CN105859339A - Flora for recycling treatment of organic wastes and application of flora - Google Patents
Flora for recycling treatment of organic wastes and application of flora Download PDFInfo
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- CN105859339A CN105859339A CN201610192517.4A CN201610192517A CN105859339A CN 105859339 A CN105859339 A CN 105859339A CN 201610192517 A CN201610192517 A CN 201610192517A CN 105859339 A CN105859339 A CN 105859339A
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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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- 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
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- 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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- 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
- C12N1/16—Yeasts; Culture media therefor
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- 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
- C12N1/20—Bacteria; Culture media therefor
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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
- Y02P60/80—Food processing, e.g. use of renewable energies or variable speed drives in handling, conveying or stacking
- Y02P60/87—Re-use of by-products of food processing for fodder production
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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
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Abstract
The invention is suitable for the technical field of recycling organic wastes, and discloses a flora for recycling treatment of organic wastes. The flora for recycling treatment of organic wastes is efficiently compounded from a variety of bacteria such as bacillus subtilis, aspergillus niger, saccharomycete and soil flora, wherein the soil flora is extracted from the natural world and comprises three or more of bacillus megatherium, bacillus mucilaginosus, bacillus licheniformis, bacillus thuringiensis, bacillus laterosporus, bacillus mucilaginosus, streptomyces jingyangensis, mycorrhiza fungi, azotobacter vinelandii, photosynthetic bacteria, bacillus coagulans, aspergillus oryzae, and paecilomyces lilacinus. According to the flora for recycling treatment of organic wastes, disclosed by the invention, by virtue of mutual promotion, mutual coordination and combined action of a variety of beneficial microorganisms, the organic wastes are recycled, environmental pollution is reduced, and wastes are changed into valuables; and the flora for recycling treatment of organic wastes can be used for producing industrial fermentation products and improving the health and growth conditions of animals, and can also improve the current situation of serious soil hardening at present and improve soil quality, thereby promoting the rapid development of agricultural economics.
Description
[technical field]
The present invention relates to the technical field that reclaiming organic waste utilizes, process flora and application thereof particularly to a kind of reclaiming organic waste utilization.
[background technology]
Organic waste includes urban kitchen waste, household kitchen wastes, ight soil, rural culture discarded object, die of illness domestic animal, stalk, vegetable and fruit Meat processing clout, river silt, pond sludge etc., and changing food waste is particularly acute, it it is the sanitary waste that formed during personal consumption of resident, easily rot, distribute stench, spread germs and virus, surprising plus China's dining table waste, produce the changing food waste of flood tide every day, these changing food wastes may contain multiple germ, unprocessed culturing directly livestock and poultry, can be by livestock and poultry vivotoxin, health is brought harm by the accumulation of harmful substance, thus cause the cross infection between people and animals, the danger of the hugest pathogen transfer of this food chain form and diffusion, food-safety problem and social concern are become.Many countries such as the U.S., Canada, European Union have formulated the undressed changing food waste of a lot of law bans and have directly fed pigs, and China has also given strict control to this.Although changing food waste yield is huge, impact is extensively, but classify, collect, transport, the link such as process lacks effective supervision and oversight of government, also lack actively participating in of excellent enterprise, thus the present situation that resource utilization efficiency is low and market is unordered forming changing food waste.Furthermore, China is large agricultural country, populous nation, the substantial amounts of organic waste of annual generation, as processed not in time, can cause serious environmental pollution.
At present, the general modfel of the recycling of organic waste being included landfill disposal method, Traditional compost facture, burning disposal method, pyrolysismethod, protein feed method etc., cost is high and effect is low, and economy is poor.Generally containing large quantity of moisture in organic waste, burning disposal method is used not only to cause CO2, the air pollution such as two English, also result in energy substance waste；Using landfill disposal method to produce a large amount of percolates, polluted underground water, occupy cultivated land area；Owing to Traditional compost facture cycle length needs about 40 days, added value of product is low；And use kitchen fodder cannot solve protein homology sex chromosome mosaicism.Furthermore, it is heavy that China's industrial fermentation goods consume grain, grain yield and demand compare and allow of no optimist, international market grain is nervous, grain price goes up, adding China is protein and the country of edible oil shortage, externally importation dependence is up to more than 50%, therefore make full use of kitchen castoff do industry fermented product replace grain be necessary, but utilize fermentable to process kitchen castoff, rubbish from cooking, reaction is slow, time is long, cost is big and effect is low, for alleviating current soil compaction phenomenon, improve reclaiming organic waste to utilize, especially kitchen castoff, it is necessary that proposing a kind of reclaiming organic waste utilization processes flora and application thereof.
