CN104531550A - High-temperature kitchen waste degradation microbial agent and preparing and using method thereof - Google Patents

High-temperature kitchen waste degradation microbial agent and preparing and using method thereof Download PDF

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CN104531550A
CN104531550A CN201410647380.8A CN201410647380A CN104531550A CN 104531550 A CN104531550 A CN 104531550A CN 201410647380 A CN201410647380 A CN 201410647380A CN 104531550 A CN104531550 A CN 104531550A
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genus bacillus
bacillus
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liquid activation
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李宗武
马玉莹
贺保国
卢乐健
孙加安
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SHANDONG URBAN-MINING ENVIRONMENTAL PROTECTION GROUP Co Ltd
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SHANDONG URBAN-MINING ENVIRONMENTAL PROTECTION GROUP Co Ltd
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    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12NMICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
    • C12N1/00Microorganisms, 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
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    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless

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Abstract

The invention discloses a high-temperature kitchen waste degradation microbial agent and a preparing and using method thereof. A microbial strain comprises, by weight, 15-30 parts of nuby land anoxybacillus, 10-25 parts of liquefaction thermophilic bacillus, 20-40 parts of hot nitrogen bacillus and 25-50 parts of geobacillus stearothermophilus. Compared with the prior art, the high-temperature kitchen waste degradation microbial agent has the beneficial effects that as for kitchen waste with different integrants, reasonable matching on single bacterium powder can be carried out, and single bacterial strains are cooperated for degrading the kitchen waste in a collaborative mode; the number of effective viable bacteria in the single bacterium powder in the composite microbial agent is large, and when the microbial agent is used for degrading the kitchen waste, only a small number of microbial agents is needed for sufficiently and rapidly degrading the kitchen waste; components in the microbial agent are high-temperature cultures, the optimum fermentation temperature ranges from 55 DEG C to 65 DEG C, pathogenic bacteria such as escherichia coli and staphylococcus aureus in the kitchen waste can be effectively inactivated in the fermentation process, and the biosecurity is high.

Description

A kind of high temperature degradation changing food waste microbiobacterial agent and preparation thereof, using method
Technical field
The invention belongs to biological technical field, relate to a kind of high temperature degradation changing food waste microbiobacterial agent and preparation thereof, using method.
Background technology
Changing food waste has the features such as high oil, high salt, high protein content, be easy to grow mosquitos and flies, rot if dealt with improperly, and distribute stench, grow mosquitos and flies, some changing food wastes are even used for refining " sewer oil ", feeding " swill pig " etc. by lawless person, cause serious impact to environment and health of people.
At present, the biological treatment of changing food waste, mainly contains mesophilic microorganism facture and high temperature microbe facture.
The leavening temperature of mesophilic microorganism facture is generally 25 ~ 40 DEG C, and the leavening temperature of pyroprocess can reach more than 50 DEG C.
Due to most of pathogenic bacterium, the optimum growth temperature of such as streptococcus aureus, intestinal bacteria etc. is about 35 DEG C, by mesophilic microorganism facture, fermentative processing is carried out to changing food waste, the pathogenic bacterium of non-deactivation in its output object, may be there are, there is potential safety hazard to a certain degree.
If carry out fermentative processing by high temperature microbe facture to changing food waste, then while fermenting process, deactivation can be carried out to the pathogenic bacterium existed in changing food waste.And the optimum temperuture of general enzyme is 50 ~ 60 DEG C, adopts the fermentation of high temperature microbe facture, the enzyme in bacterial classification can be made to play maximum degradation rate, shorten fermentation time, reduce fermentation energy consumption.
Summary of the invention
For the above-mentioned technical problem existed in prior art, the present invention proposes a kind of high temperature degradation changing food waste microbiobacterial agent, this microbiobacterial agent, as the microbial inoculum used in high temperature microbe facture, effectively can be degraded to changing food waste.
To achieve these goals, the present invention adopts following technical scheme:
A kind of high temperature degradation changing food waste microbiobacterial agent, described microbial strains is composited by the strain raw material of following mass fraction: exert than halogen ground anaerobic genus bacillus 15-30 part, thermophilic liquefaction genus bacillus 10-25 part, hot denitrogenation ground bacillus 20-40 part, Geobacillus stearothermophilus 25-50 part.
The invention allows for a kind of preparation method of high temperature degradation changing food waste microbiobacterial agent, it adopts following technical scheme:
A preparation method for high temperature degradation changing food waste microbiobacterial agent, comprises following preparation process:
S1, will exert and carry out individual plant cultivation respectively than halogen ground anaerobic genus bacillus, thermophilic liquefaction genus bacillus, hot denitrogenation ground bacillus, Geobacillus stearothermophilus, then obtained individual plant bacterium colony is carried out activation culture according in the inoculum size access liquid nutrient medium of 10-20%, then volume ratio is housed is ferment in the fermentation equipment of 60-75% substratum by the bacterial classification access after activation;
Adsorbed by gained fermented liquid carrier, obtained living bacteria count is 5 × 10 9individual/gram exert bacterium powder more single than halogen ground anaerobic genus bacillus, thermophilic liquefaction genus bacillus, hot denitrogenation ground bacillus, Geobacillus stearothermophilus; Absorption carrier is diatomite;
S2, obtain and exert than halogen ground anaerobic genus bacillus 15-30 part, thermophilic liquefaction genus bacillus 10-25 part, hot denitrogenation ground bacillus 20-40 part, Geobacillus stearothermophilus 25-50 part, the mass fraction of single for above-mentioned each bacterial strain bacterium powder is fully mixed to get microbiobacterial agent.
