WO1999057243A1 - Liqueurs de culture microbienne contenant des micro-organismes de caracteristiques differentes vivant en symbiose et des metabolites de ceux-ci, vecteurs et adsorbants contenant les composants actifs de ces liqueurs de culture et leur utilisation - Google Patents
Liqueurs de culture microbienne contenant des micro-organismes de caracteristiques differentes vivant en symbiose et des metabolites de ceux-ci, vecteurs et adsorbants contenant les composants actifs de ces liqueurs de culture et leur utilisation Download PDFInfo
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- WO1999057243A1 WO1999057243A1 PCT/JP1999/002346 JP9902346W WO9957243A1 WO 1999057243 A1 WO1999057243 A1 WO 1999057243A1 JP 9902346 W JP9902346 W JP 9902346W WO 9957243 A1 WO9957243 A1 WO 9957243A1
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- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12P—FERMENTATION OR ENZYME-USING PROCESSES TO SYNTHESISE A DESIRED CHEMICAL COMPOUND OR COMPOSITION OR TO SEPARATE OPTICAL ISOMERS FROM A RACEMIC MIXTURE
- C12P39/00—Processes involving microorganisms of different genera in the same process, simultaneously
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- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01N—PRESERVATION OF BODIES OF HUMANS OR ANIMALS OR PLANTS OR PARTS THEREOF; BIOCIDES, e.g. AS DISINFECTANTS, AS PESTICIDES OR AS HERBICIDES; PEST REPELLANTS OR ATTRACTANTS; PLANT GROWTH REGULATORS
- A01N63/00—Biocides, pest repellants or attractants, or plant growth regulators containing microorganisms, viruses, microbial fungi, animals or substances produced by, or obtained from, microorganisms, viruses, microbial fungi or animals, e.g. enzymes or fermentates
- A01N63/30—Microbial fungi; Substances produced thereby or obtained therefrom
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- A—HUMAN NECESSITIES
- A61—MEDICAL OR VETERINARY SCIENCE; HYGIENE
- A61L—METHODS 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
- A61L9/00—Disinfection, sterilisation or deodorisation of air
- A61L9/01—Deodorant compositions
- A61L9/013—Deodorant compositions containing animal or plant extracts, or vegetable material
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
- B09C1/10—Reclamation of contaminated soil microbiologically, biologically or by using enzymes
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
- C02F3/341—Consortia of bacteria
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- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F11/00—Other organic fertilisers
- C05F11/08—Organic fertilisers containing added bacterial cultures, mycelia or the like
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- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
- C05F17/10—Addition or removal of substances other than water or air to or from the material during the treatment
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- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
- C05F17/20—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation using specific microorganisms or substances, e.g. enzymes, for activating or stimulating the treatment
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- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F3/00—Fertilisers from human or animal excrements, e.g. manure
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- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
- C12N1/00—Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
- C12N1/14—Fungi; Culture media therefor
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/12—Halogens or halogen-containing compounds
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/20—Heavy metals or heavy metal compounds
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/32—Hydrocarbons, e.g. oil
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/16—Nature of the water, waste water, sewage or sludge to be treated from metallurgical processes, i.e. from the production, refining or treatment of metals, e.g. galvanic wastes
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/20—Nature of the water, waste water, sewage or sludge to be treated from animal husbandry
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/34—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
- C02F2103/40—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the manufacture or use of photosensitive materials
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/141—Feedstock
- Y02P20/145—Feedstock the feedstock being materials of biological origin
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P60/00—Technologies relating to agriculture, livestock or agroalimentary industries
- Y02P60/20—Reduction of greenhouse gas [GHG] emissions in agriculture, e.g. CO2
- Y02P60/22—Methane [CH4], e.g. from rice paddies
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/30—Wastewater or sewage treatment systems using renewable energies
- Y02W10/37—Wastewater or sewage treatment systems using renewable energies using solar energy
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
Definitions
- the present invention relates to a microorganism culture solution, a method for producing the same, and a use thereof. More specifically, a microorganism culture solution in which anaerobic microorganisms and aerobic microorganisms originally incompatible with each other coexist and contain an enzyme as a metabolite thereof, a method for producing the same, and an active ingredient in the culture solution
- the present invention relates to a carrier and an adsorbent material containing, and their use in the agricultural and environmental fields.
- Japanese Examined Patent Publication No. 4-4-2355 discloses that rhizobia and azotopactor or photosynthetic bacteria and sulfur bacteria are added to an aqueous solution of plant ash with sucrose or maltose and inoculated into a sterilized medium.
- a mixture of cultures of nitrifying bacteria, yeast, thermophiles, Bacillus subtilis, and Pseudomonas bacteria is used separately to promote the maturation of compost, improve soil, increase fertilizer effectiveness, and reduce residual pesticides. It discloses the ability to detoxify and control diseased microorganisms.
- horticulture such as bonsai and gardening is now widespread, and plants such as ornamental plants, edible plants and herbs are cultivated not only by plant growers but also by ordinary households. ing.
- a solid medium for plant cultivation is usually placed in a so-called container, such as plantan or Ueki, and plant seeds or bulbs are planted or plant seedlings are transplanted to grow plants. It is common to do it.
- the solid medium used to grow such plants contains a large number of pests, eggs, and molds that inhibit plant growth.
- a solid plant culture medium such as soil by pathogens such as eggs of various insects, insects themselves, white silkworm, powdery mildew, root-knot disease, mottled scab, scab, rust, etc.
- pathogens such as eggs of various insects, insects themselves, white silkworm, powdery mildew, root-knot disease, mottled scab, scab, rust, etc.
- harmful substances such as pesticides may be mixed.
- eggs are laid on plants or medium cultivated by insects and the like, which may propagate and adversely affect the plants.
- Japanese Patent Publication No. 4-422355 describes that a mixed solution of various microorganisms is sprayed on a solid medium for plant cultivation such as soil or the plant itself.
- rhizobia and azotobacter or photosynthetic bacteria and sulfur bacteria are added to an aqueous solution of plant ash with sucrose or maltose and a growth promoting solution of the microorganism according to the present invention, and inoculated into a sterilized medium at 25 ° C.
- a suitable mixture of microbial mixed cultures obtained by culturing for a suitable period of time before and after, and separately preparing cultures of nitrifying bacteria, yeast, thermophiles, Bacillus subtilis, and Pseudomonas in a microorganism growth promoting solution according to the present invention. It is said to have the ability to promote maturity of compost, improve soil, increase fertilizer effectiveness, detoxify pesticide residues, and control diseased microorganisms.
- these bacterial groups even if these bacterial groups are used, it has a disadvantage that it takes a long time to exert an effect after application, and the effect lasts for a short time. In addition, these fungi could not be applied to plants grown in containers.
- EM bacteria an effective bacterium group that is considered to coexist with both anaerobic bacteria and aerobic bacteria
- EM bacteria especially bacteria mainly composed of lactic acid bacteria, soil
- improved methods and insecticides have been developed, the synergistic effect of the EM bacteria group cannot be expected because only the aerobic bacteria group and the breathable bacteria group are substantially present.
- EM bacteria were used, fermentation materials called EM blur had to be used, and the range of use was extremely limited.
- Sestone is a general term for particles suspended in water, and refers to organisms from swimming organisms and non-organisms from soil and fine particles. These sestons often aggregate to form clumps.
- Organic seston can be a habitat for micro-organisms, but it is desirable to remove it because it deteriorates the transparency of water and causes rot such as coconut due to decay of organic seston.
- inorganic sestone contained in wastewater from chemical factories is a so-called lump of particles containing harmful substances, and it is desirable to remove it.
- the target waters include inorganic wastewater such as sewage treatment wastewater, food processing wastewater, human waste treatment wastewater such as swine raising and livestock production, organic wastewater such as eutrophic lake water, and wastewater from chemical factories. Due to the wide variety of wastewaters, there are a wide variety of sestons, and a single flocculant may not be able to handle them.
- coconut was generated in the eutrophic hydrosphere, and it was desired to remove it.
- it has been desired to remove oil that has spilled into sea areas in the event of accidents involving petroleum tankers, etc., and there is a demand to develop effective means for these.
- Examples of the wastewater treatment method include, for example, JP-A-55-86559, JP-A-60-137394, Kaihei 6-71293, JP-A-9 Japanese Patent Publication No. 206678/1999 describes a method of treating wastewater separately with anaerobic microorganisms and aerobic microorganisms. These methods have limited treatment targets, and it has been difficult to say that they are effective and sufficient. At present, no treatment method has been developed that can centrally cope with contaminations of different origins.
- organic halogen compounds including chlorine and bromine are specified as specified chemical substances or specified chemical substances, and many of them are substances causing environmental problems.
- Typical examples thereof include dioxins, polychlorinated biphenyls, and benzene-substituted aromatic organic compounds such as chlorobenzene, tetrachloroethylene, trichloroethylene, dichloromethane, carbon tetrachloride, 2-dichloroethylene, 1,1-dichloroethylene, cis_1,2-dichloroethylene, 1,1,1 trichloroethane, 1,1,2-trichloroethane, 1,3-dichloropropene And other aliphatic organic halogen compounds.
- an organochlorine compound which is characterized in that contaminants of an organochlorine compound are dechlorinated in a reducing atmosphere and under neutral conditions in the presence of at least one kind of heterotrophic anaerobic microorganism and metallic iron.
- a method for purifying contaminants is described in Japanese Patent Application Laid-Open No. 10-216694, and heterotrophic anaerobic microorganisms present in soil include methanogens (e.g., Me thanosarcina, Me thanothrix, Me thanobacterium).
- Me thanobrevibacter genus Me thanobrevibacter genus, Sulfate reducing bacteria (for example, Desulfovibrio, DesI fotomacuIum, Desulfobacterium, Desiffobacter, Desulfococcus), acid-producing bacteria (for example, CI ostridium) Acetivibrio, Bacteroides, Rum inococcus, facultative anaerobic microbes (eg, Baciius, Lact ObacciIlus ⁇ , Aeromonas, Genus Streptococcus, Micrococcus) and the like.