[summary of the invention]
It is an object of the invention to overcome above-mentioned the deficiencies in the prior art, a kind of reclaiming organic waste utilization is provided to process flora and application thereof, it aims to solve the problem that in prior art, reclaiming organic waste utilization rate is low, it is long that fermentable processes the time, converts not thorough and that the big effect of cost is low technical problem.
For achieving the above object, the present invention proposes a kind of reclaiming organic waste utilization and processes flora, by bacillus subtilis, aspergillus niger, saccharomycete and soil flora multiple bacterium high efficiency composition form, described soil flora extracts from nature, described soil flora includes bacillus megaterium, bacillusmusilaginosiengineering, bacillus licheniformis, bacillus thuringiensis, bacillus laterosporus, colloid bacillus cereus, Streptomyces jingyangensis, mycorrhizal fungi, azotobacter vinelandii, photosynthetic bacteria group, bacillus coagulans, aspergillus oryzae, in Paecilomyces lilacinus three kinds and more than three kinds.
As preferably, described a kind of reclaiming organic waste utilization processes flora, is calculated in mass percent, and is by 30% bacillus subtilis, 25% aspergillus niger, 25% saccharomycete and the soil flora composition of 20%.
As preferably, described a kind of reclaiming organic waste utilization processes flora and also includes at least one in bifidocaterium, lactic acid bacteria, acetic acid bacteria.
As preferably, described a kind of reclaiming organic waste utilization processes flora, is calculated in mass percent, and is by 25% bacillus subtilis, 20% aspergillus niger, 20% saccharomycete, 8% bifidocaterium, 9% lactic acid bacteria, 8% acetic acid bacteria and the soil flora composition of 10%.
As preferably, described a kind of reclaiming organic waste utilization processes flora, also includes thermophilic actinomycete and nitrobacteria.
As preferably, described thermophilic actinomycete and nitrobacteria account for a kind of reclaiming organic waste utilization and process the 5% of flora gross mass.
A kind of reclaiming organic waste utilization processes the application of flora, by a kind of reclaiming organic waste utilization process flora: brown sugar: the mass ratio of sterilized water=1:10:100 weighs and mixes, being placed in lucifuge in sealing incubator to cultivate 1～3 day, temperature is 25～35 DEG C, obtains liquid spawn；Again by liquid spawn: brown sugar: urea: salt: the mass ratio of sterilized water=50:100:1:1:1000 weighs and mixes, it is placed in lucifuge in sealing container to ferment 3～7 days, temperature is 25～35 DEG C, obtain flora stoste, described flora stoste is for the microbial degradation of organic waste, described organic waste is first pulverized after automatic sorting, then refrigerated separation after boiling, and undecomposed organic waste recycling flora stoste carries out microorganism and fully degrades.
As preferably, in the preparation process of described liquid spawn and flora stoste, sterilized water is first heated to 100 DEG C, continues heating 5～8min removal miscellaneous bacteria after adding brown sugar, after being cooled to 35 DEG C, add a kind of reclaiming organic waste utilization and process flora or liquid spawn.
As preferably, described organic waste includes kitchen castoff, household kitchen wastes, ight soil, rural culture discarded object, the domestic animal that dies of illness, stalk, vegetable and fruit Meat processing clout.
nullBeneficial effects of the present invention: compared with prior art，A kind of reclaiming organic waste utilization that the present invention provides processes flora and application thereof，By bacillus subtilis、Aspergillus niger、Saccharomycete and soil flora multiple bacterium high efficiency composition form，By mutually promoting of multiple beneficial microorganism、It is complementary to one another、The most collaborative，Common effect is fully degraded organic waste，And can be in process of production，Reduce Ammonia valatilization，Improve environment，Prevent the generation of harmful levels of pathogens，And after the fermented degraded of organic waste，Industrialized production can prepare industrial fermentation goods，There is higher nutritive value，Due to containing multiple beneficial bacterium，Pig and other microbial population of animal intestinal tract balance can be regulated，Produce multiple digestive ferment and growth factor，Plus these microorganisms inherently rich in protein、Amino acid and the source of trace element，It is thus possible to be substantially improved health and the upgrowth situation of animal，Improve food conversion ratio and promote growth，Can be widely used for aquaculture、Animal husbandry，Also can improve the present situation that current soil compaction is serious，Improve soil property，Not only reclaiming organic waste is utilized，Prevent from polluting，Socioeconomic development can also be promoted.