In above-mentioned steps s1, exert and than the single bacterium powder preparation process of halogen ground anaerobic genus bacillus be:
S111, exerting on the test tube slant after purified be seeded to than halogen ground anaerobic genus bacillus volume ratio is housed is in the triangular flask of liquid activation medium of 10-20%; The solvent of liquid activation medium is distilled water, and solute component and concentration thereof are: peptone 8-12g/L, extractum carnis 2-4g/L, yeast extract paste 3-5g/L, Zulkovsky starch 15-35g/L, sodium-chlor 4-6g/L, and the pH value of liquid activation medium is 7.0-7.2; Inoculation exert than halogen ground anaerobic genus bacillus liquid activation medium temperature 55-65 DEG C, under shaking speed is 140-160r/min, cultivate 18-24h;
S112, will activate exerting to be seeded to than halogen ground anaerobic genus bacillus and being equipped with in fermentor tank that volume ratio is the fermention medium of 60-75% of gained through step s111, inoculum size is 2-4%; The solvent of fermention medium is distilled water, and solute component and concentration thereof are: peptone 8-12g/L, extractum carnis 2-4g/L, yeast extract paste 3-5g/L, Zulkovsky starch 15-35g/L, sodium-chlor 4-6g/L, and the pH value of fermention medium is 7.0-7.2; Inoculation exert than halogen ground anaerobic genus bacillus fermention medium temperature 55-65 DEG C, under mixing speed is 200-220r/min, enlarged culturing 20-30h, until in fermentor tank to exert than halogen ground anaerobic genus bacillus spore production rate be more than 80%, exerting after fermentation is adsorbed, until living bacteria count reaches 5 × 10 than halogen ground anaerobic genus bacillus carrier 9individual/gram, the single bacterium powder than halogen ground anaerobic genus bacillus must be exerted.
In above-mentioned steps s1, the single bacterium powder preparation process of thermophilic liquefaction genus bacillus is:
S121, the thermophilic liquefaction genus bacillus on the test tube slant after purified is seeded to volume ratio is housed is in the triangular flask of liquid activation medium of 10-20%; The solvent of liquid activation medium is distilled water, solute component and concentration thereof are: peptone 8-12g/L, extractum carnis 2-4g/L, tween 80 20-35ml/L, N.F,USP MANNITOL 15-25g/L, yeast extract paste 5-10g/L, glucose 15-25g/L, sodium-chlor 4-6g/L, and the pH value of liquid activation medium is 7.0-7.2; The liquid activation medium inoculating thermophilic liquefaction genus bacillus temperature 55-60 DEG C, under shaking speed 140-160r/min, cultivate 18-24h;
S122, to be seeded to by the thermophilic liquefaction genus bacillus activating gained to be equipped with in fermentor tank that volume ratio is the fermention medium of 60-75% through step s121, inoculum size is 2-4%; The solvent of fermention medium is distilled water, solute component and concentration thereof are: peptone 8-12g/L, extractum carnis 2-4g/L, tween 80 20-35ml/L, N.F,USP MANNITOL 15-25g/L, yeast extract paste 5-10g/L, glucose 15-25g/L, sodium-chlor 4-6g/L, and the pH value of fermention medium is 7.0-7.2; The fermention medium inoculating thermophilic liquefaction genus bacillus temperature 55-62 DEG C, under mixing speed is 200-220r/min, enlarged culturing 24-36h, until the thermophilic liquefaction genus bacillus spore production rate in fermentor tank is more than 80%, thermophilic liquefaction genus bacillus carrier after fermentation is adsorbed, until living bacteria count reaches 5 × 10 9individual/gram, obtain the single bacterium powder of thermophilic liquefaction genus bacillus.
In above-mentioned steps s1, the single bacterium powder preparation process of hot denitrogenation ground bacillus is:
S131, the denitrogenation ground bacillus on the test tube slant after purified is seeded to volume ratio is housed is in the triangular flask of liquid activation medium of 10-25%; The solvent of liquid activation medium is distilled water, and solute component and concentration thereof are: peptone 8-12g/L, extractum carnis 2-4g/L, N.F,USP MANNITOL 15-25g/L, glucose 15-25g/L, sodium-chlor 4-6g/L, and the pH value of liquid activation medium is 7.0-7.2; The liquid activation medium of inoculation denitrogenation ground bacillus temperature 55-65 DEG C, under shaking speed is 140-160r/min, cultivate 18-24h;
S132, be seeded to be equipped with activating the denitrogenation ground bacillus of gained through step s131 in fermentor tank that volume ratio is the fermention medium of 60-75%, inoculum size is 2-4%; The solvent of fermention medium is distilled water, and solute component and concentration thereof are: peptone 8-12g/L, extractum carnis 2-4g/L, N.F,USP MANNITOL 15-25g/L, glucose 15-25g/L, sodium-chlor 4-6g/L, and the pH value of fermention medium is 7.0-7.2; The fermention medium of inoculation denitrogenation ground bacillus temperature 55-65 DEG C, under mixing speed is 200-220r/min, enlarged culturing 24-40h, until the denitrogenation ground bacillus spore production rate in fermentor tank is more than 80%, denitrogenation ground bacillus carrier after fermentation is adsorbed, until living bacteria count reaches 5 × 10 9individual/gram, obtain the single bacterium powder of denitrogenation ground bacillus.