- Sulfate reducing bacteria for example, Desulfovibrio, DesI fotomacuIum, Desulfobacterium, Desiffobacter, Desulfococcus
- acid-producing bacteria for example, CI ostridium
- Acetivibrio Bacteroides, Rum inococcus, facultative anaerobic microbes (eg, Baciius, Lact Obacci
- Solids and liquids such as incineration ash, soda glass, soil, semiconductor processing wastewater, and plating wastewater contain various heavy metals such as chromium, manganese, cobalt, nickel, zinc, lead, and mercury. There is a need to remove these metals based on the action of microorganisms.
- photographic waste liquids include those containing various harmful substances.
- Photographic films and photographic papers generally include silver halide emulsions (eg, silver bromide, silver iodide, silver iodobromide), stabilizers (eg, benzotriazole) as photosensitive materials. , Azaindolizines, etc.), various chemicals such as color sensitizers (e.g., orthochromatic match, panchromatic, superpanchromatic dyes, etc.), and hardeners (e.g., aldehyde compounds).
- silver halide emulsions eg, silver bromide, silver iodide, silver iodobromide
- stabilizers eg, benzotriazole
- Azaindolizines, etc. various chemicals such as color sensitizers (e.g., orthochromatic match, panchromatic, superpanchromatic dyes, etc.), and hardeners (e.g., aldehyde compounds).
- intensification work is performed with a chromium compound such as potassium dichromate, a mercury compound such as mercuric chloride, etc.
- a mixture or permanganate ream is used to reduce the pressure.
- porous adsorbents Another area in which there is a demand for detoxification of chemical substances is porous adsorbents.
- Activated carbon and other porous adsorbent materials are used as adsorbent materials for treating harmful substances in various fields such as filters for water treatment and filters for deodorization.
- porous adsorbing materials exhibit an adsorbing effect by adsorbing a substance to be treated into a large number of pores of the adsorbing material itself, but the adsorbing ability decreases when a certain amount of the substance is adsorbed.
- Such used porous material is usually recovered and regenerated, but the harmful substances adsorbed at that time are released from the porous adsorbent material to the outside of the system, and released out of the system during regeneration. Measures must be taken to treat and detoxify harmful substances, which requires enormous costs.
- river sand has been used as fine aggregate such as concrete and asphalt, but its supply has been declining. At present, river sand itself is becoming more polluted and contains various harmful substances.
- incinerated ash contains harmful substances such as lead, zinc, heavy metals and organochlorine compounds, they are treated and used as aggregates in the form of slag.
- a harmful substance such as an organic chlorine compound may be contained, and in some cases, such a harmful substance must be treated as a pretreatment. Insufficient metal removal.
- it is used only as aggregate with high grain size, not as fine aggregate.
- the method of grinding waste glass into sand and using it was very expensive to contain impurities such as lead in the glass or to grind and use it for fine aggregate.
- sand containing salt existing on the sandy beaches of the coast is not suitable for fine aggregate because it contains salt.
- Garbage disposal is another area where there is a demand for utilizing the action of microorganisms.
- Waste is generally classified into household waste and business waste, and these wastes are currently dumped in landfill facilities or treated by incineration to reburn. is the current situation.
- garbage such as food waste is occupied.
- a large amount of garbage is also discharged from various facilities such as restaurants, grocery stores, convenience stores, accommodation facilities, and medical facilities. It is said that these garbage, together with household garbage and business garbage, account for about 30% of the total waste to be treated.
- Garbage disposal method by such microorganisms 1) garbage the ways and 2) a method of Ru is extinguished garbage a C 0 2 and H 2 0 volume reduction decompose or substantially the composting It is roughly divided into two types.
- the method of composting garbage is generally performed by using a composting container called a composter or a container having a ventilation means called a compoplanter having both functions of a composter and a planter.
- the composter is composed of a container body consisting of a vent, a space, a heat insulation layer and a lid.
- a material such as rice husk ( ⁇ ⁇ nutrient soil) is laid in the container body, and the same material as the material is placed on it.
- the garbage is laid at a depth, and a fermentation agent containing cultivation soil and bacilli and actinomycetes is further poured on the garbage. In this way, the composting is promoted by alternately stacking culture soil and garbage to promote fermentation of garbage. In this way, after about one month, the garbage in the composter is fermented to produce a compost.
- Such a method of composting garbage with microorganisms can be performed with inexpensive equipment, but it takes a long time of one month or more to compost the garbage, and the garbage that can be processed in one operation Has the disadvantage of being limited in amount. Furthermore, the fertilizer obtained as a result of processing garbage has a strong odor, and when such fertilizer is applied, there is a problem such as generation of fusarium.
- Such a garbage disposal apparatus is composed of a sealed container provided with a vent, a heat insulating layer, an aeration unit, a drainage unit and a stirring unit, and the bottom of the container is partitioned by a porous plate.
- Materials for improving the air permeability are spread on the porous plate, and on the porous plate are germ beds for microorganisms, and sawdust and the like for the purpose of adjusting the water content of the garbage.
- the specified microorganisms are charged into the container, and the garbage is further charged.
- the mixture is stirred by aeration means such as a pump under aeration. It is decomposed into water and reduces the volume and volume of garbage.
- aeration means such as a pump under aeration. It is decomposed into water and reduces the volume and volume of garbage.
- Such a processing apparatus can process about 1 kg of garbage, but the actual volume reduction rate of garbage is as low as 60% to 80%. The body also needs to be replaced every three to four months.
- sulfur dioxide, nitrogen oxides, etc. were generated when the garbage was decomposed, so it was necessary to take countermeasures, and the processing equipment was expensive.
- an ultra-reduction device for garbage As a device to reduce a large amount of garbage, an ultra-reduction device for garbage has been developed.
- This apparatus is composed of a closed container having a volume of about 500 to 600 liters, which has stirring means, aeration means, deodorizing means and the like. Almost all wood chips such as cedar chips are put into this container as a material, and about 20 kg of garbage is put in and 100 to 300 liters of air per minute is intermittently supplied. The garbage is decomposed by microorganisms that live in the chips by agitation.
- Methods for desalinating seawater include the multi-stage flash method, the multiple effect method, and the reverse osmosis method.
- the multi-stage flash method and the multiple-effect method are effective for large-scale plants such as national plants, desalination of seawater by the reverse osmosis method, which requires relatively little capital investment, is becoming the mainstream at present.
- Japanese Patent Application Laid-Open No. 10-12838 / 25 discloses that seawater is passed through a reverse osmosis membrane separation device in which two stages of seawater are arranged in series using a single pump.
- a method for obtaining fresh water with a low boron concentration is described in Japanese Patent Application Laid-Open No. H10-1283225 in order to pump water produced from a reverse osmosis membrane module and a water collection pipe of the reverse osmosis membrane module.
- a desalination apparatus equipped with a water pump is described.
- an object of the present invention is to establish a microbial technology that can respond to these uses, and to provide a group of microorganisms and metabolites thereof that exhibit excellent effects in various agricultural and environmental fields.
- Another object of the present invention is to provide an application method in the fields of agriculture and environment based on these microbial technologies.
- Yet another object of the present invention is to find new ways of applying these microbial technologies.
- the present invention relates to the following items.
- the microbial culture solution according to the above item 1 including one obtained by crossing Basidiomycete oyster mushroom and Tamagitake mushroom.
- microorganism culture solution according to the above item 1 further containing a photosynthetic fungus.
- the microbial culture solution according to the above item 3 further comprising a carbon-degrading enzyme.
- a method for producing a microorganism culture solution comprising:
- a method for producing a microbial culture solution comprising the steps of: introducing a group of photosynthetic bacteria and continuing culturing further under anaerobic dark conditions.
- step (4) diluting the culture obtained in step (4) 2 to 4 times with the solution obtained in step (3)
- a method for producing a microorganism culture solution comprising:
- porous adsorbent material according to the above item 10, wherein the porous adsorbent material is based on activated carbon.
- the porous adsorbent material is a used porous adsorbent material, and is immersed in the above solution or its diluent for a time sufficient to decompose the components adsorbed in the pores of the porous material. 13.
- a filter comprising the adsorbent according to the above item 10.
- Plant-derived fiber is coniferous sawdust, crushed thinned wood, crushed fallen trees Item 17.
- the soil base material according to the above item 16 which is a material, a fir, a buckwheat hull, a primary-treated building material, or a mixture thereof.
- a method for improving soil comprising mixing the soil base material according to paragraph 16 or 17 with a fertilizer and laying 1 to 100 cm on the soil to be treated.
- a method for improving soil comprising spraying a solution diluted with water.
- a method for optimizing a plant system comprising a container for plant cultivation, a solid medium for plant cultivation, and a cultivated plant,
- a method for optimizing a plant system comprising sealing a container and holding the container for a period of time sufficient to kill pests, eggs and harmful microorganisms against the plant in a culture medium and a cultivated plant.
- Organic fertilizer obtained by adding a solution obtained by diluting the microorganism culture solution according to any one of the above items 1 to 4 with water or the carrier according to the above item 8 to livestock manure. .
- a garbage decomposition bed obtained by immersing a plant-derived fiber in a solution obtained by diluting the microbial culture solution according to any one of the above items 1 to 4 with water.
- a method for treating garbage wherein the garbage to be treated is put into the garbage decomposition bed described in paragraph 32 or 33 above and stirred to decompose the garbage into an odorless liquid.
- a liquid fertilizer containing an odorless liquid obtained by the method according to the above item 34.
- a method for treating a solid characterized by stirring, mixing, and washing the carrier according to the above item 8 with a solid to be treated containing a harmful substance or a salt or a mixture thereof.
- Fine aggregate comprising sand treated by the method of paragraph 37 above.
- a reduced structure comprising the carrier according to the above item 8.
- a method for removing cocoa which comprises spraying a solution obtained by diluting the microorganism culture solution according to any one of the above items 1 to 4 with water onto cocos generated by eutrophication.
- a method for treating seston which comprises introducing the carrier according to the above item 8 into a water area containing seston to aggregate the seston.
- a method for treating a water area which comprises introducing the carrier according to the above item 8 into a water area containing the sludge and decomposing the sludge.
- a seston flocculant comprising the carrier according to the above item 8.
- a method for treating a liquid comprising the step of passing salt-containing water once or more than once through a filter containing the adsorbent material according to item 15 to remove salt.
- the method for treating a liquid according to the above item 48 comprising a step of charging the carrier according to the above item 8 into water containing salt and stirring the pretreatment.
- a method for treating a liquid comprising charging the carrier according to the above item 8 to a liquid containing a harmful substance.