[detailed description of the invention]
For making the object, technical solutions and advantages of the present invention of greater clarity, below by embodiment, the present invention is further elaborated.However, it should be understood that specific embodiment described herein is only in order to explain the present invention, it is not limited to the scope of the present invention.Additionally, in the following description, the description to known features and technology is eliminated, to avoid unnecessarily obscuring idea of the invention.
The embodiment of the present invention provides a kind of reclaiming organic waste utilization to process flora, formed by bacillus subtilis, aspergillus niger, saccharomycete and soil flora multiple bacterium high efficiency composition, described soil flora extracts from nature, and described soil flora includes three kinds in bacillus megaterium, bacillusmusilaginosiengineering, bacillus licheniformis, bacillus thuringiensis, bacillus laterosporus, colloid bacillus cereus, Streptomyces jingyangensis, mycorrhizal fungi, azotobacter vinelandii, photosynthetic bacteria group, bacillus coagulans, aspergillus oryzae, Paecilomyces lilacinus and more than three kinds.
Further, described a kind of reclaiming organic waste utilization processes flora, is calculated in mass percent, and is by 30% bacillus subtilis, 25% aspergillus niger, 25% saccharomycete and the soil flora composition of 20%.
Further, described a kind of reclaiming organic waste utilization processes flora and also includes at least one in bifidocaterium, lactic acid bacteria, acetic acid bacteria, described a kind of reclaiming organic waste utilization processes flora, it is calculated in mass percent, is by 25% bacillus subtilis, 20% aspergillus niger, 20% saccharomycete, 8% bifidocaterium, 9% lactic acid bacteria, 8% acetic acid bacteria and the soil flora composition of 10%.
Further, described a kind of reclaiming organic waste utilization processes flora, also includes that thermophilic actinomycete and nitrobacteria, described thermophilic actinomycete and nitrobacteria account for a kind of reclaiming organic waste utilization and process the 5% of flora gross mass.Utilizing the resistant to elevated temperatures performance of thermophilic actinomycete can fully degrade organic waste, nitrobacteria can reduce Ammonia valatilization, improve environment, prevent the generation of harmful levels of pathogens in process of production.
The embodiment of the present invention also provides for a kind of reclaiming organic waste utilization and processes the application of flora, by a kind of reclaiming organic waste utilization process flora: brown sugar: the mass ratio of sterilized water=1:10:100 weighs and mixes, it is placed in lucifuge in sealing incubator to cultivate 1～3 day, temperature is 25～35 DEG C, obtains liquid spawn；Again by liquid spawn: brown sugar: urea: salt: the mass ratio of sterilized water=50:100:1:1:1000 weighs and mixes, it is placed in lucifuge in sealing container to ferment 3～7 days, temperature is 25～35 DEG C, obtain flora stoste, described flora stoste is for the microbial degradation of organic waste, described organic waste is first pulverized after automatic sorting, then refrigerated separation after boiling, and undecomposed organic waste recycling flora stoste carries out microorganism and fully degrades.
Wherein, in the preparation process of described liquid spawn and flora stoste, sterilized water is first heated to 100 DEG C, heating 5～8min removal miscellaneous bacteria is continued after adding brown sugar, after being cooled to 35 DEG C, adding a kind of reclaiming organic waste utilization and process flora or liquid spawn, described organic waste includes kitchen castoff, household kitchen wastes, ight soil, rural culture discarded object, the domestic animal that dies of illness, stalk, vegetable and fruit Meat processing clout.
nullOne reclaiming organic waste utilization of the present invention processes flora，Mutually promoting of multiple probio、It is complementary to one another、The most collaborative，Fully degraded kitchen castoff by the common effect of multiple probio、Household kitchen wastes、Ight soil、Rural culture discarded object、Die of illness domestic animal、Stalk、The organic wastes such as vegetable and fruit Meat processing clout，Not only improve the problem that organic waste pollutes environment，Can also turn waste into wealth simultaneously，Organic waste is resolved into glucose、Galacturonic acid、Glycerine、The multiple nutrients materials such as higher fatty acids，Pass through industrialized production，Prepare industrial fermentation goods，There is higher nutritive value，Due to containing multiple beneficial bacterium，Pig and other microbial population of animal intestinal tract balance can be regulated，Produce multiple digestive ferment and growth factor，Plus these microorganisms inherently rich in protein、Amino acid and the source of trace element，It is thus possible to be substantially improved health and the upgrowth situation of animal，Improve food conversion ratio and promote growth，Can be widely used for aquaculture、Animal husbandry；And the organic waste after microbial degradation is used for cultivating insect, insect source biological feed can be produced, rich in insect protein, amino acid and trace element, non-harmful insect protein and microprotein are as the source of protein, with the antibiotic of insect and microorganism as the function adjuster of animal, and seldom with antibiotic and other drug, the delicious meat produced, with low cost, simultaneously, with insect albumen powder as the substitute of fish meal, the breach of the great demand of protein resource can be alleviated, also can add the insects such as earthworm, improve the present situation that current soil compaction is serious, improve soil property, not only reclaiming organic waste is utilized, added value of product is high, can also prevent from polluting, promote socioeconomic development.
