクター501の次亜塩素酸水供給口に接続された第2配管505と、一端がコンプレッサー506に接続され、他端がエジェクター501の空気導入口に接続された第3配管507とで構成されている。 In the present invention, the chlorine-based deodorizing gas diffusion mechanism 500 has a first pipe 502 having one end opened in the vicinity of the fan 85 of the cooler 8 and the other end connected to the discharge port of the ejector 501, and the open/close valve 503 at one end. Second pipe 505 connected to the hypochlorous acid water storage container 504 through the other end and the other end connected to the hypochlorous acid water supply port of the ejector 501, and one end connected to the compressor 506 and the other end. And a third pipe 507 connected to the air introduction port 501.
 したがって、前記開閉弁503を開にして次亜塩素酸水収容容器504から第2配管505を介して次亜塩素酸水をエジェクター501の供給口に供給可能とし、またコンプレッサー506を駆動し、コンプレッサー506から第3配管507を介してエジェクター501に送風すると、エジェクター501内部で次亜塩素酸水が気流に吸い込まれ、ガス化してエジェクター501吐出口から第1配管502を通って次亜塩素酸ガスを噴射することで、前記冷却器8のファン85により次亜塩素酸ガスが建屋A内全体に拡散されて悪臭成分、例えばアンモニアを分解して悪臭を脱臭するものである。 Therefore, the opening/closing valve 503 is opened so that hypochlorous acid water can be supplied from the hypochlorous acid water storage container 504 to the supply port of the ejector 501 through the second pipe 505, and the compressor 506 is driven to drive the compressor. When air is blown from the ejector 501 to the ejector 501 through the third pipe 507, the hypochlorous acid water is sucked into the air flow inside the ejector 501, gasifies, and is ejected from the ejector 501 discharge port through the first pipe 502 to the hypochlorite gas. By injecting, the hypochlorous acid gas is diffused throughout the building A by the fan 85 of the cooler 8 and decomposes a malodorous component such as ammonia to deodorize the malodor.
 なお、本発明の実施態様では塩素系脱臭水を次亜塩素酸水で説明しているが、この次亜塩素酸水は、二酸化塩素水であってもよく、もちろん亜塩素酸水であってよく、更には塩素系の脱臭水であれば使用することができる。 In the embodiment of the present invention, the chlorine-based deodorized water is described as hypochlorous acid water, but this hypochlorous acid water may be chlorine dioxide water, or, of course, chlorous acid water. Of course, chlorine-based deodorized water can be used.
 今回、開示した実施形態は全ての点で例示であって、限定的な解釈の根拠となるものではない。本発明の技術的範囲は、前記した実施形態のみによって解釈されるものではなく、請求の範囲の記載に基づいて画定される。また、本発明の技術的範囲には、特許請求の範囲と均等の意味及び範囲内での全ての変更が含まれる。 The embodiment disclosed this time is an example in all respects, and is not a basis for a limited interpretation. The technical scope of the present invention should not be construed only by the embodiments described above, but should be defined based on the claims. The technical scope of the present invention includes meanings equivalent to the scope of the claims and all modifications within the scope.
 この出願は、2018年12月26日に日本で出願された特願2018-243375号に基づく優先権を請求する。これに言及することにより、その全ての内容は本出願に組み込まれるものである。 This application claims the priority right based on Japanese Patent Application No. 2018-243375 filed in Japan on December 26, 2018. By reference to this, the entire contents of which are incorporated into the present application.
 本発明は、有機物を含む処理対象物の処理装置における脱臭装置及びその処理方法に利用することができる。 The present invention can be used for a deodorizing device and a processing method thereof in a processing device for a processing object containing an organic substance.
 1  処理装置
 2  投入装置
 3  減圧発酵乾燥装置
 30  タンク(密閉容器)
 33  凝縮部
 36  真空ポンプ
 8  冷却器
 80  冷却水経路
 86  冷却水ポンプ
 100  第1実施形態の塩素系脱臭ガス拡散機構
 200  第2実施形態の塩素系脱臭ガス拡散機構
 300  第3実施形態の塩素系脱臭ガス拡散機構
 400  第4実施形態の塩素系脱臭ガス拡散機構
 500  第5実施形態の塩素系脱臭ガス拡散機構
1 processing device 2 charging device 3 reduced pressure fermentation drying device 30 tank (closed container)
33 Condensing part 36 Vacuum pump 8 Cooler 80 Cooling water path 86 Cooling water pump 100 Chlorine deodorizing gas diffusion mechanism of the first embodiment 200 Chlorine deodorizing gas diffusion mechanism of the second embodiment 300 Chlorine deodorizing mechanism of the third embodiment Gas diffusion mechanism 400 Chlorine-based deodorant gas diffusion mechanism of the fourth embodiment 500 Chlorine-based deodorized gas diffusion mechanism of the fifth embodiment

Claims (8)

