CN102747011A - Mixing strain for treating kitchen waste, and method - Google Patents
Mixing strain for treating kitchen waste, and method Download PDFInfo
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- CN102747011A CN102747011A CN2012101450834A CN201210145083A CN102747011A CN 102747011 A CN102747011 A CN 102747011A CN 2012101450834 A CN2012101450834 A CN 2012101450834A CN 201210145083 A CN201210145083 A CN 201210145083A CN 102747011 A CN102747011 A CN 102747011A
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Abstract
The present invention provides a mixing strain for treating kitchen waste, and a method for carrying out a kitchen waste treatment by using the mixing strain. The mixing strain comprises Bacillus amyloliquefaciens, Bacillus licheniformis, Bacillus cereus, Bacillus megaterium, and Bacillus subtilis. According to the present invention, the strains are mixed with kitchen waste, a water spraying effect is adopted, fermentation decomposition is performed within a water content range of 50-95%, fermentation products are discharged in the form of aqueous solutions, and no solid residue is remained.
Description
Technical field
The present invention relates to a kind of method and mikrobe associate strain that utilizes biological degradation to handle rubbish from cooking; Relate in particular to a kind of method of handling the associate strain of rubbish from cooking and using said associate strain processing rubbish from cooking; Said bacterial classification and method are handled after the rubbish from cooking, not the residual solids residue.
Background technology
Catering trades such as rubbish from cooking (hogwash) general reference restaurant, hotel, and the food blanking and the food residues in canteens such as enterprises and institutions, universities and colleges.Along with the urban economy rapid growth, the rapid expansion of city size, rubbish from cooking grows with each passing day.The generation of China's rubbish from cooking every day surpasses 20Kt, it is reported ton surplus only the generating capacity of Shanghai City hogwash every day just reaches 1300.Because rubbish from cooking is fermented easily, rotten, rot, not only produce a large amount of toxin, distribute foul gas, go back polluted-water and atmosphere, have a strong impact on environmental health, to people's health formation potential threat.Thereby the severe pendulum of hogwash refuse treatment problem is in face of the people.
The traditional rubbish from cooking processing mode of China is directly to deliver to plant to feed live pig, and this kind processing mode exists multiple potential harm to environment, very easily causes transmission of disease.Bird flu in recent years, communicable diseases such as foot and mouth disease are popular on a large scale, and the cross infection between people and animals is to human beings'health, and society stable constituted great threat.At present, Shanghai, cities such as Suzhou have formulated relevant policies in succession, prohibite with hogwash and feed live pig.
The method of this type of countries in the world processing at present rubbish has usually: 1) landfill method: through refuse collection, be shipped to landfill yard and pave compacting.Its advantage is simple and easy to do.Shortcoming is polluted, and is taken a large amount of soils for causing underground water, air, surrounding environment.2) burning method: solid waste high temperature decomposes, the comprehensive treating process process of deep oxidation.Its advantage is eliminated unwanted bacteria for reducing the waste volume rapidly significantly, can also be used for the heat supply generating.Shortcoming is big for investment, to airborne release objectionable impurities ianthone such as dioxin etc.) and scatter bad dust, and generated energy is limited.3) compost: become harmless corruption behind the rubbish fermentation and plant matter, like the disclosed method that rubbish from cooking is converted into fertilizer of patent CN1858027A.But fermentation period is long, and nutrient content is low, and it is big to handle the back volume, is only applicable to ungetable rural area, is inappropriate for the bigger city of rubbish from cooking generation.