- a method for treating a liquid comprising charging the carrier according to the above item 8 into a liquid containing a harmful substance and stirring the liquid.
- a method for treating a liquid comprising passing a liquid containing a harmful substance once or a plurality of times through a filter containing the adsorbent material according to the above item 15.
- step b) passing the liquid treated in step a) one or more times through the filter containing the adsorbent material according to claim 15 above.
- step a) is performed under stirring.
- the liquid containing harmful substances to be treated is a waste liquid containing heavy metals, organic halogen compounds, or petroleum, a plating waste liquid, a semiconductor waste liquid, a photographic development processing waste liquid, a dye-containing waste liquid, a sewer water, and a waste liquid containing these.
- a supply port for supplying water to be treated
- a filtration means comprising one or more filters comprising the adsorbent material of paragraph 15 above;
- the liquid processing apparatus according to the above item 56 or 57, further comprising a pretreatment water tank provided with a stirring means, and comprising means for conveying the liquid to the filtration means.
- a method for treating a gas comprising spraying a diluted solution obtained by diluting the microorganism culture solution according to any one of the above items 1 to 4 with a gas to be treated.
- a method for treating a gas comprising passing the gas to be treated through a filter containing the adsorbent material according to the above item 15.
- a liquid deodorant comprising a diluent obtained by diluting the microorganism culture solution according to any one of the above items 1 to 4 with water.
- a liquid decoloring agent comprising a diluent obtained by diluting the microorganism culture solution according to the above item 4 with water.
- a method for removing harmful substances from building materials comprising spraying or immersing a diluent obtained by diluting the microbial culture solution according to paragraph 4 with water into the building materials.
- a fungicide comprising a diluent obtained by diluting the microorganism culture solution according to the above item 4 with water.
- a plant resuscitation agent comprising a diluent obtained by diluting the microorganism culture solution according to the above item 4 with water.
- a water treatment filter comprising the filter containing the adsorption material according to the above item 15.
- a water purifier including the water treatment filter according to paragraph 69 above.
- a water detergent comprising the carrier according to item 8 above.
- a water purifier comprising the porous adsorbent according to item 10 above.
- FIG. 1 is a cross-sectional view illustrating an example of an apparatus for treating pests in one embodiment of the present invention.
- FIGS. 2 to 3 are cross-sectional views showing an example of an apparatus for processing liquid processing in one embodiment of the present invention
- FIG. 4 (a) to 4 (d) are graphs for comparing the adsorption capacity of the adsorbent according to the present invention with the conventional adsorbent, and FIG. 4 (a) shows the adsorption of formaldehyde on the adsorbent of the present invention.
- Fig. 4 (b) is a graph showing the adsorption capacity when formaldehyde is adsorbed on a conventional adsorbent material
- Fig. 4 (c) is a graph showing the adsorption capacity when ammonia is added to the adsorbent material of the present invention.
- Fig. 4 (d) is a graph showing the adsorption capacity when ammonia was adsorbed on a conventional adsorbent material.
- an aerobic microorganism and a specific basidiomycete are cultured in a bioactive agent which the present inventors previously applied as a specific culture medium, and then the anaerobic microorganism is cultured in the culture medium.
- a bioactive agent which the present inventors previously applied as a specific culture medium
- the anaerobic microorganism is cultured in the culture medium.
- OM a group of microorganisms obtained by the process and a metabolite of the microorganism
- OME a solution
- OME a solution
- Bioactive agent In preparing OME in the present invention, first, an aerobic microorganism group and a basidiomycete are introduced into a bioactive agent, and the cells are aerobic under aerobic conditions, that is, at room temperature and normal pressure for 2 to 5 weeks. Preferably, these bacterial groups are cultured for 20 to 30 days.
- the bioactive agent used in this case is described in Japanese Patent Application Laid-Open No. H5-224496, which was previously filed by the present inventors. As disclosed in Japanese Patent Publication No. 2 (1), (1) crushing a protein mainly composed of animal protein, (2) mixing the crushed product with cereals and yeast, and (3) heating the fermented product.
- an aerobic microorganism group and a basidiomycete are introduced into the bioactive agent to start cultivation.
- the aerobic microorganism group is a microorganism group generally existing in soil or the like and living in the presence of oxygen.
- Means These representative aerobic bacteria include those commonly found in nature, such as Bacillus and Cytopha-Gaseromonas, which belong to the group of Gram-negative aerobic bacteria, aerobic spore bacteria, and euphoric bacteria. There is no particular limitation as long as the effects of the present invention described below are not impaired.
- the most common source of aerobic microorganisms is humus obtained by decaying broadleaf leaves and the like in nature, and is preferably decay in progress.
- the dosage of such aerobic biosources into the bioactive agent is generally in the range of 1 to 7%, preferably 2 to 6% by weight of humus per tonne of bioactive agent. If the input amount of the source is less than the above range, it takes a long time to proceed with the culture. Conversely, when the amount exceeds the above range, the culture medium becomes viscous, and the culture medium with poor air ventilation becomes patchy.
- basidiomycetes derived from mushrooms belonging to the Pleurochoceae family preferably, a Japanese Patent Application Laid-Open No. (5)
- a mushroom-derived basidiomycete (referred to as Pleolotusenu) belonging to the Pleurocetaceae described in Japanese Patent No. 2528284 is used as an essential component.
- other basidiomycetes derived from other mushrooms are introduced together. May be. Generally, such basidiomycetes are introduced in the form of an extract.
- the input amount at this time is also arbitrary as in the case of the aerobic microorganism, but is preferably in the range of 1 to 7 liters, more preferably 1 to 5 liters, as basidiomycete extract per ton of the bioactive agent.
- the introduction of this basidiomycete greatly increases the productivity of cellulase.
- the aerobic microorganisms and the basidiomycetes are introduced into the bioactive agent in this manner, and the resulting mixture is subjected to aerobic conditions, that is, at room temperature and normal pressure under air rate for 2 to 5 weeks, preferably 20 to 3 weeks. On day 0, these bacterial groups are cultured. When the culture is completed in this way, the culture solution that had emitted an off-flavor at the beginning of the introduction becomes odorless (hereinafter referred to as OM stock solution).
- This OM stock solution is a culture solution containing the aerobic microorganisms, basidiomycetes and their metabolites.
- anaerobic microorganisms are added to the OM stock solution thus prepared, and the culture is further continued.
- the anaerobic microorganisms to be introduced include bacterial groups belonging to two groups, Gram-negative anaerobic eubacteria and Gram-positive fermentative eubacteria.
- a source of such anaerobic bacteria is sewage sludge.
- the amount of such an anaerobic microorganism source to be added to the bioactive agent is generally in the range of 1 to 7% by weight, preferably 2 to 6% by weight of the anaerobic microorganism source per ton of OM stock solution.
- the cultivation takes a long time, and if the input amount exceeds the above range, the viscosity including the sludge increases, and as a culture solution, there are factors that hinder the progress of the next step.
- After introducing the anaerobic microorganism supply source into the OM stock solution leave it under anaerobic conditions, that is, without aeration, generally at room temperature and normal pressure for 2 to 5 weeks, preferably 20 to 30 days, and culture. To continue.
- the off-flavor from the supply source disappears, and an odorless OM solution is obtained.
- the OM solution contains anaerobic microorganisms and their metabolites in addition to the components of the OM stock solution.
- the anaerobic microorganism is cultured at the same time, during the culturing stage, or after culturing.
- a group of photosynthetic bacteria can be added and cultivation can be performed under anaerobic dark conditions.
- examples of such a photosynthetic bacterium group include cyanobacteria, green sulfur bacteria, green non-sulfur bacteria, and red sulfur bacteria. By culturing these, the reducing power is increased.
- the amount of these optional photosynthetic bacteria to be added is generally in the range of 1 to 10 liters, preferably ⁇ 2 to 5 liters, per ton of the liquid.
- a culture solution (hereinafter abbreviated as ⁇ ) is produced.
- ⁇ is diluted with water or an aqueous medium, preferably 300 to 500
- diluent can also be used as a diluent after diluting it by a factor of 0, more preferably by a factor of 500 to 3000 (hereinafter simply referred to as a diluent).
- ⁇ can be used by adsorbing it on a carrier as described below.
- the second aspect of the present invention relates to an OME component-containing carrier (hereinafter, abbreviated as DCP) obtained by treating fine carbonaceous material with 0 ME or a diluent thereof to dissolve the carbonaceous material.
- DCP OME component-containing carrier
- OME has an enzyme that has the effect of dissolving carbonaceous material as described above.
- OME diluted solution or a diluent diluted with water or aquatic medium
- the carbonaceous material is dissolved by the action of the carbon-decomposing enzyme in the OM active ingredient, and the OME active ingredient (enzyme) is dissolved.
- microorganisms are absorbed into the carbonaceous material to obtain a carrier containing the OME active ingredient having a special function.
- the finely divided carbonaceous material used in the production of DCP refers to fine powder of graphite-based carbon and amorphous carbon, and is generally used at a low temperature, preferably at a low temperature of about 400 ° C or lower.
- the source is not limited as long as it is obtained by combustion and achieves the object of the present invention.
- Examples of carbon sources of DCP include woody materials, cellulosic carbon such as crushed wood (wood chips) and vegetation, plant-based carbon derived from plants containing carbohydrates, protein-based carbon derived from animals and plants containing proteins, and the like.
- Examples include petroleum-based carbon obtained from petroleum, and these carbons can be used alone or in combination. It is particularly preferred to use carbon of these various origins which is discarded as so-called garbage.
- the ratio between the carbonaceous material and the OME diluent is not particularly limited as long as the object and effects of the present invention are not impaired. Not something.
- an aqueous solution of a microorganism may be introduced into the carbonaceous material, or the carbonaceous material may be introduced into the aqueous solution of the microorganism.
- the carbonaceous material is gradually introduced into the aqueous microbial solution with stirring.
- the finely-divided carbonaceous material and the aqueous solution of the bacterial group are mixed and stirred, and the carbonaceous material is gradually decomposed.
- it becomes a sludge-like carrier, and the load of stirring becomes small.
- the cake-like or sludge-like carrier can be used as it is, but it can be dried, for example, by sunlight or air drying, to give a sludge-like carrier containing a desired moisture content, or a fine powdery carrier.