In above-mentioned steps s1, the single bacterium powder preparation process of Geobacillus stearothermophilus is:
S141, the Geobacillus stearothermophilus on the test tube slant after purified is seeded to volume ratio is housed is in the triangular flask of liquid activation medium of 10-20%; The solvent of liquid activation medium is distilled water, solute component and concentration thereof are: peptone 8-12g/L, yeast extract paste 5-10g/L, glucose 15-25g/L, sodium-chlor 4-6g/L, Bromothymol blue solution trace, and the pH value of liquid activation medium is 7.0-7.2; The liquid activation medium of inoculation Geobacillus stearothermophilus temperature 55-65 DEG C, under shaking speed is 140-160r/min, cultivate 18-24h;
S142, be seeded to be equipped with activating the Geobacillus stearothermophilus of gained through step s141 in fermentor tank that volume ratio is the fermention medium of 60-75%, inoculum size is 2-4%; The solvent of fermention medium is distilled water, and solute component and concentration thereof are: peptone 8-12g/L, yeast extract paste 5-10g/L, glucose 15-25g/L, sodium-chlor 4-6g/L, Bromothymol blue solution trace, and the pH value of fermention medium is 7.0-7.2; The fermention medium of inoculation Geobacillus stearothermophilus temperature 55-65 DEG C, under mixing speed is 200-220r/min, enlarged culturing 24-40h, until the Geobacillus stearothermophilus spore production rate in fermentor tank is more than 80%, Geobacillus stearothermophilus carrier after fermentation is adsorbed, until living bacteria count reaches 5 × 10 9individual/gram, obtain the single bacterium powder of Geobacillus stearothermophilus.
In addition, the invention allows for a kind of using method of high temperature degradation changing food waste microbiobacterial agent, its technical scheme is as follows:
The microbiobacterial agent prepared fully is mixed according to the ratio that mass ratio is 1:250-500 with changing food waste, at 55-65 DEG C, aerobic fermentation 12-15h.
Compared with prior art, the bacterial strain exerted than halogen ground anaerobic genus bacillus, thermophilic liquefaction genus bacillus, hot denitrogenation ground bacillus, Geobacillus stearothermophilus is carried out enlarged culturing by the present invention, carry out high-density enlarged culturing again, finally carry out adsorbing obtaining the single dry bacterium powder of each bacterial strain with carrier, rational proportion is adopted according to its purposes, obtain the high temperature microbe microbial inoculum for changing food waste of degrading after compound, for the process of changing food waste, it has following several respects advantage:
1, the changing food waste for heterogeneity can carry out rational proportion to single bacterium powder, each single bacterial strain is cooperated with each other, Synergistic degradation changing food waste.
2, in composite fungus agent, in each one-component, living bacteria count is high, for degrade changing food waste time, only need an a small amount of microbiobacterial agent just can to degrade fully, rapidly changing food waste, cost is low, consumption is few, using method is easy.
3, in composite fungus agent, each component is high-temperature strain, and optimum leavening temperature is all at 55-65 DEG C, and effectively can carry out deactivation to pathogenic bacterium such as the intestinal bacteria in changing food waste, streptococcus aureuses during the fermentation, biological safety is high.
Embodiment
Below in conjunction with embodiment, the present invention is described in further detail:
A kind of high temperature degradation changing food waste microbiobacterial agent, is composited by the strain raw material of following mass fraction: exert than halogen ground anaerobic genus bacillus 15-30 part, thermophilic liquefaction genus bacillus 10-25 part, hot denitrogenation ground bacillus 20-40 part, Geobacillus stearothermophilus 25-50 part.
In actual application, according to the difference of protein, starch, fat, content of cellulose in changing food waste, the consumption of above each component in microbiobacterial agent can be adjusted targetedly.
One, the preparation of the single bacterium powder of each bacterial strain and microbiobacterial agent
Embodiment 1
Individual plant cultivation and high-density enlarged culturing is carried out than halogen ground anaerobic genus bacillus, thermophilic liquefaction genus bacillus, hot denitrogenation ground bacillus, Geobacillus stearothermophilus respectively to exerting, finally the single thalline diatomite obtained after cultivation is adsorbed, the single dry bacterium powder of obtained each bacterial strain.