In general the rubbish from cooking waste material is abundant, and the contents of saccharide ratio is big, and hogwash is with protein; Starch and animal tallow class etc. are staple, and saliferous, and oil quantity is high; Be unfavorable for direct utilization; But organic content is high, has higher biodegradability, and this also provides feasible approach for the trans-utilization of hogwash.Present topmost transformation technology is a biotransformation method.Bio-transformation is the metabolism that utilizes mikrobe, realizes the stabilization of rubbish, and is innoxious, carries out the recycling of resource simultaneously.Wherein apparatus for disposing of food waste is to handle rubbish from cooking the best way at present, and hogwash and microbial strains are dropped in the special garbage disposer, utilizes multiple aerobic mikrobe that the organism in the hogwash is decomposed.It is low that this method has expense, obvious processing effect with can eliminate rubbish in advantages such as sources, therefore also be one of problem of popular research both at home and abroad in recent years.
The research of Japan aspect biological degradation hogwash rubbish is more successful, and the hogwash handler is in big area popularization in Japan.China also has company to introduce this type handler of Japan; But microbial strains then can only dependence on import, and the microbial strains of Japan is relatively poor to the degradation effect of oils composition in the rubbish, and some fibre-bearing food with high residues can not well be degraded; The diet formula of China has determined that the oils composition is higher in the hogwash rubbish of China; Therefore, the microbial strains of import is when handling domestic hogwash rubbish, and effect is unsatisfactory.
In recent years; China also has some enterprise self-determinings to research and develop microbial strains and the method for handling rubbish from cooking; Microbial preparation like the disclosed degraded hogwash of treatment process, the patent CN101173232A rubbish of the disclosed high concentration swill of patent CN100375723C; Solved the handling problem of rubbish from cooking to a certain extent, but the inferior position of aspect such as its reduction rate is low, the treatment time is long, ambient temperature range is little has also limited its development.
Also having company to choose anaerobion degrades; In the experiment of laboratory lab scale; This bacterial classification has higher degradation rate, but in suitability for industrialized production and practical application, is difficult to reach the anaerobism requirement, so anaerobion is not suitable for present refuse biochemical treatment facility.
At present, still there is following deficiency in the prior art of utilizing biological degradation to handle rubbish from cooking that can industrial application:
1) can not efficient degradation fibre-bearing food with high residue.The high residues of fibre-bearing such as the wild rice stem in the rubbish from cooking, bamboo shoot shell if can not in time degrade, often are deposited on and handle in the trough operation that then hinders whipping device of long duration.
2). the grease in the rubbish from cooking can not effectively be degraded.China's diet formula has determined that grease is high in the hogwash, and grease can not get good degraded then makes matrix be sticked together, and after operation for some time, the matrix in the trough just can be lumpd, and influences the normal operation of machine.
3) degradation time is long, and degradation rate is low.In the daily life, have every day a large amount of new hogwash to produce, if can not be degraded timely and effectively, hogwash is accumulated in to be handled in the trough, the load that then exceeds handler of long duration, and severe patient loses the use of machine.
In sum, the present treatment process of rubbish from cooking still can the lingering section residue, is unfavorable for the work of treatment facility, and residual residue also needs further to handle simultaneously, therefore, still needs mikrobe associate strain, preparation and the method for new processing rubbish from cooking.
Summary of the invention
To be solved by this invention is the existing method of handling rubbish from cooking, the residual problem that residue is arranged.
The purpose of this invention is to provide a kind of associate strain of rubbish from cooking and a kind of method of handling rubbish from cooking of residual residue not handled.
First purpose of the present invention provides a kind of associate strain of handling rubbish from cooking, comprising:
Bacillus amyloliquefaciens (
Bacillus amyloliquefaciens),
Bacillus licheniformis (
Bacillus licheniformis),
Bacillus cereus (
Bacillus cereus)
Bacillus megaterium (
Bacillus megaterium),
Subtilis (
Bacillus subtilis).
The above-mentioned associate strain of the present invention; The part by weight of bacillus amyloliquefaciens, Bacillus licheniformis, bacillus cereus, bacillus megaterium and subtilis is preferably 1 ~ 3:1 ~ 3:0.5 ~ 2:1 ~ 3:1 ~ 3; Further be preferably 1.5 ~ 3:1.5 ~ 3:0.5 ~ 1.5:1.5 ~ 3:1.5 ~ 3, more preferably 1.5 ~ 2.5:1.5 ~ 2.5:0.5 ~ 1.5:1.5 ~ 2.5:1.5 ~ 2.5; Most preferably be 2:2:1:2:2.