- OM component-containing carrier can be used as it is, but it can be dried, for example, by sunlight or air drying, to give a sludge-like carrier containing a desired moisture content, or a fine powdery carrier.
- the porous adsorbent material is immersed in OME or a diluent thereof, and is left for a predetermined period of time. (Hereinafter abbreviated as "RCS").
- the treatment of the porous adsorbent material in the RCS is not particularly limited as long as the OME active ingredient can be introduced into the pores.
- activated carbon SOG sand, Taisheng stone, barley stone, Iio stone, tourmaline, various ceramics Activated carbon is preferred.
- shape of the porous adsorbent used in the present invention is not particularly limited, and may be granular, fibrous, or molded. Particular preference is given to being granular.
- the porosity of the porous adsorbent used in the present invention is OME or its dilution.
- the immersion conditions at this time are not particularly limited, but the immersion can be carried out usually at least 8 hours after water washing, preferably at least 24 hours at normal temperature and normal pressure, with or without aeration.
- the used adsorbent is regenerated at the same time, it is preferable to immerse for 24-72 hours. If activated carbon is used as the adsorbent, immersion for more than 72 hours is not preferable because carbon will dissolve out.
- the OM cultured in the present invention contains OM active components, that is, metabolites of these microorganisms in addition to various microorganisms such as aerobic microorganisms, anaerobic microorganisms, basidiomycetes, and photosynthetic bacteria. Contains enzymes.
- OME has a carbonaceous dissolving effect. It can be assumed that the OME active ingredient contains carbon-degrading enzymes. Therefore, it can be used as a unique carrier (DCP) and an adsorption material according to the present invention.
- OM active ingredients cause the following microbial-enzymatic reactions selectively depending on the substance to be treated (OM, OME. DCP, RCS) 0
- R-CH-OR ' + H 2 0 - ⁇ RH + H0-CH-0R " (In the formula, R and R ′ each independently represent a hydrocarbon group which may be substituted.)
- R and R ′ each independently represent a hydrocarbon group which may be substituted.
- R, R ′ and R ′′ each independently represent a hydrocarbon group which may be substituted.
- R represents an optionally substituted hydrocarbon group
- X represents a halogen atom
- R represents an optionally substituted hydrocarbon group
- X represents a halogen atom
- Sawdust and bark of conifers contain phenols, tannins, lignin, and essential oils, which are substances that inhibit plant growth.
- Phenolic acids, non-phenolic acids, and higher fatty acids in raw sawdust inhibit the elongation of seed roots and lateral roots.
- sawdust wood has an extremely high CZN ratio of 1000 to 1500, and is hardly decomposable due to the strong binding of cellulose and lignin. It is possible to decompose these hardly decomposable components successively by continuous cometabolism such as gliding eubacteria, myxobacteria, actinomycetes and filamentous fungi in the OM.
- OM, OME, DCP, and RCS can be used as assimilative substances that coexist with such microorganisms.
- OME has an action of removing heavy metals such as zinc, lead, tin, nickel, chromium, copper, con- trol, manganese, mercury, cadmium, and dross components in semiconductors. Although it is not clear by what mechanism heavy metals are removed, as a result of the inventor's experiments on plating waste liquid and semiconductor waste liquid, it has been found that these heavy metals can be substantially removed.
- heavy metals such as zinc, lead, tin, nickel, chromium, copper, con- trol, manganese, mercury, cadmium, and dross components in semiconductors.
- organic halogen compounds for example, halogen-substituted aromatic organic compounds such as dioxins, polychlorinated biphenyls, and chlorobenzene, tetrachloroethylene, trichloroethylene, dichloromethane, carbon tetrachloride, 1,2 —Dichloroethylene, 1,1-dichloroethylene, cis-1,2-dichloroethylene, 1,1,1-trichloroethane, 1,1,2-trichloroethane, 1,3-dichloropropene, etc.
- Anaerobic and facultative anaerobic chemoheterotrophs contained in OM and OME have either anaerobic respiration or fermentation mechanisms.
- Anaerobic respiration is essentially the same biochemical pathway as aerobic metabolism (aerobic breath), instead terminal electron acceptor is oxygen electron transport chain, nitrate (N0 3 -), sulfate (S0 4 2 —), fumaric acid or trimethylamine oxide.
- N0 3 one, S0 4 case 2 _ of, acts as a reducing product your final electron acceptor.
- Ammonia becomes odorless by the following reaction in OM or OME.
- Ammonia water also presents ammonium carbonate, and when the supply of oxygen is small, the ammonium ion (NH 4 _) changes from nitrous acid to nitric acid due to digestive bacteria and becomes odorless.
- DCP has excellent seston aggregation ability regardless of the type of seston.
- DCP also has the function of decomposing sludge deposited on the bottom. It is not clear by what reaction mechanism the microbial-containing carrier of the present invention decomposes the head opening for such action, but the microorganism-containing carrier according to the present invention is used for water containing sludge deposited on the bottom. When the carrier was applied, the sludge deposited on the bottom was gradually removed within 2 weeks to 1 month after application.
- OM and OME, DCP, RSC are applicable over the entire pH range. It also has the effect of returning pH to neutral (see Examples below).
- OM and OME can exert these effects over the entire pH range. According to the experiment of the inventor, in the treatment of strongly acidic waste liquid generated during the production of umeboshi, When NaOH having a pH of 14 or more was treated, it was possible to treat each, and the pH after the treatment was close to neutral.
- OME has the effect of reducing BOD and COD.
- the OME, DCP, and RSC that have the unique effects described above can be applied to the following applications.
- OME OME
- OME enzyme OME
- OME diluent DCP
- RCS RCS
- the soil matrix that can be used in this embodiment is a plant-derived cellulosic material that is applied to the soil to rejuvenate the aggregated structure, and that is capable of decomposing cellulose by OME or a diluent thereof into soil.
- cellulosic materials include, for example, sawdust, coniferous forest leaves, hay, bark, husk (for example, rice husk, buckwheat husk, etc.), cut straw, primary-treated building waste, fallen trees, and the like.
- it can be used as a mixture of two or more.
- the sawdust is easily available and inexpensive, especially in coniferous forests that have been difficult to treat in the past.
- the soil base material is applied to the soil to be treated.
- soil depleted by pesticides soil in a dormant state in rotation, acidity It can be applied to soil acidified by rain, desertified soil, sandy soil around rivers, etc., and sandy soil with salt on beaches.
- the amount of soil base material to be laid depends on the type of soil to be treated, the climate, the plant to be cultivated, etc., but it is usually 10 171 to 100 171, preferably 2 cm to 50 cm. is there.
- OME preferably 0ME with enhanced cellulase-producing ability is sprayed onto the soil on which the soil base material is laid, and treated.
- the object of the present invention is to use a culture solution in which anaerobic bacteria and aerobic bacteria are conventionally symbiotic and are said to have cellulose degradability. It was surprising that the desired effect was obtained by simultaneously using the basidiomycete culture solution.
- 0 ME can be used in a stock solution, it is usually used by diluting it to 500 to 2000 times, preferably ⁇ 100 times with water.
- the dry soil material may be sprayed until it is completely wet.
- the soil matrix according to the present invention is applied to the target soil, and OME, preferably 0 ME with enhanced cellulase-producing ability, is sprayed on the soil matrix, and is sprayed for several days or more, preferably for one month or more. If left for more than 2 months, the soil is improved to be ready for plant cultivation. OME may be additionally sprayed when the progress of soil improvement is not remarkable. This fog process is performed as needed, but a good organic soil can be provided by mixing the soil base material with sewer sludge, livestock dung, etc., and performing the turning process about once or three times a month.
- the first feature of these soil base materials is that they can completely decompose the harmful substances present in the fibrous materials and garbage to be treated by the toxic substance decomposition action of OME.
- OM E is converted into fiber derived from crops harvested using fertilizers such as fallen leaves and straws of fruit trees and the like obtained by spraying pesticides, and manure obtained from livestock and poultry fertilizers administered antibiotics. These components are completely harmless by spraying diluent and composting Be transformed into
- the second characteristic is that in addition to ordinary soil, soil depleted by pesticides, dormant soil during rotation, soil acidified by acid rain, desertified soil, sandy soil around rivers, etc. It can be applied to sandy soils containing salt on beaches, etc., and converted to good crop cultivation soils.
- the soil becomes reduced soil, and it is possible to produce crops that are resistant to various pathogens and pests.
- the cellulosic material derived from plants was applied to the soil in advance, and then the OME diluent was sprayed.
- these cellulosic materials and 0ME were previously mixed. It is also possible.
- a method for optimizing a plant system comprising a container for plant cultivation, a solid medium for plant cultivation, and a cultivated plant using OME is provided. That is, the system is completely placed in a sealed container, and the sealed container is completely filled with the OME or OME diluent, and then the sealed container is sealed.
- the plant system is capable of controlling the above-mentioned pests by keeping it for a sufficient time to kill harmful microorganisms to the plant.
- the sealed container is transparent and is kept under exposure to sunlight.
- solid media for plants or cultivation of basidiomycetes can be treated using OMII. That is, by immersing the culture medium with ⁇ ⁇ ⁇ or ⁇ ⁇ ⁇ diluent for a time sufficient to kill the pests and their eggs present in the culture medium, the pests or the eggs in the solid medium can be killed. It becomes possible.
- FIG. 1 is a cross-sectional view for explaining a method for optimizing a plant system comprising a container for plant cultivation, a solid medium for plant cultivation, and a cultivated plant of the present invention.
- plant container 1 for plant cultivation The plant system S composed of the solid medium 2 and the cultivated plant 3 is placed in the sealed container 4.
- the plant system applicable in the present invention is not particularly limited, and the container 1 in which the solid medium 2 is laid is Applies to all plants 3 grown within.
- Representative examples of plants applicable to the present invention include trees such as pine and plum, various plants of annual and perennial plants, various herbs, potatoes, edible plants such as tomato, parsley, and eggplant.
- the solid culture medium for plant cultivation includes, for example, culture soil obtained by spoiling black soil, fallen leaves, and the like. Usually, a suitable solid culture medium corresponding to these plants 3 is selected and cultivated.
- containers 1 for cultivating these plants 3 are also diversified and various, and for example, various containers made of wood, ceramics, and plastics such as flowerpots and plantans are appropriately selected.
