CN102527700A - Treatment process for treating microorganisms of kitchen garbage in situ and realization method of treatment process - Google Patents
Treatment process for treating microorganisms of kitchen garbage in situ and realization method of treatment process Download PDFInfo
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- CN102527700A CN102527700A CN2011100006659A CN201110000665A CN102527700A CN 102527700 A CN102527700 A CN 102527700A CN 2011100006659 A CN2011100006659 A CN 2011100006659A CN 201110000665 A CN201110000665 A CN 201110000665A CN 102527700 A CN102527700 A CN 102527700A
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- treatment process
- kitchen garbage
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- food waste
- changing food
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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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/78—Recycling of wood or furniture waste
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Abstract
The invention provides a treatment process for treating microorganisms of kitchen garbage in situ and a realization method of the treatment process. The treatment process is finished through the following three stages: 1, a pre-treatment stage, 2, a treatment stage, and 3, a post-treatment stage. An enzymic preparation is added into a barrel, 1kg of kitchen garbage is added into the barrel, and the pre-treatment process is finished within 48 hours at the environment temperature of over 10 DEG C, wherein the ending sign is that some penetrated liquid and colorless hyphae appear. Not more than 1kg of kitchen garbage is added into the barrel everyday and is properly stirred with a stirring tool to provide the microorganisms with the power for breeding and metabolism, and then the decomposition efficiency during the treatment stage of the kitchen garbage can be up to 60 percent. The residues in the metabolic residues in the treatment barrel are stable; after being collected, the residues are subjected to a draining process and a re-fermentation process to extract effective components from the residues, and the effective components are reused as a resource. Through the treatment process, the conveying processes of the kitchen garbage are reduced, the pollution processes are reduced, no waste water is discharged, and a zero-waste kitchen garbage source treating process is realized.
Description
Technical field
The present invention relates to utilize the technical field of microbial technique processing utensil rubbishes, specifically a kind of in-situ treatment changing food waste micro-organism treatment process and its implementation in the source.
Background technology
Changing food waste is meant in the daily life organic waste in producing kitchen leftover bits and pieces, dining table discarded object, result from produce in the activities of serving the meals such as resident family, catering service, aircraft, train, steamer, oil drilling platform also a fresh organic waste that does not foul and rot.
Changing food waste contains a large amount of moisture and accounts for 70%; Mainly contain cellulose and protein and fat (cellulose 60%, protein contain 30% approximately, fat contain 10% approximately) in addition in the part; Certificate is the authoritative department statistics in the world; The ratio that meal kitchen organic waste accounts for house refuse is major pollution source in the house refuse up to 70%.
Through discovering; Cellulose comprises is according to a large amount of ratios in the changing food waste, and the volume of changing food waste is being supported in and all kinds of cellulosic existence in the food; Find that at first all kinds of meal kitchen organic waste all is that skeleton constitutes with the cellulose; Such as celluloses such as animal origin, string, grass fiber, wood-fibred, in case cellulosic chain is interrupted, meal kitchen organic waste just can be realized decrement.Utilize the plain ability of microorganism cut staple just can realize utilizing microorganism to decompose the method with decrement in the source of generation changing food waste,
Extensive use is occasions such as resident family, catering service, aircraft, train, steamer, oil drilling platform.
Summary of the invention
The object of the invention relates to a kind of in-situ treatment changing food waste micro-organism treatment process and its implementation.
The present invention addresses the above problem and main accomplishes through following three phases: 1, pretreatment stage, 2, the processing stage, 3, three phases completion such as post processing processing.
The present invention is achieved in that
(1) pretreatment stage: enzyme preparation is put in the bucket, thrown in 1 kilogram changing food waste, more than 10 ℃, accomplish pretreating process after 48 hours in environment temperature, the sign of completion is that some permeation liquids are arranged, and begins to have colourless mycelia to occur.
(2) processing stage: drop into changing food waste amount at 0.5 to 1 kilogram to every barrel every day; If the changing food waste of throwing in is too much; It is not very abundant perhaps decomposing, and use the stirring tool agitation as appropriate, let below the bucket microbial inoculum cover upward changing food waste; Simultaneously, also play and let the purpose of the abundant ingress of air of following changing food waste.The power of microbial reproduction metabolism is provided, and the protein in the changing food waste exists with polypeptide form.The processing stage decomposition efficiency can reach 60%.