The associate strain that the present invention is above-mentioned, water cut is preferably 20 ~ 35%; More preferably 25 ~ 30%, most preferably be 28.2 ~ 28.5%.
Second purpose of the present invention provides a kind of method of handling rubbish from cooking, and step comprises:
Step 1 provides the present invention above-mentioned associate strain;
Step 2 is mixed above-mentioned associate strain with rubbish from cooking, ferment; Wherein, in the fermenting process, water ratio maintains in 50% ~ 95% scope.
The method of the above-mentioned processing rubbish from cooking of the present invention; Treatment facility can be selected existing any available processes equipment for use; Like the disclosed hogwash material processor of patent CN2734354Y, the disclosed hogwash garbage disposer of patent CN2894847Y, perhaps commercially available hogwash handler etc.
In the method for processing rubbish from cooking of the present invention, in the step 2, the fermenting process water ratio is preferably 60% ~ 90%, and more preferably 80% ~ 90%.
In the method for the processing rubbish from cooking that the present invention is above-mentioned, every gram associate strain is handled hogwash weight and is preferably 0.1 ~ 1 kilogram, and more preferably 0.1 ~ 0.8 kilogram, further be preferably 0.1 ~ 0.5 kilogram, most preferably be 0.2 kilogram.
The method of processing rubbish from cooking according to the invention, said rubbish from cooking can disposablely feed intake, intermittent type feeds intake, continous way feeds intake or the arbitrary combination of above-mentioned feeding mode.
The method of processing rubbish from cooking according to the invention, in treatment system, adding entry can be disposable adding, intermittent type adds, continous way adds or the above-mentioned arbitrary combination that adds the water mode.In a kind of preferred embodiment of the present invention, be provided with the water inlet pipe that leads to treatment system, hydromining adds with intermittent type or continous way adds.The method that adds water preferably sprays.
The method of processing rubbish from cooking according to the invention, the treatment time is preferably 5 ~ 20 hours.
Associate strain of the present invention carries out rubbish from cooking to be handled, and can not produce solid residue, and tunning is all emitted with the form of the aqueous solution, and the rubbish from cooking degradation speed is fast, and efficient is high, can realize the serialization of rubbish from cooking, the extensive processing.
Embodiment
The invention provides and a kind ofly handle the associate strain of rubbish from cooking and use said associate strain to carry out the method that rubbish from cooking is handled; Said associate strain comprises bacillus amyloliquefaciens, Bacillus licheniformis, bacillus cereus, bacillus megaterium and subtilis; Above-mentioned bacterial classification is mixed with rubbish from cooking; In 50 ~ 95% water ratio scopes, ferment, tunning is aqueous solution form and discharges, and does not have solid residue.
The method of through specific embodiment the present invention being handled the associate strain of rubbish from cooking below and using said associate strain to carry out the rubbish from cooking processing is carried out detailed introduction and description; So that better understand content of the present invention; But should be understood that following embodiment does not limit the scope of the invention.
Embodiment 1
Associate strain: the part by weight of bacillus amyloliquefaciens, Bacillus licheniformis, bacillus cereus, bacillus megaterium and subtilis is 2:2:1:2:2.
Drop into the 100kg rubbish from cooking in the rubbish from cooking treatment facility, add above-mentioned associate strain 500g.The rubbish from cooking treatment facility is connected with water inlet pipe, in treatment system, adds entry, and water ratio is reached in 60% ~ 90% scope, ferments.
In the fermenting process, can according to the variation of water ratio in the treatment system constantly or intermittent type add entry.
After 10 hours, rubbish from cooking is processed fully, and tunning is all discharged with the form of the aqueous solution, does not have solid residue residual.