- Such a plant S is placed in a sealed container.
- the sealed container can completely seal the plant by completely inserting the plant, and even if the culture solution or the diluent described below is filled, the solution is not filled.
- the shape and material are not particularly limited as long as they do not leak, and a bag-like material can be used in addition to a usual plastic container.
- a container that is at least partially transparent can be held while being exposed to sunlight, and the state of the plant system can be observed at the time of holding. It is preferably used, and particularly preferably a transparent container as a whole. It is also possible to put one plant S in the container, but if there is an insertion space, it is possible to put two or more.
- the inside of the sealed container 4 is filled with OME or OME diluent 5.
- OME organic compound
- Such an OME (diluent) 5 has the ability to kill pests, eggs, and harmful microorganisms, the ability to decompose chemicals such as pesticides, and the ability to improve media such as soil.
- the plant system S is maintained using the culture solution described in Japanese Patent Publication No. 4-4-2325, the cultivated plant 3 causes root rot, whereas such an OME solution 5 is used. Surprisingly, it has been found that it does not cause root rot when used.
- the container After filling the inside of the hermetic container 4 containing the plant with the OME (diluent) 5 in this way, the container is closed and kept for a predetermined time.
- the treatment time at this time is maintained for a time sufficient to kill the pests and their eggs in the medium and the cultivated plants, but this time depends on the type of plant, the type of solid medium, the status of pests, etc. Different, but usually not a few minutes It is held for several hours, for example, 2 minutes to 10 hours.
- This operation can be performed only once, but it can also be performed several times after a certain number of days. Furthermore, when the plant 3 is slightly withering, it can be reactivated and revived by the treatment of the present invention. In addition, when treated in this way, the solid medium 2 can be used repeatedly even after the life of the plant has ended.
- not only the plant system but also a medium for plant cultivation or a medium for mushroom cultivation can be treated with OME to control the medium from pests.
- the plant system described above is used except that it is not always necessary to use a closed container and there is no cultivated plant, so that the treatment time can be extended and the medium can be more completely activated. Therefore, the repeated description is omitted. It is also possible to eliminate and reuse harmful insects such as mites that have spread in the culture medium during mushroom cultivation.
- OM or OME is sprayed and washed on a plant, especially a rhizosphere of a plant, which has been violated by a pathogen such as blight, clubroot, scab, scab, powdery mildew, rust, etc.
- a pathogen such as blight, clubroot, scab, scab, powdery mildew, rust, etc.
- the soil in which the rhizosphere of these plants was acidic and concreted was softened and changed to a reduced state, making it possible to prevent the transmission of pathogenic bacteria.
- these pathogens are killed by the attack of basidiomycetes, the active ingredient of OME, and then degraded by hydrolytic enzymes. Specifically, the whole plant that has been violated by these pathogens and pests is immersed in the OME diluent. Plants treated in this way are revived.
- the OME diluent or DCP By adding the OME diluent or DCP to livestock manure, these manure can be made odorless and good fertilizer can be obtained. At this time, the ideal compost can be obtained by constantly mixing and stirring the coniferous sawdust.
- OME OME enzyme
- OME diluent OME diluent
- DCP OME diluent
- Table 2 shows examples of environmental response based on 0 ME active ingredients.
- the garbage can be treated using a garbage disposal material (garbage decomposition floor) produced based on OME.
- a garbage disposal material garbage decomposition floor
- the material for treating garbage in the present invention is based on a plant-derived cellulosic material.
- the plant-derived cellulosic material are the same as the soil matrix described in the above item A-I. It is preferable to mix hard-to-decompose materials such as peach and so on, preferably in a ratio of about 1 to 0.3 to 2, since air circulation is improved.
- the garbage disposal material thus produced When the garbage disposal material thus produced is brought into contact with the garbage, the garbage is decomposed and fermented by the OME hydrolase and microorganisms in the garbage disposal material. However, at the same time as the odor in the garbage is completely removed, the odor components of sulfide and nitride are completely decomposed.
- the garbage disposal method it is possible to deodorize the garbage simply by putting the garbage into the garbage disposal material and stirring the garbage. It is also possible to further apply the above-mentioned plant-derived cellulosic material on garbage, and it is also possible to further apply an OME solution to this cellulosic material. Alternatively, the garbage disposal material of this embodiment can be applied. In particular, if the above-mentioned cellulosic substance is applied to the garbage and the OME solution is further applied, or if the garbage disposal material of this embodiment is applied, the odor is removed when the garbage is treated. preferable.
- garbage disposal material of this aspect it is possible to dispose of garbage in the conventional composter and compoplanter, and it is also possible to apply the garbage disposal material of this aspect to, for example, a garbage landfill to treat garbage. It is possible. By treating in this way, garbage can be easily treated without generating offensive odor.
- the garbage When left for several hours in this way, the garbage differs depending on the components of the garbage, but the garbage begins to decompose as soon as it is put in, becomes odorless, and becomes completely liquid after about 24 to 36 hours. This liquid can be applied as an excellent odorless liquid fertilizer.
- the material for treating garbage according to this embodiment can be produced by a simple method of immersing a plant-derived cellulosic material and OME or a diluent thereof.
- Materials for garbage disposal can be used as they are as existing composters, compo-planters, and garbage decomposition floors for garbage disposal equipment.
- the obtained food waste material When the obtained food waste material is brought into contact with food waste, it can be processed into a liquid without generating odor, and food waste can be processed at low cost and easily.
- the obtained liquid can be used as a good odorless liquid fertilizer.
- the DCP is mixed with sand containing at least one component to be removed selected from the group consisting of salt, organic harmful substances and heavy metals, and stirred to substantially remove the components to be removed from the sand. It can be removed.
- the sand containing at least one component to be removed selected from the group consisting of salt, organic harmful substances, and heavy metals is sand containing salt such as sea sand, and / or zinc, force dope, Sand containing harmful substances such as heavy metals such as nickel, aromatic halogen compounds (eg, PCBs, dioxins), halogenated hydrocarbons (eg, dichloromethane, trichloromethane, carbon tetrachloride, etc.), and azo compounds.
- substantially removing means that these salts and harmful substances are removed to values below the administrative guidelines of the government and local governments.
- the present invention relates to a method for treating incinerated ash, which comprises mixing and stirring DCP into incinerated ash to substantially remove harmful substances in the incinerated ash.
- the treatment By performing the treatment in this manner, it is possible to substantially remove heavy metals such as lead and zinc and harmful substances such as organic halogen compounds in the incinerated ash, and to obtain the obtained incinerated ash and DCP.
- the mixture can be reused as fine aggregate for structures such as concrete, and similarly, a reduced structure excellent in water purification action can be obtained.
- the DCP is mixed and stirred with waste glass containing at least one component to be removed selected from the group consisting of salt, organic harmful substances and heavy metals, and waste glass discharged in the glass manufacturing process.
- the present invention relates to a method for treating waste glass and cakes, which substantially removes components to be removed from sand.
- waste glass such as soda lime glass and cake-like by-products mainly composed of calcium carbonate generated from a soda ash manufacturing plant in the glass manufacturing process
- sodium chloride, lead, soda ash and the like are treated. It can be removed and can be used as coarse aggregate in the form of slag or can be refined and used as fine aggregate.
- DCP is used to treat sand containing salt, incinerated ash, river sand, and the like to obtain a mixture of DCP and fine aggregate.
- salty sands When treating salty sands, mix with at least 1 kg, preferably 1-4 kg, of DCP per ton of sand. When the salt-containing sand and DCP are mixed and stirred in this manner, salt such as sodium chloride contained in the sand is removed.
- the amount of DCP added is less than the above amount, the removal of salts is insufficient. Also, there is no upper limit on the amount of addition because the obtained sand is used as fine aggregate, that is, That is, it can be appropriately selected depending on the degree of demand such as a case where the production of a strongly reduced structure is required or a case where it is sufficient to simply treat the salt. Generally, 2 to 5 kg per ton of sand is sufficient.
- the mixing and stirring may be performed in a dry state, but it is preferable to add water and mix in a slurry. For example, it can be treated by mixing and stirring DCP and sand slurry to be treated using an ordinary kneader, a device marketed by Mixer Daiki Rubber Industries Co., Ltd. under the name of MD Cyclone. .
- river sand and sea sand containing harmful substances can be further treated by DCP.
- Treat chemical hazards such as heavy metals such as zinc, lead, chromium, and cadmium, and organic halogen compounds (aromatic organic halogen compounds such as PCB, dioxin, and chlorophenol, mono- or poly-halogen hydrocarbons) as the target harmful substances.
- organic halogen compounds aromatic organic halogen compounds such as PCB, dioxin, and chlorophenol, mono- or poly-halogen hydrocarbons
- the amount of DCP added is appropriately selected depending on the type and concentration of the harmful substance, but is generally the same as that of sand containing salt.
- the treatment of river sand that contains almost no salt or harmful substances is also an object of this mode.
- this embodiment encompasses all the mixture of sand and DCP.
- a mixture is used as fine aggregate, an excellent reduced-type structure as described later can be obtained.
- incineration ash means all incineration ash including fly ash.
- incinerated ash contain metals such as lead, zinc, chromium, mercury, and other various heavy metals such as dioxins, and chemical hazards such as PCBs.
- the amount of DCP to be added depends on the type and amount of harmful substances contained in the incinerated ash, but is generally about 1 to 5 kg DCP per ton of incinerated ash.
- the treatment When the treatment is performed in this way, it is possible to stabilize the metal by adsorbing metals such as heavy metals such as lead, zinc, and chromium, and to substantially reduce organic halides such as dioxin and PCB. Is removed.
- the treatment of the incinerated ash in this embodiment can be utilized not only as a fine aggregate using the treated mixture but also as a pretreatment for treating by a conventionally known method such as landfilling after removing the metal. It is.
- the pH value is automatically adjusted by the action of microorganisms and enzymes of DCP, so that they can be used for landfills, etc., and reused as fine aggregate. It is also safe. The same method can be used for treating incinerated ash as for sand. If further safety is required, the used RCS should be washed and then immersed again in OME liquid to mix and use as fine aggregate.
- the mixture of DCP and sand or incineration ash thus treated has excellent properties similar to OME, DCP, RSC and the like.