1. exert the preparation of bacterium powder more single than halogen ground anaerobic genus bacillus
(1), exerting on the test tube slant after purified is seeded to than halogen ground anaerobic genus bacillus volume ratio is housed is in the triangular flask of liquid activation medium of 10-20%; The solvent of liquid activation medium is distilled water, and solute component and concentration thereof are: peptone 8g/L, extractum carnis 3g/L, yeast extract paste 5g/L, Zulkovsky starch 17g/L, sodium-chlor 4g/L, and the pH value of liquid activation medium is 7.0; Inoculation exerts liquid activation medium than halogen ground anaerobic genus bacillus under temperature 55 DEG C, shaking speed are 140r/min, cultivates 22h;
(2), will exerting to be seeded to than halogen ground anaerobic genus bacillus and be equipped with in fermentor tank that volume ratio is the fermention medium of 65% through step (1) activation gained, inoculum size is 2%; The solvent of fermention medium is distilled water, and solute component and concentration thereof are: peptone 8g/L, extractum carnis 3g/L, yeast extract paste 5g/L, Zulkovsky starch 17g/L, sodium-chlor 4g/L, and the pH value of liquid activation medium is 7.0; Inoculation exerts liquid activation medium than halogen ground anaerobic genus bacillus under temperature 55 DEG C, mixing speed are 200r/min, enlarged culturing 28h, until in fermentor tank to exert than halogen ground anaerobic genus bacillus spore production rate be more than 80%, exerting after fermentation is adsorbed, until living bacteria count reaches 5 × 10 than halogen ground anaerobic genus bacillus carrier 9individual/gram, the single bacterium powder than halogen ground anaerobic genus bacillus must be exerted.
2. the preparation of the single bacterium powder of thermophilic liquefaction genus bacillus
(1), the thermophilic liquefaction genus bacillus on the test tube slant after purified is seeded to volume ratio is housed is in the triangular flask of liquid activation medium of 15%; The solvent of liquid activation medium is distilled water, solute component and concentration thereof are: peptone 10g/L, extractum carnis 4g/L, tween 80 25ml/L, N.F,USP MANNITOL 15g/L, yeast extract paste 9g/L, glucose 25g/L, sodium-chlor 6g/L, and the pH value of liquid activation medium is 7.1; The liquid activation medium inoculating thermophilic liquefaction genus bacillus, under temperature 60 C, shaking speed 160r/min, cultivates 18h;
(2), by being seeded to through the thermophilic liquefaction genus bacillus of step (1) activation gained be equipped with in fermentor tank that volume ratio is the fermention medium of 70%, inoculum size is 3%; The solvent of fermention medium is distilled water, solute component and concentration thereof are: peptone 10g/L, extractum carnis 4g/L, tween 80 25ml/L, N.F,USP MANNITOL 15g/L, yeast extract paste 9g/L, glucose 25g/L, sodium-chlor 6g/L, and the pH value of liquid activation medium is 7.1; Inoculate the liquid activation medium of thermophilic liquefaction genus bacillus under temperature 60 C, mixing speed are 220r/min, enlarged culturing 24h, until the thermophilic liquefaction genus bacillus spore production rate in fermentor tank is more than 80%, thermophilic liquefaction genus bacillus carrier after fermentation is adsorbed, until living bacteria count reaches 5 × 10 9individual/gram, obtain the single bacterium powder of thermophilic liquefaction genus bacillus.
3. the preparation of the single bacterium powder of hot denitrogenation ground bacillus
(1), the denitrogenation ground bacillus on the test tube slant after purified is seeded to volume ratio is housed is in the triangular flask of liquid activation medium of 25%; The solvent of liquid activation medium is distilled water, and solute component and concentration thereof are: peptone 9g/L, extractum carnis 4g/L, N.F,USP MANNITOL 20g/L, glucose 25g/L, sodium-chlor 4g/L, and the pH value of liquid activation medium is 7.0; The liquid activation medium of inoculation denitrogenation ground bacillus, under temperature 65 DEG C, shaking speed are 150r/min, cultivates 19h;
(2), by being seeded to through the denitrogenation ground bacillus of step (1) activation gained be equipped with in fermentor tank that volume ratio is the fermention medium of 70%, inoculum size is 2%; The solvent of fermention medium is distilled water, and solute component and concentration thereof are: peptone 11g/L, extractum carnis 3g/L, N.F,USP MANNITOL 22g/L, glucose 24g/L, sodium-chlor 5g/L, and the pH value of fermention medium is 7.0; The fermention medium of inoculation denitrogenation ground bacillus is under temperature 58 DEG C, mixing speed are 210r/min, enlarged culturing 36h, until the denitrogenation ground bacillus spore production rate in fermentor tank is more than 80%, denitrogenation ground bacillus carrier after fermentation is adsorbed, until living bacteria count reaches 5 × 10 9individual/gram, obtain the single bacterium powder of denitrogenation ground bacillus.