Embodiment 2
Associate strain: the part by weight of bacillus amyloliquefaciens, Bacillus licheniformis, bacillus cereus, bacillus megaterium and subtilis is 1.8:2:0.9:2.2:1.9.
Drop into the 70kg rubbish from cooking in the rubbish from cooking treatment facility, add above-mentioned associate strain 500g.The rubbish from cooking treatment facility is connected with water inlet pipe, in treatment system, adds entry, and water ratio is reached in 80% ~ 90% scope, ferments.
In the fermenting process, can according to the variation of water ratio in the treatment system constantly or intermittent type add entry.
After 5 hours, rubbish from cooking is processed fully, and tunning is all discharged with the form of the aqueous solution, does not have solid residue residual.
Embodiment 3
Associate strain: the part by weight of bacillus amyloliquefaciens, Bacillus licheniformis, bacillus cereus, bacillus megaterium and subtilis is 2.2:1.9:1.2:2.1:1.9.
Drop into the 250kg rubbish from cooking in the rubbish from cooking treatment facility, add above-mentioned associate strain 500g.The rubbish from cooking treatment facility is connected with water inlet pipe, in treatment system, adds entry, and water ratio is reached in 50% ~ 70% scope, ferments.
In the fermenting process, can according to the variation of water ratio in the treatment system constantly or intermittent type add entry.
After 19 hours, rubbish from cooking is processed fully, and tunning is all discharged with the form of the aqueous solution, does not have solid residue residual.
Embodiment 4
Associate strain: the part by weight of bacillus amyloliquefaciens, Bacillus licheniformis, bacillus cereus, bacillus megaterium and subtilis is 2.8:1.2:1.0:2.5:1.4.
Drop into the 500kg rubbish from cooking in the rubbish from cooking treatment facility, add above-mentioned associate strain 500g.The rubbish from cooking treatment facility is connected with water inlet pipe, in treatment system, adds entry, and water ratio is reached in 70% ~ 95% scope, ferments.
In the fermenting process, can according to the variation of water ratio in the treatment system constantly or intermittent type add entry.
After 20 hours, rubbish from cooking is processed fully, and tunning is all discharged with the form of the aqueous solution, does not have solid residue residual.
Embodiment 5
Associate strain: the part by weight of bacillus amyloliquefaciens, Bacillus licheniformis, bacillus cereus, bacillus megaterium and subtilis is 1.4:1.0:0.6:2.0:2.7.
Drop into the 400kg rubbish from cooking in the rubbish from cooking treatment facility, add above-mentioned associate strain 500g.The rubbish from cooking treatment facility is connected with water inlet pipe, in treatment system, adds entry, and water ratio is reached in 70% ~ 95% scope, ferments.
In the fermenting process, can according to the variation of water ratio in the treatment system constantly or intermittent type add entry.
After 17 hours, rubbish from cooking is processed fully, and tunning is all discharged with the form of the aqueous solution, does not have solid residue residual.
Embodiment 6
Associate strain: the part by weight of bacillus amyloliquefaciens, Bacillus licheniformis, bacillus cereus, bacillus megaterium and subtilis is 2.5:2.7:1.2:2.0:2.0.
Drop into the 150kg rubbish from cooking in the rubbish from cooking treatment facility, add above-mentioned associate strain 500g.The rubbish from cooking treatment facility is connected with water inlet pipe, in treatment system, adds entry, and water ratio is reached in 70% ~ 95% scope, ferments.
In the fermenting process, can according to the variation of water ratio in the treatment system constantly or intermittent type add entry.
After 10 hours, rubbish from cooking is processed fully, and tunning is all discharged with the form of the aqueous solution, does not have solid residue residual.
More than specific embodiment of the present invention is described in detail, but it is just as example, the present invention is not restricted to the specific embodiment of above description.To those skilled in the art, any equivalent modifications that the present invention is carried out with substitute also all among category of the present invention.Therefore, not breaking away from impartial conversion and the modification of being done under the spirit and scope of the present invention, all should contain within the scope of the invention.