The foregoing is only presently preferred embodiments of the present invention, not in order to limit the present invention, all any amendment, equivalent or improvement etc. made within the spirit and principles in the present invention, should be included within the scope of the present invention.
Claims (9)
1. a reclaiming organic waste utilization processes flora, it is characterised in that: by bacillus subtilis, black song
Mould, saccharomycete and soil flora multiple bacterium high efficiency composition form, and described soil flora extracts from nature,
Described soil flora includes bacillus megaterium, bacillusmusilaginosiengineering, bacillus licheniformis, Su Yun
Gold bacillus, bacillus laterosporus, colloid bacillus cereus, Streptomyces jingyangensis, mycorrhizal fungi, brown
In nitrogen-fixing bacteria, photosynthetic bacteria group, bacillus coagulans, aspergillus oryzae, Paecilomyces lilacinus three kinds and three kinds with
On.
2. a kind of reclaiming organic waste utilization as claimed in claim 1 processes flora, it is characterised in that: institute
A kind of reclaiming organic waste utilization stated processes flora, is calculated in mass percent, is by 30% withered grass
Bacillus, 25% aspergillus niger, 25% saccharomycete and the soil flora composition of 20%.
3. a kind of reclaiming organic waste utilization as claimed in claim 1 processes flora, it is characterised in that: institute
A kind of reclaiming organic waste utilization stated processes flora and also includes in bifidocaterium, lactic acid bacteria, acetic acid bacteria
At least one.
4. a kind of reclaiming organic waste utilization as claimed in claim 3 processes flora, it is characterised in that: institute
A kind of reclaiming organic waste utilization stated processes flora, is calculated in mass percent, is by 25% withered grass
Bacillus, 20% aspergillus niger, 20% saccharomycete, 8% bifidocaterium, 9% lactic acid bacteria, 8% acetic acid bacteria and
The soil flora of 10% is constituted.
5. a kind of reclaiming organic waste utilization as claimed in claim 1 processes flora, it is characterised in that: institute
A kind of reclaiming organic waste utilization stated processes flora, also includes thermophilic actinomycete and nitrobacteria.
6. a kind of reclaiming organic waste utilization as claimed in claim 5 processes flora, it is characterised in that: institute
The thermophilic actinomycete stated and nitrobacteria account for a kind of reclaiming organic waste utilization and process flora gross mass
5%.
7. the application of a reclaiming organic waste utilization process flora, it is characterised in that: by a kind of organic waste
Thing recycling process flora: brown sugar: the mass ratio of sterilized water=1:10:100 weighs and mixes,
Being placed in lucifuge in sealing incubator to cultivate 1～3 day, temperature is 25～35 DEG C, obtains liquid spawn；Again
By liquid spawn: brown sugar: urea: salt: the mass ratio of sterilized water=50:100:1:1:1000
Weighing and mix, being placed in lucifuge in sealing container and ferment 3～7 days, temperature is 25～35 DEG C, obtains bacterium
Group's stoste, described flora stoste is for the microbial degradation of organic waste, described organic waste
First pulverize after automatic sorting, then refrigerated separation after boiling, undecomposed organic waste recycling flora
Stoste carries out microorganism and fully degrades.
A kind of reclaiming organic waste utilization the most as claimed in claim 7 processes the application of flora, and its feature exists
In: in the preparation process of described liquid spawn and flora stoste, sterilized water is first heated to 100 DEG C, adds
Continue heating 5～8min removal miscellaneous bacteria after entering brown sugar, after being cooled to 35 DEG C, add a kind of organic waste
Thing recycling processes flora or liquid spawn.