4. the preparation of the single bacterium powder of Geobacillus stearothermophilus
(1), the Geobacillus stearothermophilus on the test tube slant after purified is seeded to volume ratio is housed is in the triangular flask of liquid activation medium of 15%; The solvent of liquid activation medium is distilled water, and solute component and concentration thereof are: peptone 9g/L, yeast extract paste 7g/L, glucose 18g/L, sodium-chlor 5g/L, Bromothymol blue solution trace, and the pH value of liquid activation medium is 7.2; The liquid activation medium of inoculation Geobacillus stearothermophilus, under temperature 62 DEG C, shaking speed are 150r/min, cultivates 24h;
(2), by being seeded to through the Geobacillus stearothermophilus of step (1) activation gained be equipped with in fermentor tank that volume ratio is the fermention medium of 75%, inoculum size is 4%; The solvent of fermention medium is distilled water, and solute component and concentration thereof are: peptone 10g/L, yeast extract paste 9g/L, glucose 17g/L, sodium-chlor 5g/L, Bromothymol blue solution trace, and the pH value of fermention medium is 7.0; The fermention medium of inoculation Geobacillus stearothermophilus is under temperature 57 DEG C, mixing speed are 220r/min, enlarged culturing 40h, until the Geobacillus stearothermophilus spore production rate in fermentor tank is more than 80%, Geobacillus stearothermophilus carrier after fermentation is adsorbed, until living bacteria count reaches 5 × 10 9individual/gram, obtain the single bacterium powder of Geobacillus stearothermophilus.
5. the preparation of microbiobacterial agent
Get and exert than halogen ground anaerobic genus bacillus 25 parts, thermophilic liquefaction genus bacillus 20 parts, hot denitrogenation ground bacillus 30 parts, Geobacillus stearothermophilus 40 parts, the mass fraction of single for above-mentioned each bacterial strain bacterium powder is fully mixed to get microbiobacterial agent.
Embodiment 2
Individual plant cultivation and high-density enlarged culturing is carried out than halogen ground anaerobic genus bacillus, thermophilic liquefaction genus bacillus, hot denitrogenation ground bacillus, Geobacillus stearothermophilus respectively to exerting, finally the single thalline diatomite obtained after cultivation is adsorbed, the single dry bacterium powder of obtained each bacterial strain.
1. exert the preparation of bacterium powder more single than halogen ground anaerobic genus bacillus
(1), exerting on the test tube slant after purified is seeded to than halogen ground anaerobic genus bacillus volume ratio is housed is in the triangular flask of liquid activation medium of 15%; The solvent of liquid activation medium is distilled water, and solute component and concentration thereof are: peptone 9g/L, extractum carnis 4g/L, yeast extract paste 3g/L, Zulkovsky starch 25g/L, sodium-chlor 6g/L, and the pH value of liquid activation medium is 7.0; Inoculation exerts liquid activation medium than halogen ground anaerobic genus bacillus under temperature 60 C, shaking speed are 160r/min, cultivates 18h;
(2), will exerting to be seeded to than halogen ground anaerobic genus bacillus and be equipped with in fermentor tank that volume ratio is the fermention medium of 60% through step (1) activation gained, inoculum size is 4%; The solvent of fermention medium is distilled water, and solute component and concentration thereof are: peptone 10g/L, extractum carnis 3g/L, yeast extract paste 5g/L, Zulkovsky starch 18g/L, sodium-chlor 5g/L, and the pH value of fermention medium is 7.2; Inoculation exerts fermention medium than halogen ground anaerobic genus bacillus under temperature 65 DEG C, mixing speed are 210r/min, enlarged culturing 25h, until in fermentor tank to exert than halogen ground anaerobic genus bacillus spore production rate be more than 80%, exerting after fermentation is adsorbed, until living bacteria count reaches 5 × 10 than halogen ground anaerobic genus bacillus carrier 9individual/gram, the single bacterium powder than halogen ground anaerobic genus bacillus must be exerted.
2. the preparation of the single bacterium powder of thermophilic liquefaction genus bacillus
(1), the thermophilic liquefaction genus bacillus on the test tube slant after purified is seeded to volume ratio is housed is in the triangular flask of liquid activation medium of 20%; The solvent of liquid activation medium is distilled water, solute component and concentration thereof are: peptone 8g/L, extractum carnis 4g/L, tween 80 20ml/L, N.F,USP MANNITOL 20g/L, yeast extract paste 7g/L, glucose 24g/L, sodium-chlor 4g/L, and the pH value of liquid activation medium is 7.1; The liquid activation medium inoculating thermophilic liquefaction genus bacillus, under temperature 55 DEG C, shaking speed 140r/min, cultivates 20h;
(2), by being seeded to through the thermophilic liquefaction genus bacillus of step (1) activation gained be equipped with in fermentor tank that volume ratio is the fermention medium of 60%, inoculum size is 2%; The solvent of fermention medium is distilled water, and solute component and concentration thereof are: peptone 8g/L, extractum carnis 4g/L, tween 80 20ml/L, N.F,USP MANNITOL 20g/L, yeast extract paste 7g/L, glucose 24g/L, sodium-chlor 4g/L, and the pH value of liquid activation medium is 7.1; Inoculate the liquid activation medium of thermophilic liquefaction genus bacillus under temperature 55 DEG C, mixing speed are 210r/min, enlarged culturing 26h, until the thermophilic liquefaction genus bacillus spore production rate in fermentor tank is more than 80%, thermophilic liquefaction genus bacillus carrier after fermentation is adsorbed, until living bacteria count reaches 5 × 10 9individual/gram, obtain the single bacterium powder of thermophilic liquefaction genus bacillus.