Claims (10)
1. an associate strain of handling rubbish from cooking is characterized in that, comprising: bacillus amyloliquefaciens, Bacillus licheniformis, bacillus cereus, bacillus megaterium and subtilis.
2. associate strain according to claim 1 is characterized in that, the part by weight of bacillus amyloliquefaciens, Bacillus licheniformis, bacillus cereus, bacillus megaterium and subtilis is 1 ~ 3:1 ~ 3:0.5 ~ 2:1 ~ 3:1 ~ 3.
3. associate strain according to claim 2 is characterized in that, the part by weight of bacillus amyloliquefaciens, Bacillus licheniformis, bacillus cereus, bacillus megaterium and subtilis is 2:2:1:2:2.
4. method of using the said associate strain of claim 1 to handle rubbish from cooking is characterized in that step comprises:
Step 1 provides claim 1 described associate strain;
Step 2 is mixed above-mentioned associate strain with rubbish from cooking, ferment; Wherein, in the fermenting process, water ratio maintains in 50% ~ 95% scope.
5. method according to claim 4 is characterized in that, in the step 2, the fermenting process water ratio is 60% ~ 90%.
6. method according to claim 4 is characterized in that, it is 0.1 ~ 1 kilogram that every gram associate strain is handled hogwash weight.
7. method according to claim 5 is characterized in that, it is 0.2 kilogram that every gram associate strain is handled hogwash weight.
8. according to any described method in the claim 4 ~ 7, it is characterized in that, said rubbish from cooking be disposablely feed intake, intermittent type feeds intake, continous way feeds intake or the arbitrary combination of above-mentioned feeding mode.
9. method according to claim 4 is characterized in that, in treatment system, adding entry is intermittent type adding, continous way adding, disposable adding or the above-mentioned arbitrary combination that adds the water mode.
10. method according to claim 9 is characterized in that, is provided with the water inlet pipe that leads to treatment system, and hydromining adds with intermittent type or continous way adds.
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| CN2012101450834A CN102747011A (en) | 2012-05-11 | 2012-05-11 | Mixing strain for treating kitchen waste, and method |
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Cited By (10)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104307841A (en) * | 2014-08-29 | 2015-01-28 | 广东源盛生态环保科技有限公司 | Low-cost method for killing domestic garbage infectious disease source |
| CN104611268A (en) * | 2015-02-05 | 2015-05-13 | 浙江大学 | Pesticide-degrading bacterium taking bacillus amyloliquefaciens as main body as well as preparation method and application thereof |
| CN106623349A (en) * | 2016-10-31 | 2017-05-10 | 广州博善生物科技股份有限公司 | Kitchen waste on-site treatment method |
| CN107649493A (en) * | 2017-10-31 | 2018-02-02 | 上海恒晔生物科技有限公司 | A kind of preparation method and waste disposal method of the bio-matrix for loading strain |
| CN111548949A (en) * | 2020-03-27 | 2020-08-18 | 惠州市通用机电设备有限公司 | Microbial agent for degrading organic wastes and preparation method thereof |
| CN112481152A (en) * | 2020-11-05 | 2021-03-12 | 上海应用技术大学 | Microbial agent-enzyme preparation compound and method for degrading kitchen garbage by using same |
| WO2021046858A1 (en) * | 2019-09-14 | 2021-03-18 | 南京大学（溧水）生态环境研究院 | Mixed bacteria used for aerobic treatment of kitchen waste |
| WO2021046853A1 (en) * | 2019-09-14 | 2021-03-18 | 南京大学（溧水）生态环境研究院 | Aerobic treatment method for kitchen waste |