(3) the post processing process segment: will fill with the metabolism residue centralized collection of handling bucket and handle; Residue is stable; Handle the liquid that decomposition obtains comprising major part by changing food waste; And the changing food waste that does not decompose fully, extract wherein active ingredient through draining, fermentation, drying and standardization technology after the centralized collection, respectively as the utilization of resources.
Whole machining process technology of the present invention.Utilize solid fermentation process to reduce pollution section.No waste water, the useless strong acid of nothing, useless highly basic discharging.The mud that the waste water circulation obtains is as the raw material of producing organic fertilizer.Processing technology for " zero rubbish " discharging, " zero pollutes ", trace element " zero destroys ".
Description of drawings:
Accompanying drawing 1: culture process figure in the microbial bacteria
Accompanying drawing 2: changing food waste micro-organism treatment process
The practical implementation method
Below in conjunction with specific embodiment the present invention is made more detailed description:
The fermented bacterium source
Bacterial strain such as bacillus subtilis, actinomyces is purchased in Chinese industrial microorganism fungus kind preservation center in the present embodiment, and Microbiological Lab of Chinese Academy of Sciences result of laboratory test is shown as non-pathogenic, and Escherichia coli and salmonella are had inhibitory action.Colony counts surpasses 280,000,000IU/g.Bacillus subtilis.Thermally-stabilised good with genetic stability.
4.2 the cultivation of induction mutation of bacterium and enzyme
Gather changing food waste, carry out the bacterial classification cultivation and decompose the enzyme screening.Utilize inclined-plane inoculation and laboratory advanced growth of digital tesseract technical Analysis and fermentation diagram, theoretical foundation accurately is provided for inoculating proportion and inoculation.At first bacterial strain is processed bacteria suspension, use the 15W uviol lamp, to 30cm irradiation 30 seconds, irradiation while stirring guaranteed that thalline evenly absorbs ultraviolet light wave apart from 25cm.
Utilize nutrient agar as culture medium,
Peptone 5%～10%, beef extract 35%, NaCl 8% agar 20%, distilled water; PH does not need the high-temperature sterilization sterilization 5～7.5 early stages, and the thermophilic bacteria virus killing by sweat produces inserts bacterial strain in the seed culture fluid; After 8h～24h is cultivated in 20 ℃～25 ℃ constant temperature shaking table concussions, in seed liquor precursor reactant groove, at 30 ℃～45 ℃; Cultivate 10h～16h, after the drying, obtain product.
Concrete production procedure: 1, inclined-plane inoculation 2, bacterial classification amplify 3, material handles 4, fermentation 5, dry 6, sieve 7, standardization 8, finished product packing
Through 40 ℃ of oven dry 24h, make the powder microorganism and be used for changing food waste processing pulvis at last, normal temperature is met wet condition more than 10 ℃, and micro organism powder can growth and breeding and ability decomposing organic matter.
Changing food waste micro-organism treatment process overall process is to begin from the changing food waste preliminary treatment, and enzyme preparation is put in the bucket, throws in 1 kilogram changing food waste; In environment temperature more than 10 ℃; Accomplished pretreating process in 48 hours, the sign of completion is that some permeation liquids are arranged, and begins to have colourless mycelia to occur.
The processing stage: drop into changing food waste to handling bucket every day; Every barrel is dropped into the changing food waste amount at 0.5 to 1 kilogram, if the changing food waste of throwing in is too much, it is not very abundant perhaps decomposing; Use the stirring tool agitation as appropriate; Let below the bucket microbial inoculum cover to go up changing food waste, simultaneously, also play letting the purpose of the abundant ingress of air of following changing food waste.The power of microbial reproduction metabolism is provided, and the protein in the changing food waste exists with polypeptide form.The processing stage decomposition efficiency can reach 60%.
The post processing process segment: will fill with the metabolism residue centralized collection of handling bucket and handle; Residue is stable; Handle the liquid that decomposition obtains comprising major part by changing food waste; And the changing food waste that does not decompose fully, after the centralized collection through draining, zymotechnique extracts wherein active ingredient again, respectively as the utilization of resources.Whole machining process technology has reduced the changing food waste transit link, the processing stage 60% changing food waste be broken down into the protein permeation liquid that polypeptide form exists, and be stable, transportation is analyte again, has reduced pollution section through technology.Non-wastewater discharge has solved the problem that transportation rubbish equals to transport waste water, realizes " zero is discarded " changing food waste source processing technology.