3. the preparation of the single bacterium powder of hot denitrogenation ground bacillus
(1), the denitrogenation ground bacillus on the test tube slant after purified is seeded to volume ratio is housed is in the triangular flask of liquid activation medium of 25%; The solvent of liquid activation medium is distilled water, and solute component and concentration thereof are: peptone 10g/L, extractum carnis 3g/L, N.F,USP MANNITOL 23g/L, glucose 24g/L, sodium-chlor 4g/L, and the pH value of liquid activation medium is 7.2; The liquid activation medium of inoculation denitrogenation ground bacillus, under temperature 65 DEG C, shaking speed are 160r/min, cultivates 22h;
(2), by being seeded to through the denitrogenation ground bacillus of step (1) activation gained be equipped with in fermentor tank that volume ratio is the fermention medium of 62%, inoculum size is 3%; The solvent of fermention medium is distilled water, and solute component and concentration thereof are: peptone 10g/L, extractum carnis 3g/L, N.F,USP MANNITOL 23g/L, glucose 24g/L, sodium-chlor 4g/L, and the pH value of liquid activation medium is 7.2; The liquid activation medium of inoculation denitrogenation ground bacillus is under temperature 65 DEG C, mixing speed are 200r/min, enlarged culturing 28h, until the denitrogenation ground bacillus spore production rate in fermentor tank is more than 80%, denitrogenation ground bacillus carrier after fermentation is adsorbed, until living bacteria count reaches 5 × 10 9individual/gram, obtain the single bacterium powder of denitrogenation ground bacillus.
4. the preparation of the single bacterium powder of Geobacillus stearothermophilus
(1), the Geobacillus stearothermophilus on the test tube slant after purified is seeded to volume ratio is housed is in the triangular flask of liquid activation medium of 20%; The solvent of liquid activation medium is distilled water, and solute component and concentration thereof are: peptone 12g/L, yeast extract paste 10g/L, glucose 15g/L, sodium-chlor 6g/L, Bromothymol blue solution trace, and the pH value of liquid activation medium is 7.2; The liquid activation medium of inoculation Geobacillus stearothermophilus, under temperature 55 DEG C, shaking speed are 160r/min, cultivates 24h;
(2), by being seeded to through the Geobacillus stearothermophilus of step (1) activation gained be equipped with in fermentor tank that volume ratio is the fermention medium of 75%, inoculum size is 4%; The solvent of fermention medium is distilled water, and solute component and concentration thereof are: peptone 12g/L, yeast extract paste 10g/L, glucose 15g/L, sodium-chlor 6g/L, Bromothymol blue solution trace, and the pH value of liquid activation medium is 7.2; The liquid activation medium of inoculation Geobacillus stearothermophilus is under temperature 55 DEG C, mixing speed are 210r/min, enlarged culturing 40h, until the Geobacillus stearothermophilus spore production rate in fermentor tank is more than 80%, Geobacillus stearothermophilus carrier after fermentation is adsorbed, until living bacteria count reaches 5 × 10 9individual/gram, obtain the single bacterium powder of Geobacillus stearothermophilus.
5. the preparation of microbiobacterial agent
Get and exert than halogen ground anaerobic genus bacillus 20 parts, thermophilic liquefaction genus bacillus 15 parts, hot denitrogenation ground bacillus 25 parts, Geobacillus stearothermophilus 30 parts, the mass fraction of single for above-mentioned each bacterial strain bacterium powder is fully mixed to get microbiobacterial agent.
Embodiment 3
Individual plant cultivation and high-density enlarged culturing is carried out than halogen ground anaerobic genus bacillus, thermophilic liquefaction genus bacillus, hot denitrogenation ground bacillus, Geobacillus stearothermophilus respectively to exerting, finally the single thalline diatomite obtained after cultivation is adsorbed, the single dry bacterium powder of obtained each bacterial strain.
1. exert the preparation of bacterium powder more single than halogen ground anaerobic genus bacillus
(1), exerting on the test tube slant after purified is seeded to than halogen ground anaerobic genus bacillus volume ratio is housed is in the triangular flask of liquid activation medium of 10%; The solvent of liquid activation medium is distilled water, and solute component and concentration thereof are: peptone 12g/L, extractum carnis 2g/L, yeast extract paste 4g/L, Zulkovsky starch 15g/L, sodium-chlor 5g/L, and the pH value of liquid activation medium is 7.1; Inoculation exerts liquid activation medium than halogen ground anaerobic genus bacillus under temperature 65 DEG C, shaking speed are 150r/min, cultivates 24h;
(2), will exerting to be seeded to than halogen ground anaerobic genus bacillus and be equipped with in fermentor tank that volume ratio is the fermention medium of 75% through step (1) activation gained, inoculum size is 2-4%; The solvent of fermention medium is distilled water, and solute component and concentration thereof are: peptone 12g/L, extractum carnis 4g/L, yeast extract paste 3g/L, Zulkovsky starch 35g/L, sodium-chlor 6g/L, and the pH value of fermention medium is 7.1; Inoculation exert than halogen ground anaerobic genus bacillus fermention medium temperature 55-65 DEG C, under mixing speed is 220r/min, enlarged culturing 30h, until in fermentor tank to exert than halogen ground anaerobic genus bacillus spore production rate be more than 80%, exerting after fermentation is adsorbed, until living bacteria count reaches 5 × 10 than halogen ground anaerobic genus bacillus carrier 9individual/gram, the single bacterium powder than halogen ground anaerobic genus bacillus must be exerted.