A kind of reclaiming organic waste utilization the most as claimed in claim 7 processes the application of flora, and its feature exists
In: described organic waste includes giving up in kitchen castoff, household kitchen wastes, ight soil, rural culture
Gurry, the domestic animal that dies of illness, stalk, vegetable and fruit Meat processing clout.
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| CN106467419A (en) * | 2016-09-08 | 2017-03-01 | 江南大学 | A kind of preparation method of biological organic fertilizer |
| CN106550761A (en) * | 2016-11-26 | 2017-04-05 | 山西省农业科学院作物科学研究所 | A kind of implantation methods of organic millet |
| CN107699522A (en) * | 2017-10-27 | 2018-02-16 | 银川保绿特生物技术有限公司 | A kind of composite bacteria for biofermentation kitchen leftover and preparation method thereof |
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| CN108753651A (en) * | 2018-06-13 | 2018-11-06 | 东北农业大学 | A kind of Saline-alkali ponds chicken manure fermenting compound bacteria and its application process |
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| CN111285714A (en) * | 2020-04-13 | 2020-06-16 | 山东本源生态农业科技有限公司 | Organic fertilizer fermenting agent suitable for low-temperature environment |
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| CN112159783A (en) * | 2020-10-28 | 2021-01-01 | 深圳市家家分类环保技术开发有限公司 | Acid-resistant salt-resistant microbial agent for degrading kitchen garbage and preparation method thereof |
| CN113278539A (en) * | 2021-03-18 | 2021-08-20 | 惠州市通用机电设备有限公司 | Microbial inoculum for treating organic garbage and preparation and use methods thereof |
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| CN114368999A (en) * | 2021-12-10 | 2022-04-19 | 北京嘉博文生物科技有限公司 | Soil conditioner for loosening soil and activating soil and preparation method thereof |
| CN114853514A (en) * | 2022-06-06 | 2022-08-05 | 惟农农业科技(江苏)有限公司 | Production process of environment-friendly bio-organic fertilizer with high fermentation efficiency |
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Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1348940A (en) * | 2001-12-11 | 2002-05-15 | 北京六合新星生物技术有限公司 | Comprehensive biotechnological process of producing organic fertilizer with organic waste |
| CN1624100A (en) * | 2004-10-29 | 2005-06-08 | 南京师范大学 | Microbial fermenting agent |
| CN1850965A (en) * | 2006-05-31 | 2006-10-25 | 北京嘉博文生物科技有限公司 | Method for resource circulating treatment of dining-kitchen organic waste using compound bacteria |
| CN102173884A (en) * | 2011-02-28 | 2011-09-07 | 湖北省农业科学院经济作物研究所 | High-mountain vegetable waste microbiological treatment method |
| CN104892281A (en) * | 2015-06-25 | 2015-09-09 | 金烜伊 | Production technology of organic orange dreg fertilizer |
| CN105087398A (en) * | 2015-09-09 | 2015-11-25 | 浙江师范大学 | Mixed inoculant agent for effective degradation of mushroom bran, and preparation method and application thereof |
| CN105420158A (en) * | 2015-12-21 | 2016-03-23 | 镇江兴农有机肥有限公司 | Special fermentation microbial inoculum for harmless treatment of solid organic waste |
-
2016
- 2016-03-30 CN CN201610192517.4A patent/CN105859339A/en active Pending
Patent Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1348940A (en) * | 2001-12-11 | 2002-05-15 | 北京六合新星生物技术有限公司 | Comprehensive biotechnological process of producing organic fertilizer with organic waste |
| CN1624100A (en) * | 2004-10-29 | 2005-06-08 | 南京师范大学 | Microbial fermenting agent |
| CN1850965A (en) * | 2006-05-31 | 2006-10-25 | 北京嘉博文生物科技有限公司 | Method for resource circulating treatment of dining-kitchen organic waste using compound bacteria |
| CN102173884A (en) * | 2011-02-28 | 2011-09-07 | 湖北省农业科学院经济作物研究所 | High-mountain vegetable waste microbiological treatment method |
| CN104892281A (en) * | 2015-06-25 | 2015-09-09 | 金烜伊 | Production technology of organic orange dreg fertilizer |
| CN105087398A (en) * | 2015-09-09 | 2015-11-25 | 浙江师范大学 | Mixed inoculant agent for effective degradation of mushroom bran, and preparation method and application thereof |
| CN105420158A (en) * | 2015-12-21 | 2016-03-23 | 镇江兴农有机肥有限公司 | Special fermentation microbial inoculum for harmless treatment of solid organic waste |
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