- the structure manufactured with the DCP mixture when used for general sewerage and agricultural sewerage, it has the action of neutralizing pH and reducing BOD and COD. It can be used as a very good structure having a purifying action. It should be noted that a structure having the same effect can be produced by directly adding DCP to the raw concrete material.
- salt and harmful substances are substantially removed from sand containing salt and harmful substances by a simple method of adding, mixing, and stirring DCP.
- the resulting mixture can be used as a suitable fine aggregate.
- DCP is added, mixed and stirred by a simple method. It is possible to remove harmful substances from the incineration ash, and the incineration ash thus treated can be secondarily treated by a conventional method or used directly as excellent fine aggregate.
- the obtained DCP mixture can be used as fine aggregate for producing a reduced structure having excellent water purification action.
- ready-mixed concrete for reduction-type structures at the same time as treating salt and harmful substances.
- a process such as drying is not required, and the treatment of harmful substances is directly performed.
- ready-mixed concrete can be manufactured.
- Table 3 below shows examples of the correspondence to liquids based on the action of the OME active ingredient in the present invention.
- Liquid treatment methods are roughly divided into: a) a method of spraying OME (removal of cocoa, etc.), b) a method of spraying DCP, c) a filter containing RCS after spraying DCP as a pretreatment if desired. Through the method.
- water containing these sestons for example, organic wastewater including sewage treatment wastewater, food processing wastewater, human waste treatment wastewater such as swine and livestock raising, and eutrophic lake water and chemical plant wastewater.
- organic wastewater including sewage treatment wastewater, food processing wastewater, human waste treatment wastewater such as swine and livestock raising, and eutrophic lake water and chemical plant wastewater.
- water treatment can be performed by separating these sediment and / or suspended matter by filtration, etc., which is different from the case of using a conventional polymer flocculant or sulfate band. You don't have to.
- various sestones can be treated regardless of whether they are inorganic or organic.
- DCP also has the function of decomposing sludge deposited on the bottom. It is not clear by what reaction mechanism the microbial-containing carrier of the present invention decomposes the head opening for such action, but the microorganism-containing carrier according to the present invention is used for water containing sludge deposited on the bottom. When the carrier was applied, the sludge deposited on the bottom was gradually removed within 2 weeks to 1 month after application.
- DCP selectively absorbs heavy oil.
- the heavy oil adsorbed on the carrier of the present invention is decomposed into gaseous carbon dioxide, water, etc. by the 0 ME active component and made harmless.
- sulfur content in heavy oil Sulfur dioxide and other components generated by the action of sulfur bacteria present in seawater are instantaneously decomposed and hydrogen sulfide is generated by the interaction of sulfur oxidizing bacteria and sulfate reducing bacteria. It is instantly decomposed and made harmless.
- ME active components have a dehalogenating effect, heavy oils containing these components are also rendered harmless.
- seawater treated in step a) can be desalinated by passing it through a filter made of RCS.
- such DCP is mixed with seawater under forced stirring and then forcedly stirred, and the stirring means at this time is such that the DCP and seawater come into sufficient contact and seawater is desalinated by the action of DCP.
- the stirring means at this time is such that the DCP and seawater come into sufficient contact and seawater is desalinated by the action of DCP.
- examples thereof include stirring with a mixer or the like and stirring with a jet of water, particularly preferably forced stirring with an OHR line mixer sold by Seika Sangyo Co., Ltd.
- This step of contacting DCP with seawater and forcibly stirring may be performed once or may be performed several times as necessary.
- This is a forced stirring device of the type in which two types of fluids different from the OHR line mixer are passed through different spiral flow paths and then collided and contacted.
- a fluid A in which DCP is added to a part of seawater in advance and an untreated seawater B are brought into contact with each other and reacted.
- the seawater thus treated with about 80% salinity is passed through a filter containing RCS.
- the filter made of the RCS thus formed the filter is completely desalinated.
- saltwater in the seawater can be removed and desalinated simply by passing it through RCS.
- DCP and RCS can be used for wastewater containing various harmful substances, wastewater containing strongly acidic or strongly alkaline pH values, wastewater containing metals, wastewater with odor, colored wastewater, and wastewater combining these. Wastewater treatment is possible. a) Waste liquid treatment by DCP
- DCP which is a powder carrier
- the treatment of waste liquid by DCP in this embodiment is 1) waste liquid with relatively low contamination, and 2) treatment through an RSC filter described later is difficult. It is used as a pretreatment for the treatment of natural liquids, for example, lakes, marshes, seawater, rivers, etc. with a large treatment area, and 3) the treatment with the RSC filter described later.
- Waste liquid treatment is performed by passing waste liquid through a filter containing an adsorbent material. Waste liquid treatment by RCS is performed as final treatment. Especially for highly contaminated effluents, this can be done by passing them through an RCS filter several times.
- the treatment of the wastewater of each of these DCP and RCS and the combined wastewater treatment are basically the same as the methods for desalination of seawater.
- Such effluents include wastewater from chemical factories, especially wastewater containing toxic substances such as plating wastewater, photographic wastewater, dye wastewater, PCBs, dyes, etc., and wastewater from food factories.
- Plum vinegar waste liquid discharged in Such seawater and harmful substances can be treated by a liquid treatment device as shown in Figs.
- This device consists of a supply port 2 for supplying water to be treated, filtration means F composed of one or more RCS filters as claimed (Fig. 2), and a water storage tank 3 for storing the treated water. . Also connected to water tank 3 It is preferable to include a means for supplying the treated and treated liquid to the filtration means, and after a predetermined number of treatments, supply treated water to the filter to regenerate the filter.
- a pretreatment water tank 5 provided with a stirring means 6 for treatment by the DCP, and to connect this with a filtration means F and a liquid transport means 7 such as a pump.
- odors derived from organic compounds for example, odors caused by the deterioration of animals and plants, animal manure, methane, mercaptan and the like, and odors derived from inorganic compounds, for example, ammonia, hydrogen sulfide, etc. It can absorb, adsorb, decompose, and deodorize PCBs, nitrogen oxides, etc.
- gas treatment methods are roughly: a) removing the OME diluent by spraying it on the gas, b) introducing DCP into the OME diluent and applying it to the gas source, and c. ) If the gas to be treated is a gas that passes through a closed environment, eg a flue, it can be treated by passing it through a filter containing one or more RSCs. Further, in the treatment of dioxin and the like, it is possible to treat with an OME mist trap or the like, or in the same manner as in the method described in Japanese Patent Application No. 91-291467.
- the OME, DCP, and RCS in the present invention can be used in various forms other than the above applications. Hereinafter, examples of these uses will be described. Since the OME diluent has a deodorizing effect as described above, it can be used as a liquid deodorizer for households, chemical factories, etc., for example, in the livestock industry, etc., by putting it in a spray container such as an atomizer or sprayer. is there.
- the OME diluent can be used in the form of a spray container in the same manner as an agent for controlling pathogenic bacteria of plants and an agent for plant fleas as described above.
- insect repellent effects can be imparted by immersing a building material such as wood in an OME diluent for a short period of time, preferably within one day. At this time, care must be taken when immersed in the OME diluent for a long time because cellulose in wood and the like will be decomposed.
- DCP or RCS or a mixture thereof can be used as a powder deodorant for refrigerators, shoes and the like.
- RCS Since RCS has a function of removing harmful substances, especially chlorine, and has a bactericidal effect, it is necessary to introduce a filter incorporating RCS as a filter for water treatment into a filter for drinking water purification equipment and a shower head. It can be used as a filter for a shower or as a filter for an air purifier.
- DCP can be put into a nonwoven fabric or the like and introduced into, for example, a tea bag-like bag, and used as a detergent for water in a tank or a pond, a detergent for bath water, or the like.
- RCS is used as a filter agent for the purification device of the aquarium, it is possible to keep the water transparent without replacing it for more than 8 months.
- Orient Green Co., Ltd. is based on broadleaf trees as a source of aerobic microorganisms per ton of bioactive material sold under the brand name Revitaly Aminone ⁇ 5% by weight of mulch and oyster mushrooms and Tamagotake mushrooms as basidiomycete sources. 5% by weight of the mushroom extract was added, and the mixture was cultured at normal temperature and normal pressure under aeration for 30 days. Different at the initial stage of culture It smelled, but after 30, it was odorless.
- the photosynthetic bacteria group sold by Orient Green Co., Ltd. under the trade names of Green Amin and Red Amin under the same conditions as the photosynthetic bacteria group was added to the culture solution at 1.5 liters per ton of the culture solution, and then added to the culture solution.
- the OM solution was produced by culturing for a day.
- the culture solution thus obtained was diluted with three times the volume of the previously obtained 0 M solution to produce a 0 ME solution.
- mice were tested. In this guideline, no death was observed at the maximum dose that could be administered (2 ml per 100 g body weight (20 mIg), and no abnormalities were observed at the time of the autopsy.
- the lethal dose by oral administration was found to be 2 OmI / kg or more for both sexes.
- the cultivation was carried out in the same manner as in Example 1 except that basidiomycetes were not introduced in the 0M liquid production method, and the aerobic microorganisms and anaerobic microorganisms described in A culture solution was prepared.
- the carbon derived from the burned plants was immersed in a diluent obtained by diluting OME obtained in Example 1 with water 1000 times. After about 3 to 7 days, the carbonaceous material melted and DCP was obtained (DCP slurry). This DCP slurry was air-dried to obtain DCP powder. Similarly, carbon fines derived from plants burned at low temperature were immersed in a diluent obtained by diluting the culture solution obtained in Comparative Example 1 with water 1,000 times. No change was seen.
- Example 4 Comparative Examples 2, 3 and Control Example 1 (Improvement of sandy soil containing salt)
- Example 1 softwood sawdust was laid as a soil base material on a sandy beach so as to have a thickness of about 5 to 1 Ocm, and some chicken dung was put into it, and the OM E obtained in Example 1 was placed there. Was diluted about 100 times with water and sprayed so that the soil base material was sufficiently moistened (Example 1).
- a culture solution of a microorganism conventionally known to have cellulose degradability (a culture solution according to Japanese Patent Publication No. 4-42555) (Comparative Example 2) and a culture solution of Comparative Example 1 (Comparative Example 2) were sprayed.
- a control only chicken dung was added (Control Example 1).