2. the preparation of the single bacterium powder of thermophilic liquefaction genus bacillus
(1), the thermophilic liquefaction genus bacillus on the test tube slant after purified is seeded to volume ratio is housed is in the triangular flask of liquid activation medium of 10%; The solvent of liquid activation medium is distilled water, solute component and concentration thereof are: peptone 12g/L, extractum carnis 2g/L, tween 80 35ml/L, N.F,USP MANNITOL 25g/L, yeast extract paste 10g/L, glucose 15g/L, sodium-chlor 5g/L, and the pH value of liquid activation medium is 7.2; The liquid activation medium inoculating thermophilic liquefaction genus bacillus, under temperature 60 C, shaking speed 155r/min, cultivates 24h;
(2), by being seeded to through the thermophilic liquefaction genus bacillus of step (1) activation gained be equipped with in fermentor tank that volume ratio is the fermention medium of 75%, inoculum size is 4%; The solvent of fermention medium is distilled water, and solute component and concentration thereof are: peptone 12g/L, extractum carnis 2g/L, tween 80 35ml/L, N.F,USP MANNITOL 25g/L, yeast extract paste 10g/L, glucose 15g/L, sodium-chlor 5g/L, and the pH value of fermention medium is 7.2; Inoculate the fermention medium of thermophilic liquefaction genus bacillus under temperature 62 DEG C, mixing speed are 200r/min, enlarged culturing 36h, until the thermophilic liquefaction genus bacillus spore production rate in fermentor tank is more than 80%, thermophilic liquefaction genus bacillus carrier after fermentation is adsorbed, until living bacteria count reaches 5 × 10 9individual/gram, obtain the single bacterium powder of thermophilic liquefaction genus bacillus.
3. the preparation of the single bacterium powder of hot denitrogenation ground bacillus
(1), the denitrogenation ground bacillus on the test tube slant after purified is seeded to volume ratio is housed is in the triangular flask of liquid activation medium of 10%; The solvent of liquid activation medium is distilled water, and solute component and concentration thereof are: peptone 12g/L, extractum carnis 2g/L, N.F,USP MANNITOL 25g/L, glucose 15g/L, sodium-chlor 6g/L, and the pH value of liquid activation medium is 7.1; The liquid activation medium of inoculation denitrogenation ground bacillus, under temperature 55 DEG C, shaking speed are 140r/min, cultivates 24h;
(2), by being seeded to through the denitrogenation ground bacillus of step (1) activation gained be equipped with in fermentor tank that volume ratio is the fermention medium of 75%, inoculum size is 4%; The solvent of fermention medium is distilled water, and solute component and concentration thereof are: peptone 12g/L, extractum carnis 4g/L, N.F,USP MANNITOL 25g/L, glucose 25g/L, sodium-chlor 6g/L, and the pH value of fermention medium is 7.1; The fermention medium of inoculation denitrogenation ground bacillus is under temperature 55 DEG C, mixing speed are 220r/min, enlarged culturing 40h, until the denitrogenation ground bacillus spore production rate in fermentor tank is more than 80%, denitrogenation ground bacillus carrier after fermentation is adsorbed, until living bacteria count reaches 5 × 10 9individual/gram, obtain the single bacterium powder of denitrogenation ground bacillus.
4. the preparation of the single bacterium powder of Geobacillus stearothermophilus
(1), the Geobacillus stearothermophilus on the test tube slant after purified is seeded to volume ratio is housed is in the triangular flask of liquid activation medium of 10%; The solvent of liquid activation medium is distilled water, and solute component and concentration thereof are: peptone 8g/L, yeast extract paste 5g/L, glucose 25g/L, sodium-chlor 4g/L, Bromothymol blue solution trace, and the pH value of liquid activation medium is 7.0; The liquid activation medium of inoculation Geobacillus stearothermophilus, under temperature 65 DEG C, shaking speed are 140r/min, cultivates 18h;
(2), by being seeded to through the Geobacillus stearothermophilus of step (1) activation gained be equipped with in fermentor tank that volume ratio is the fermention medium of 60%, inoculum size is 2%; The solvent of fermention medium is distilled water, and solute component and concentration thereof are: peptone 8g/L, yeast extract paste 5g/L, glucose 25g/L, sodium-chlor 4g/L, Bromothymol blue solution trace, and the pH value of fermention medium is 7.1; The fermention medium of inoculation Geobacillus stearothermophilus is under temperature 65 DEG C, mixing speed are 200r/min, enlarged culturing 24h, until the Geobacillus stearothermophilus spore production rate in fermentor tank is more than 80%, Geobacillus stearothermophilus carrier after fermentation is adsorbed, until living bacteria count reaches 5 × 10 9individual/gram, obtain the single bacterium powder of Geobacillus stearothermophilus.