  1.  有機物を含む処理対象物を密閉容器に収容し、減圧下において所定の温度範囲に加熱しながら撹拌するとともに、微生物を利用して有機物の有機成分を分解させ、減容した乾燥物を得る減圧発酵乾燥装置と、
     前記密閉容器の凝縮部と真空ポンプを介して接続された冷却器と、
     前記凝縮部と冷却器とを冷却水ポンプを介して冷却水を循環させる冷却水循環経路と、
     前記冷却器に付設された塩素系脱臭ガス拡散機構と、を備えたことを特徴とする有機物を含む処理対象物の処理装置における脱臭装置。
    Vacuum-fermentation is carried out by accommodating an object to be treated containing organic matter in a closed container and stirring it under reduced pressure while heating it to a predetermined temperature range and decomposing organic components of organic matter using microorganisms to obtain a reduced volume dried product. A dryer,
    A condenser connected to the condensing unit of the closed container via a vacuum pump,
    A cooling water circulation path for circulating the cooling water through the cooling water pump between the condenser and the cooler,
    And a chlorine-based deodorizing gas diffusing mechanism attached to the cooler.
  2.  請求項1に記載の有機物を含む処理対象物の処理装置における脱臭装置において、
     前記塩素系脱臭ガス拡散機構は、
     前記冷却器の受水槽と、
     前記受水槽に一端が接続された配管と、
     前記配管の他端が薬液ポンプを介して接続された塩素系脱臭水収容容器と、で構成されたことを特徴とする有機物を含む処理対象物の処理装置における脱臭装置。
    A deodorizing device in a processing device for an object to be processed containing the organic matter according to claim 1,
    The chlorine-based deodorant gas diffusion mechanism,
    A water tank of the cooler,
    A pipe whose one end is connected to the water receiving tank,
    A deodorizing device in a treatment device for an object to be treated containing an organic substance, comprising: a chlorine-based deodorizing water storage container, the other end of which is connected via a chemical pump.
  3.  請求項1に記載の有機物を含む処理対象物の処理装置における脱臭装置において、
     前記塩素系脱臭ガス拡散機構は、
     前記冷却器のファンの外方向近傍に設けられた噴霧ノズルと、
     前記噴霧ノズルに一端が接続された配管と、
     前記配管の他端が薬液ポンプを介して接続された塩素系脱臭水収容容器と、で構成されたことを特徴とする有機物を含む処理対象物の処理装置における脱臭装置。
    A deodorizing device in a processing device for an object to be processed containing the organic matter according to claim 1,
    The chlorine-based deodorant gas diffusion mechanism,
    A spray nozzle provided near the outside of the fan of the cooler,
    A pipe whose one end is connected to the spray nozzle,
    A deodorizing device in a treatment device for an object to be treated containing an organic substance, comprising: a chlorine-based deodorizing water storage container, the other end of which is connected via a chemical pump.
  4.  請求項1に記載の有機物を含む処理対象物の処理装置における脱臭装置において、
     前記塩素系脱臭ガス拡散機構は、
     前記冷却器のファン外方向近傍に一端が開口され、その他端が塩素系脱臭水収容容器の内部上方に開口されるように接続された第1配管と、
     一端がコンプレッサーに接続され、他端の開口が前記塩素系脱臭水収容容器の塩素系脱臭水溶液内部に入るようにして接続された第2配管と、で構成されたことを特徴とする有機物を含む処理対象物の処理装置における脱臭装置。
    A deodorizing device in a processing device for an object to be processed containing the organic matter according to claim 1,
    The chlorine-based deodorant gas diffusion mechanism,
    A first pipe connected so that one end is opened in the vicinity of the fan outside of the cooler and the other end is opened above the inside of the chlorine-based deodorized water container.
    A second pipe, one end of which is connected to the compressor, and the other end of which is connected so as to enter the inside of the chlorine-based deodorizing aqueous solution of the chlorine-based deodorizing water storage container; A deodorizing device in a processing device for processing objects.
  5.  請求項1に記載の有機物を含む処理対象物の処理装置における脱臭装置において、
     前記塩素系脱臭ガス拡散機構は、
     前記冷却器のファン外方向近傍に設けられたパンと、
     前記パンに薬液ポンプを介して接続された塩素系脱臭水収容容器と、
     前記パンの底部裏面に配設されたヒータと、で構成されたことを特徴とする有機物を含む処理対象物の処理装置における脱臭装置。
    A deodorizing device in a processing device for an object to be processed containing the organic matter according to claim 1,
    The chlorine-based deodorant gas diffusion mechanism,
    A pan provided near the outside of the fan of the cooler,
    A chlorine-based deodorized water storage container connected to the pan via a chemical pump,
    A deodorizing device in a processing device for an object to be processed containing an organic substance, comprising: a heater disposed on the back surface of the bottom of the bread.
  6.  請求項1に記載の有機物を含む処理対象物の処理装置における脱臭装置において、
     前記塩素系脱臭ガス拡散機構は、
     前記冷却器のファン近傍に一端が開口し、他端がエジェクターの吐出側に接続された第1配管と、
     一端がエジェクターの吸込側に接続され、他端がコンプレッサーに接続された第2配管と、
     一端が前記エジェクターの塩素系脱臭水供給口に接続され、他端が塩素系脱臭水収容容器に接続された第3配管と、で構成されたことを特徴とする有機物を含む処理対象物の処理装置における脱臭装置。
    A deodorizing device in a processing device for an object to be processed containing the organic matter according to claim 1,
    The chlorine-based deodorant gas diffusion mechanism,
    A first pipe having one end opened near the fan of the cooler and the other end connected to the discharge side of the ejector;
    A second pipe having one end connected to the suction side of the ejector and the other end connected to the compressor;
    A third pipe having one end connected to a chlorine-based deodorized water supply port of the ejector and the other end connected to a chlorine-based deodorized water storage container. Deodorizing device in the device.
  7.  請求項2~6のいずれか1つに記載の有機物を含む処理対象物の処理装置における脱臭装置において、
     前記塩素系脱臭水の濃度は50~5000mg/Lであることを特徴とする有機物を含む処理対象物の処理装置における脱臭装置。
    A deodorizing device in a processing device for an object to be processed containing an organic matter according to any one of claims 2 to 6,
    The concentration of the chlorine-based deodorized water is 50 to 5000 mg/L.
  8.  有機物を含む処理対象物を密閉容器に収容し、減圧下において所定の温度範囲に加熱しながら撹拌するとともに、微生物を利用して有機物の有機成分を分解させ、減容した乾燥物を得る減圧発酵乾燥工程と、
     前記密閉容器の凝縮工程を介して接続された冷却工程と、
     前記凝縮工程と冷却工程間に冷却水を循環させる冷却水循環工程と、
     前記冷却工程に付設された塩素系脱臭ガス拡散工程と、を備えたことを特徴とする有機物を含む処理対象物の処理装置における脱臭方法。
    Vacuum-fermentation is carried out by accommodating an object to be treated containing organic matter in a closed container and stirring it under reduced pressure while heating it to a predetermined temperature range and decomposing organic components of organic matter using microorganisms to obtain a reduced volume dried product. A drying process,
    A cooling process connected through a condensation process of the closed container,
    A cooling water circulation step of circulating cooling water between the condensation step and the cooling step,
    A chlorine-based deodorizing gas diffusion step attached to the cooling step, and a deodorizing method in a treatment apparatus for an object to be treated containing an organic matter.
PCT/JP2019/050390 2018-12-26 2019-12-23 Deodorization device in treatment apparatus for organic matter-containing substance to be treated, and deodorization method for deodorization device WO2020137986A1 (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115121592A (en) * 2022-07-11 2022-09-30 北京四良科技有限公司 Micro-aerobic enzymolysis system and process for dining table residual food with heat energy recycled