- Example 4 After leaving each of these treated soils for two weeks, tomato, edamame, watermelon, pumpkin, eggplant, komatsuna, and sweet potato were cultivated as plants, but the soil of Example 4 could yield good quality crops. , Comparative Examples 2 and 3, and Comparative Example 1 could not be harvested and Example 5, Comparative Examples 4 and 5, Control Example 2 (treatment of various soils)
- Example 5 Similar microbes as in Example 1, Comparative Examples 2 and 3, and Control Example 1 for sandy soil made of commercially available sand, soil that has lost its reagglomeration structure due to pesticides, acidified soil, and slash-and-burn soil
- OME Example 5
- Example 4 and 5 the soil using the culture solution of Comparative Examples 2 and 3 was obtained.
- Control Example 2 untreated soil
- the method according to the present invention shows very excellent effects in a short period of time. It is noteworthy that the progress of the sandy soil to the soil can be visually observed (approximately 30% becomes soil three months after application).
- Example 6 Relief of a plant caused by blight and scab Akamatsu, a blight disease blight disease of about 80 years old, was dug up, the affected area was excised by surgery, and the entire Akamatsu was diluted sufficiently with a 1,000-fold dilution of the OME solution obtained in Example 1 with water. Washed. Thereafter, the surgical portion was coated with DCP slurry and allowed to dry. Further, when the soil was thoroughly washed with a diluent obtained by diluting the OME solution of Example 1 with water 1,000 times and planted, emergence of new shoots 2 hours after the treatment was observed.
- Example 2 a 1,000-fold dilution of the OM solution described in Example 1 was used.
- the OM diluent obtained in Example 1 was sprayed with 300 liters of the OM diluted solution obtained in Example 1 on the cucumber at the end of the cultivation period, which was infected with the powdery mildew, and the leaf surface and the soil were treated. One week later, the spread of powdery mildew was suppressed. After about two weeks, 100 liters of OM diluent was similarly sprayed onto the soil and foliage. One week later, there was a harvest similar to a regular cucumber that was not affected by powdery mildew.
- the pest control of 4a of the strawberry house (20a) in which the insects were generated was performed using the 1,000 times dilution of the OM solution described in Example 1.
- 200 liters of OM diluent was sprayed on leaves and soil.
- One week after spraying it was observed that plant growth was enhanced compared to unsprayed areas.
- the leaves and stems of the strawberry had elasticity.
- carcass of a insect was observed. Damage to the untreated portion due to the occurrence of beetles began to appear, so the entire house was sprayed with 350 liters of OM diluent and rinsed with 600 liters of OM diluent.
- 500 liters of the OM diluent was sprayed on the entire house and rinsed with 500 liters of the OM diluent. No occurrence of leptopods was observed.
- Example 9 garbage disposal
- the diluted OME obtained by diluting the OME obtained in Example 1 by 1,000 times with water was sprayed and mixed on a mixture of coniferous sawdust and peaches in a ratio of 1: 1 to produce a garbage decomposed bed. .
- OM 3 cc obtained in Example 1 was diluted with 200 cc of water and washed with 200 cc of incinerated ash containing 0.6 mg of Zr. Thereafter, washing with water was performed twice. As a result, the lead content in the incineration ash was 0.015 mgZ liter (measured according to JIS K01 0 261.2)
- Example 1 (Removal of heavy metals in incineration ash by OM)
- Table 5 The incineration ash containing heavy metals shown in Table 5 was subjected to the same method as in Example 9 to remove heavy metals.
- Table 5 shows the amount of heavy metals in the OM cleaning solution before water washing and the heavy metal content in the incinerated ash after treatment.
- the measurement is based on the atomic absorption spectrophotometry.
- N. D. means below the detection limit.
- Example 3 1 liter of waste liquid containing cyanide, acetic acid, mercury, etc. after photo printing from a small-scale DPE store was placed in a 2-liter transparent container, and 3 mg of the DCP obtained in Example 2 was added thereto. After stirring with a magnetic stirrer for 0 minutes, these harmful substances and odors were completely removed. Thereafter, the RCS obtained in Example 3 was caught in a funnel and passed therethrough. Table 6 shows the measurement results of COP, total nitrogen and COD treatment before and after DCP treatment and No. 3 treatment.
- Example 17 The same treatment as in Example 17 was performed using a waste liquid containing 40,000 mg / L of PCB, and as a result, the content of PCB was 0.1 ppm.
- Plum vinegar-containing waste liquid discharged during the production of umeboshi having the following characteristics: 1 ton. 4 liters of DCP obtained in Example 2 was added, stirred well, filtered with sand, and then RSC obtained in Example 3 was filtered twice through a filter containing 4 liters. Table 8 shows the results.
- the solution of Example 3 was used. The treatment was performed using the filter containing the RCS obtained in the above. Table 9 shows the results.
- Example 22 Removal of odor from protein spoilage
- Example 21 1 and Comparative Example 6 Comparison of gas adsorption capacity between RCS and activated carbon
- the present invention described above has the following excellent features.
- An aerobic microorganism group, an anaerobic microorganism group, and a basidiomycete belonging to at least one kind of mushroom family coexist with microorganisms having different properties characterized in that these metabolites include enzymes.
- a carrier obtained by adsorbing the components of the solution on the finely divided carbonaceous material, and a porous material obtained by adsorbing the components of the solution on the porous material absorb and absorb harmful substances It has various functions such as decomposition, deodorization, and decolorization, and is applicable to various uses in the agricultural and environmental fields.
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Priority Applications (5)
Application Number | Priority Date | Filing Date | Title |
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AU36285/99A AU771630B2 (en) | 1998-05-06 | 1999-05-06 | Microbial culture liquors containing microorganisms differing in characteristics and living in symbiosis and metabolites thereof, carriers and adsorbents containing the active components of the culture liquors and utilization of the same |
EP99918307A EP1077252A1 (en) | 1998-05-06 | 1999-05-06 | Microbial culture liquors containing microorganisms differing in characteristics and living in symbiosis and metabolites thereof, carriers and adsorbents containing the active components of the culture liquors and utilization of the same |
CA002331966A CA2331966A1 (en) | 1998-05-06 | 1999-05-06 | Microbial culture liquors containing microorganisms differing in characteristics and living in symbiosis and metabolites thereof, carriers and absorbents containing the active components of the culture liquors and utilization of the same |
US09/673,655 US6649397B1 (en) | 1998-05-06 | 1999-05-06 | Microbial culture liquors containing microorganisms differing in characteristics and living in symbiosis and metabolites thereof, carriers and adsorbents containing the active components of the culture liquors and utilization of the same |
US10/601,668 US20050101003A1 (en) | 1998-05-06 | 2003-06-24 | Microbe culture containing microgrobes having different characters living in symbosis with each other and metabolites therefrom, carrier and absorbing material containing the active ingredients of the culture and utilization thereof |
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JP15979998 | 1998-05-06 | ||
JP10/159799 | 1998-05-06 | ||
JP18799398 | 1998-06-01 | ||
JP10/187993 | 1998-06-01 | ||
JP10/194906 | 1998-06-08 | ||
JP19490698 | 1998-06-08 | ||
JP23792098 | 1998-07-21 | ||
JP10/237920 | 1998-07-21 | ||
JP10/244323 | 1998-07-28 | ||
JP24432398 | 1998-07-28 | ||
JP24432498 | 1998-07-28 | ||
JP10/244324 | 1998-07-28 | ||
JP10/250301 | 1998-08-01 | ||
JP25030198 | 1998-08-01 | ||
JP10/279282 | 1998-08-25 | ||
JP27928298 | 1998-08-25 | ||
JP10/294400 | 1998-09-09 | ||
JP29440098 | 1998-09-09 | ||
JP10/316764 | 1998-10-05 | ||