Microorganism in the source processing utensil rubbishes fermentation reaction gentle, the product trace element is basic not to be destroyed, and does not pollute, energy consumption is low; Utilize the static fermentation technology to produce decomposition of protein, production cost reduces greatly, makes its popularization become possibility; Fill up domestic blank, realized technological break-through.
Claims (1)
1. an in-situ treatment changing food waste micro-organism treatment process and its implementation, its characteristic:
1、
The invention provides and a kind ofly utilize microorganism to decompose the method with decrement in the source that produces changing food waste; Find that at first all kinds of meal kitchen organic waste all is that skeleton constitutes with the cellulose; Like celluloses such as animal origin, string, grass fiber, wood-fibreds; In case cellulosic chain is interrupted, meal kitchen organic waste just can be realized decrement.
2、
Changing food waste is handled in the source of its generation,,, just can be realized innoxious decomposition as long as environment temperature surpasses more than 10 ℃ without any need for additionaling power.
3、
Saved the rubbish transit link, transportation no longer be rubbish, but the organic matter after the stable treated, quite stable.Contaminated environment no longer.
4、
Do not need high-temperature sterilization in the microorganism decomposition technique, but in the fermentation reaction process, pass through the growth that microorganism suppresses the key bacterium.Concrete production procedure: 1, pretreatment stage 2, the processing stage 3, subsequent treatment process segment, 4, standardization 8, finished product packing.
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Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN108971198A (en) * | 2018-07-13 | 2018-12-11 | 广州市朗云环保投资有限公司 | A kind of Food waste treatment method promoting processing system production capacity and hydrolytic decomposition pot |
Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1485152A (en) * | 2002-09-25 | 2004-03-31 | 丹东中泰工贸有限公司 | Micro-biological degradation process method for the domestic garbage |
| CN1548404A (en) * | 2003-05-13 | 2004-11-24 | 上海汇仁复合有机肥料有限公司 | Production process of microbial organic composite fertilizer |
| CN101085999A (en) * | 2007-06-21 | 2007-12-12 | 北京科技大学 | Method for kitchen garbage lactic acid fermentation facilitated by mushroom bran |
| CN101200387A (en) * | 2006-12-13 | 2008-06-18 | 四川艾蒙爱生物科技有限公司 | Preparation of microorganium fertilizer by using bacilluslaterosporus and bacillus subtilis |
| CN101358171A (en) * | 2008-09-26 | 2009-02-04 | 北京嘉博文生物科技有限公司 | Complex bacteria for preprocessing of restaurant garbage, preparation method and application thereof |
| CN101948756A (en) * | 2010-09-16 | 2011-01-19 | 江门市汉宇电器有限公司 | High-efficient restaurant-kitchen waste degrading microorganism bacterial agent and preparation method and application thereof |
| CN102174401A (en) * | 2011-01-30 | 2011-09-07 | 宁波大学 | Microorganism composite zymocyte agent as well as preparation method and application thereof |
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- 2011-01-04 CN CN2011100006659A patent/CN102527700A/en active Pending
Patent Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1485152A (en) * | 2002-09-25 | 2004-03-31 | 丹东中泰工贸有限公司 | Micro-biological degradation process method for the domestic garbage |
| CN1548404A (en) * | 2003-05-13 | 2004-11-24 | 上海汇仁复合有机肥料有限公司 | Production process of microbial organic composite fertilizer |
| CN101200387A (en) * | 2006-12-13 | 2008-06-18 | 四川艾蒙爱生物科技有限公司 | Preparation of microorganium fertilizer by using bacilluslaterosporus and bacillus subtilis |
| CN101085999A (en) * | 2007-06-21 | 2007-12-12 | 北京科技大学 | Method for kitchen garbage lactic acid fermentation facilitated by mushroom bran |
| CN101358171A (en) * | 2008-09-26 | 2009-02-04 | 北京嘉博文生物科技有限公司 | Complex bacteria for preprocessing of restaurant garbage, preparation method and application thereof |
| CN101948756A (en) * | 2010-09-16 | 2011-01-19 | 江门市汉宇电器有限公司 | High-efficient restaurant-kitchen waste degrading microorganism bacterial agent and preparation method and application thereof |
| CN102174401A (en) * | 2011-01-30 | 2011-09-07 | 宁波大学 | Microorganism composite zymocyte agent as well as preparation method and application thereof |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN108971198A (en) * | 2018-07-13 | 2018-12-11 | 广州市朗云环保投资有限公司 | A kind of Food waste treatment method promoting processing system production capacity and hydrolytic decomposition pot |
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Application publication date: 20120704 |