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS56136559A (en) * 1980-03-28 1981-10-24 Nippon Kasei Chem Deodorizing method and its device
JPS58143821A (en) * 1982-02-18 1983-08-26 Fuso:Kk Method for deodorizing malodorous gas
JP2002301143A (en) * 2001-04-09 2002-10-15 Henmi Denki Engineering:Kk Deodorization-sterilization apparatus
JP2005053741A (en) * 2003-08-04 2005-03-03 Business Plan Kk Apparatus for producing chlorine dioxide
JP2008064345A (en) * 2006-09-05 2008-03-21 Miike Iron Works Co Ltd Drying device
JP2012100718A (en) * 2010-11-08 2012-05-31 Dairy Techno Inc Interior disinfecting and deodorizing apparatus
JP2013075248A (en) * 2011-09-29 2013-04-25 Miike Iron Works Co Ltd Vacuum fermentation dryer

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS56136559A (en) * 1980-03-28 1981-10-24 Nippon Kasei Chem Deodorizing method and its device
JPS58143821A (en) * 1982-02-18 1983-08-26 Fuso:Kk Method for deodorizing malodorous gas
JP2002301143A (en) * 2001-04-09 2002-10-15 Henmi Denki Engineering:Kk Deodorization-sterilization apparatus
JP2005053741A (en) * 2003-08-04 2005-03-03 Business Plan Kk Apparatus for producing chlorine dioxide
JP2008064345A (en) * 2006-09-05 2008-03-21 Miike Iron Works Co Ltd Drying device
JP2012100718A (en) * 2010-11-08 2012-05-31 Dairy Techno Inc Interior disinfecting and deodorizing apparatus
JP2013075248A (en) * 2011-09-29 2013-04-25 Miike Iron Works Co Ltd Vacuum fermentation dryer

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115121592A (en) * 2022-07-11 2022-09-30 北京四良科技有限公司 Micro-aerobic enzymolysis system and process for dining table residual food with heat energy recycled
CN115121592B (en) * 2022-07-11 2023-08-25 北京恒诺信达生物技术有限公司 Dining table residual food micro-oxygen enzymolysis system and technology capable of recycling heat energy

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