| CN113322251A (en) * | 2021-04-09 | 2021-08-31 | 杭州楠大环保科技有限公司 | Composite microbial degradation microbial inoculum for kitchen waste treatment and preparation method and application thereof |
| CN115216433A (en) * | 2022-09-01 | 2022-10-21 | 浙江永尔佳环保科技有限公司 | Kitchen waste degrading composite bacterium and application thereof |
Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101444786A (en) * | 2008-12-29 | 2009-06-03 | 上海恒晔生物科技有限公司 | Method for treating waste after meal |
| CN101538538A (en) * | 2008-03-18 | 2009-09-23 | 上海环伟生物科技有限公司 | Composite microorganism viable bacteria preparation and preparation method and application of same |
| CN102391950A (en) * | 2011-11-17 | 2012-03-28 | 苏柯汉（潍坊）生物工程有限公司 | Food waste deodorization composite bacteria and preparation method thereof |
| CN102433261A (en) * | 2011-11-17 | 2012-05-02 | 苏柯汉（潍坊）生物工程有限公司 | Composite bacteria for removing oil from kitchen waste and preparation method for composite bacteria |
-
2012
- 2012-05-11 CN CN2012101450834A patent/CN102747011A/en active Pending
Patent Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101538538A (en) * | 2008-03-18 | 2009-09-23 | 上海环伟生物科技有限公司 | Composite microorganism viable bacteria preparation and preparation method and application of same |
| CN101444786A (en) * | 2008-12-29 | 2009-06-03 | 上海恒晔生物科技有限公司 | Method for treating waste after meal |
| CN102391950A (en) * | 2011-11-17 | 2012-03-28 | 苏柯汉（潍坊）生物工程有限公司 | Food waste deodorization composite bacteria and preparation method thereof |
| CN102433261A (en) * | 2011-11-17 | 2012-05-02 | 苏柯汉（潍坊）生物工程有限公司 | Composite bacteria for removing oil from kitchen waste and preparation method for composite bacteria |
Cited By (11)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104307841A (en) * | 2014-08-29 | 2015-01-28 | 广东源盛生态环保科技有限公司 | Low-cost method for killing domestic garbage infectious disease source |
| CN104611268A (en) * | 2015-02-05 | 2015-05-13 | 浙江大学 | Pesticide-degrading bacterium taking bacillus amyloliquefaciens as main body as well as preparation method and application thereof |
| CN106623349A (en) * | 2016-10-31 | 2017-05-10 | 广州博善生物科技股份有限公司 | Kitchen waste on-site treatment method |
| CN107649493A (en) * | 2017-10-31 | 2018-02-02 | 上海恒晔生物科技有限公司 | A kind of preparation method and waste disposal method of the bio-matrix for loading strain |
| WO2021046858A1 (en) * | 2019-09-14 | 2021-03-18 | 南京大学（溧水）生态环境研究院 | Mixed bacteria used for aerobic treatment of kitchen waste |
| WO2021046853A1 (en) * | 2019-09-14 | 2021-03-18 | 南京大学（溧水）生态环境研究院 | Aerobic treatment method for kitchen waste |
| CN111548949A (en) * | 2020-03-27 | 2020-08-18 | 惠州市通用机电设备有限公司 | Microbial agent for degrading organic wastes and preparation method thereof |
| CN112481152A (en) * | 2020-11-05 | 2021-03-12 | 上海应用技术大学 | Microbial agent-enzyme preparation compound and method for degrading kitchen garbage by using same |
| CN113322251A (en) * | 2021-04-09 | 2021-08-31 | 杭州楠大环保科技有限公司 | Composite microbial degradation microbial inoculum for kitchen waste treatment and preparation method and application thereof |
| CN113322251B (en) * | 2021-04-09 | 2022-05-10 | 杭州楠大环保科技有限公司 | Composite microbial degradation microbial inoculum for kitchen waste treatment and preparation method and application thereof |
| CN115216433A (en) * | 2022-09-01 | 2022-10-21 | 浙江永尔佳环保科技有限公司 | Kitchen waste degrading composite bacterium and application thereof |
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Application publication date: 20121024 |