JP31676498 | 1998-10-05 | ||
JP11/33348 | 1999-01-04 | ||
JP3334899 | 1999-01-04 | ||
JP11/105704 | 1999-03-09 | ||
JP10570499 | 1999-03-09 | ||
JP11/156926 | 1999-04-26 | ||
JP15692699 | 1999-04-26 |
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US (2) | US6649397B1 (ja) |
EP (1) | EP1077252A1 (ja) |
CN (1) | CN1300318A (ja) |
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CA (1) | CA2331966A1 (ja) |
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Citations (20)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5586593A (en) * | 1978-12-25 | 1980-06-30 | Kubota Ltd | Treating method of waste water of garbage incinerating plant |
JPS6027672A (ja) * | 1983-07-25 | 1985-02-12 | 日本ライフ株式会社 | 微生物の培養物を利用して、堆肥の腐熟促進、土壌の改良、肥効の増進、残留農薬の無害化、病害微生物を抑制する資料を製造する方法 |
JPS60137492A (ja) * | 1983-12-23 | 1985-07-22 | Meidensha Electric Mfg Co Ltd | 排水処理装置 |
JPH0372879A (ja) * | 1989-08-09 | 1991-03-28 | Mitsubishi Rayon Co Ltd | 微生物固定化繊維の製造法 |
JPH05244962A (ja) * | 1992-03-09 | 1993-09-24 | Keijiro Nakamura | 生物活性化剤の製造方法 |
JPH05252842A (ja) * | 1992-03-10 | 1993-10-05 | Keijiro Nakamura | 新規キノコ |
JPH0671293A (ja) * | 1992-05-22 | 1994-03-15 | Ebara Infilco Co Ltd | 固形廃棄物と廃水の処理方法 |
JPH06239608A (ja) * | 1993-02-17 | 1994-08-30 | Takeda Chem Ind Ltd | 微生物菌体を固定した活性炭、その製法および用途 |
JPH0748193A (ja) * | 1993-04-28 | 1995-02-21 | Kazuo Takahashi | 廃棄物の新聞紙等を再利用した、有機質肥料の製造方法 |
JPH07274942A (ja) * | 1994-04-08 | 1995-10-24 | Mutenka Shokuhin Hanbai Kyodo Kumiai | 好気性微生物及び嫌気性微生物の複合大量培養法 |
JPH0824828A (ja) * | 1994-07-08 | 1996-01-30 | Hiromitsu Uchibori | 生ゴミ処理悪臭消化の脱臭剤 |
JPH08119780A (ja) * | 1994-10-13 | 1996-05-14 | Shuichi Kitamura | コンポスター |
JPH08196265A (ja) * | 1995-01-24 | 1996-08-06 | Yutaka Jisho:Kk | 有用微生物群元菌増殖法 |
JPH08209669A (ja) * | 1995-01-31 | 1996-08-13 | Ube Ind Ltd | 海底泥土層の改良方法 |
JPH08252086A (ja) * | 1995-03-16 | 1996-10-01 | Yuutoku:Kk | 多孔質物質に有用微生物群を増殖する方法 |
JPH08277002A (ja) * | 1995-04-10 | 1996-10-22 | Kazuo Kogo | ネット付きゴミ受け |
JPH08280378A (ja) * | 1995-04-14 | 1996-10-29 | Netsu Nachiyuraru Farm:Kk | Em効果が飛躍的に増大するem拡大培養液並びにem混入菌床並びにem拡大培養液の利用方法並びに肥料 |
JPH1046146A (ja) * | 1996-08-08 | 1998-02-17 | Marui Hosou:Kk | 土壌改良剤 |
JPH10155476A (ja) * | 1996-11-27 | 1998-06-16 | Konsaruteeshiyon Nagaoka:Kk | Em拡大培養液,em混入ゴム,em混入接着剤並びにem混入塗料 |
JPH10167921A (ja) * | 1996-12-05 | 1998-06-23 | Michio Iriguchi | 病害虫殺菌忌避剤の製造法 |
Family Cites Families (12)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US372879A (en) * | 1887-11-08 | Teeeitoky | ||
US671293A (en) * | 1900-07-11 | 1901-04-02 | William Quinby | Machine for setting lacing-studs. |
US748193A (en) * | 1903-04-22 | 1903-12-29 | John Peter Knuehmann | Paint-brush. |
US824828A (en) * | 1906-03-05 | 1906-07-03 | William L Silvey | Secondary-battery plate. |
US1046146A (en) * | 1907-03-18 | 1912-12-03 | Franz De Buigne | Step in the mode of making die-stamps or the like. |
US5244962A (en) * | 1989-12-01 | 1993-09-14 | Avery Dennison Corporation | Olefin polymer based pressure-sensitive adhesives |
US5252842A (en) * | 1991-07-26 | 1993-10-12 | Westinghouse Electric Corp. | Low-loss semiconductor device and backside etching method for manufacturing same |
US5586593A (en) * | 1995-06-30 | 1996-12-24 | Hunt Holdings, Inc. | Partitioning system |
JP3685429B2 (ja) * | 1996-08-06 | 2005-08-17 | シャープ株式会社 | ショットキー接合の解析方法、半導体ウェーハの評価方法、絶縁膜の評価方法、およびショットキー接合解析装置 |
US6137492A (en) * | 1997-04-03 | 2000-10-24 | Microsoft Corporation | Method and system for adaptive refinement of progressive meshes |
US6027672A (en) * | 1997-12-31 | 2000-02-22 | Lightpath Technologies, Inc. | Method of producing large polymer optical blanks with predictable axil refractive index profile |
EP1077252A1 (en) * | 1998-05-06 | 2001-02-21 | Keijiro Nakamura | Microbial culture liquors containing microorganisms differing in characteristics and living in symbiosis and metabolites thereof, carriers and adsorbents containing the active components of the culture liquors and utilization of the same |
-
1999
- 1999-05-06 EP EP99918307A patent/EP1077252A1/en not_active Withdrawn
- 1999-05-06 CN CN 99805857 patent/CN1300318A/zh active Pending
- 1999-05-06 US US09/673,655 patent/US6649397B1/en not_active Expired - Fee Related
- 1999-05-06 WO PCT/JP1999/002346 patent/WO1999057243A1/ja not_active Application Discontinuation
- 1999-05-06 AU AU36285/99A patent/AU771630B2/en not_active Ceased
- 1999-05-06 CA CA002331966A patent/CA2331966A1/en not_active Abandoned
-
2003
- 2003-06-24 US US10/601,668 patent/US20050101003A1/en not_active Abandoned
Patent Citations (20)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5586593A (en) * | 1978-12-25 | 1980-06-30 | Kubota Ltd | Treating method of waste water of garbage incinerating plant |
JPS6027672A (ja) * | 1983-07-25 | 1985-02-12 | 日本ライフ株式会社 | 微生物の培養物を利用して、堆肥の腐熟促進、土壌の改良、肥効の増進、残留農薬の無害化、病害微生物を抑制する資料を製造する方法 |
JPS60137492A (ja) * | 1983-12-23 | 1985-07-22 | Meidensha Electric Mfg Co Ltd | 排水処理装置 |
JPH0372879A (ja) * | 1989-08-09 | 1991-03-28 | Mitsubishi Rayon Co Ltd | 微生物固定化繊維の製造法 |
JPH05244962A (ja) * | 1992-03-09 | 1993-09-24 | Keijiro Nakamura | 生物活性化剤の製造方法 |
JPH05252842A (ja) * | 1992-03-10 | 1993-10-05 | Keijiro Nakamura | 新規キノコ |
JPH0671293A (ja) * | 1992-05-22 | 1994-03-15 | Ebara Infilco Co Ltd | 固形廃棄物と廃水の処理方法 |
JPH06239608A (ja) * | 1993-02-17 | 1994-08-30 | Takeda Chem Ind Ltd | 微生物菌体を固定した活性炭、その製法および用途 |
JPH0748193A (ja) * | 1993-04-28 | 1995-02-21 | Kazuo Takahashi | 廃棄物の新聞紙等を再利用した、有機質肥料の製造方法 |
JPH07274942A (ja) * | 1994-04-08 | 1995-10-24 | Mutenka Shokuhin Hanbai Kyodo Kumiai | 好気性微生物及び嫌気性微生物の複合大量培養法 |
JPH0824828A (ja) * | 1994-07-08 | 1996-01-30 | Hiromitsu Uchibori | 生ゴミ処理悪臭消化の脱臭剤 |
JPH08119780A (ja) * | 1994-10-13 | 1996-05-14 | Shuichi Kitamura | コンポスター |
JPH08196265A (ja) * | 1995-01-24 | 1996-08-06 | Yutaka Jisho:Kk | 有用微生物群元菌増殖法 |
JPH08209669A (ja) * | 1995-01-31 | 1996-08-13 | Ube Ind Ltd | 海底泥土層の改良方法 |
JPH08252086A (ja) * | 1995-03-16 | 1996-10-01 | Yuutoku:Kk | 多孔質物質に有用微生物群を増殖する方法 |
JPH08277002A (ja) * | 1995-04-10 | 1996-10-22 | Kazuo Kogo | ネット付きゴミ受け |
JPH08280378A (ja) * | 1995-04-14 | 1996-10-29 | Netsu Nachiyuraru Farm:Kk | Em効果が飛躍的に増大するem拡大培養液並びにem混入菌床並びにem拡大培養液の利用方法並びに肥料 |
JPH1046146A (ja) * | 1996-08-08 | 1998-02-17 | Marui Hosou:Kk | 土壌改良剤 |
JPH10155476A (ja) * | 1996-11-27 | 1998-06-16 | Konsaruteeshiyon Nagaoka:Kk | Em拡大培養液,em混入ゴム,em混入接着剤並びにem混入塗料 |
JPH10167921A (ja) * | 1996-12-05 | 1998-06-23 | Michio Iriguchi | 病害虫殺菌忌避剤の製造法 |
Cited By (15)
Publication number | Priority date | Publication date | Assignee | Title |
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WO2001005234A1 (en) * | 1999-07-14 | 2001-01-25 | Palmrow Pty Ltd | A nematicide composition |
WO2001005927A1 (fr) * | 1999-07-19 | 2001-01-25 | Keijiro Nakamura | Tensioactifs et detergents, et procede de lavage a base de milieu de culture complexe de microorganismes/enzymes |
JP2002212154A (ja) * | 2001-01-16 | 2002-07-31 | Dainippon Ink & Chem Inc | 2,5−ジアリールアミノテレフタル酸の製造方法 |
KR20030046535A (ko) * | 2001-11-13 | 2003-06-18 | (주)이씨테크 | 폐어망에 효율적인 생물막 형성을 위한 영양분 코팅 방법및 생물막 오수정화장치 |
WO2003101472A1 (en) * | 2002-05-31 | 2003-12-11 | Calpis Co., Ltd. | Dioxin elimination promoter |
US8877483B2 (en) | 2002-05-31 | 2014-11-04 | Calpis Co., Ltd. | Dioxin elimination promoter |
US7745202B2 (en) | 2004-02-20 | 2010-06-29 | Em Research Organization, Inc. | Detergent made use of fermentation technology and production method thereof |
CN1922300B (zh) * | 2004-02-20 | 2011-03-16 | 株式会社Em研究机构 | 应用发酵技术的净洗剂及其制造方法 |
WO2005080539A1 (ja) * | 2004-02-20 | 2005-09-01 | Em Research Organization, Inc. | 発酵技術を応用した洗浄剤及びその製造方法 |
CN101157860B (zh) * | 2007-02-14 | 2011-06-01 | 林文辉 | 一种土壤生物氧化剂的配方及其制作方法 |
CN102405770A (zh) * | 2011-09-19 | 2012-04-11 | 河南农业大学 | 一种利用大豆慢生根瘤菌促进平菇生长的方法 |
JP2015136677A (ja) * | 2014-01-24 | 2015-07-30 | 新日鐵住金株式会社 | 排水処理方法 |
WO2016098711A1 (ja) * | 2014-12-15 | 2016-06-23 | 大谷 洋 | 浄化システムおよびそれを用いた浄化方法、および、藻類増殖抑制方法、および水流発生装置、および浄化装置 |
CN104548175A (zh) * | 2014-12-31 | 2015-04-29 | 北京沃土天地生物科技有限公司 | 一种复合生物除臭剂及其制备方法与应用 |
CN104548175B (zh) * | 2014-12-31 | 2019-06-21 | 北京沃土天地生物科技有限公司 | 一种复合生物除臭剂及其制备方法与应用 |
Also Published As
Publication number | Publication date |
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CN1300318A (zh) | 2001-06-20 |
EP1077252A1 (en) | 2001-02-21 |
US6649397B1 (en) | 2003-11-18 |
US20050101003A1 (en) | 2005-05-12 |
AU771630B2 (en) | 2004-04-01 |
AU3628599A (en) | 1999-11-23 |
CA2331966A1 (en) | 1999-11-11 |
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