(2), by being seeded to through the Geobacillus stearothermophilus of step (1) activation gained be equipped with in fermentor tank that volume ratio is the fermention medium of 68%, inoculum size is 3%; The solvent of fermention medium is distilled water, and solute component and concentration thereof are: peptone 9g/L, yeast extract paste 8g/L, glucose 18g/L, sodium-chlor 5g/L, Bromothymol blue solution trace, and the pH value of fermention medium is 7.0; The fermention medium of inoculation Geobacillus stearothermophilus is under temperature 58 DEG C, mixing speed are 210r/min, enlarged culturing 36h, until the Geobacillus stearothermophilus spore production rate in fermentor tank is more than 80%, Geobacillus stearothermophilus carrier after fermentation is adsorbed, until living bacteria count reaches 5 × 10 9individual/gram, obtain the single bacterium powder of Geobacillus stearothermophilus.
5. the preparation of microbiobacterial agent
Get and exert than halogen ground anaerobic genus bacillus 30 parts, thermophilic liquefaction genus bacillus 25 parts, hot denitrogenation ground bacillus 40 parts, Geobacillus stearothermophilus 50 parts, the mass fraction of single for above-mentioned each bacterial strain bacterium powder is fully mixed to get microbiobacterial agent.
Embodiment 4
Individual plant cultivation and high-density enlarged culturing is carried out than halogen ground anaerobic genus bacillus, thermophilic liquefaction genus bacillus, hot denitrogenation ground bacillus, Geobacillus stearothermophilus respectively to exerting, finally the single thalline diatomite obtained after cultivation is adsorbed, the single dry bacterium powder of obtained each bacterial strain.
1. exert the preparation of bacterium powder more single than halogen ground anaerobic genus bacillus
(1), exerting on the test tube slant after purified is seeded to than halogen ground anaerobic genus bacillus volume ratio is housed is in the triangular flask of liquid activation medium of 20%; The solvent of liquid activation medium is distilled water, and solute component and concentration thereof are: peptone 10g/L, extractum carnis 4g/L, yeast extract paste 5g/L, Zulkovsky starch 35g/L, sodium-chlor 6g/L, and the pH value of liquid activation medium is 7.0; Inoculation exerts liquid activation medium than halogen ground anaerobic genus bacillus under temperature 60 C, shaking speed are 155r/min, cultivates 20h;
(2), will exerting to be seeded to than halogen ground anaerobic genus bacillus and be equipped with in fermentor tank that volume ratio is the fermention medium of 70% through step (1) activation gained, inoculum size is 2-4%; The solvent of fermention medium is distilled water, and solute component and concentration thereof are: peptone 11g/L, extractum carnis 2g/L, yeast extract paste 4g/L, Zulkovsky starch 15g/L, sodium-chlor 5g/L, and the pH value of fermention medium is 7.0-7.2; Inoculation exert than halogen ground anaerobic genus bacillus fermention medium temperature 55-65 DEG C, under mixing speed is 205r/min, enlarged culturing 20h, until in fermentor tank to exert than halogen ground anaerobic genus bacillus spore production rate be more than 80%, exerting after fermentation is adsorbed, until living bacteria count reaches 5 × 10 than halogen ground anaerobic genus bacillus carrier 9individual/gram, the single bacterium powder than halogen ground anaerobic genus bacillus must be exerted.
2. the preparation of the single bacterium powder of thermophilic liquefaction genus bacillus
(1), the thermophilic liquefaction genus bacillus on the test tube slant after purified is seeded to volume ratio is housed is in the triangular flask of liquid activation medium of 18%; The solvent of liquid activation medium is distilled water, solute component and concentration thereof are: peptone 9g/L, extractum carnis 3g/L, tween 80 28ml/L, N.F,USP MANNITOL 20g/L, yeast extract paste 5g/L, glucose 20g/L, sodium-chlor 5g/L, and the pH value of liquid activation medium is 7.0; The liquid activation medium inoculating thermophilic liquefaction genus bacillus, under temperature 57 DEG C, shaking speed 150r/min, cultivates 21h;
(2), by being seeded to through the thermophilic liquefaction genus bacillus of step (1) activation gained be equipped with in fermentor tank that volume ratio is the fermention medium of 70%, inoculum size is 3%; The solvent of fermention medium is distilled water, and solute component and concentration thereof are: peptone 11g/L, extractum carnis 3g/L, tween 80 30ml/L, N.F,USP MANNITOL 20g/L, yeast extract paste 5g/L, glucose 15g/L, sodium-chlor 6g/L, and the pH value of fermention medium is 7.0; Inoculate the fermention medium of thermophilic liquefaction genus bacillus under temperature 58 DEG C, mixing speed are 210r/min, enlarged culturing 30h, until the thermophilic liquefaction genus bacillus spore production rate in fermentor tank is more than 80%, thermophilic liquefaction genus bacillus carrier after fermentation is adsorbed, until living bacteria count reaches 5 × 10 9individual/gram, obtain the single bacterium powder of thermophilic liquefaction genus bacillus.
3. the preparation of the single bacterium powder of hot denitrogenation ground bacillus
(1), the denitrogenation ground bacillus on the test tube slant after purified is seeded to volume ratio is housed is in the triangular flask of liquid activation medium of 18%; The solvent of liquid activation medium is distilled water, and solute component and concentration thereof are: peptone 8g/L, extractum carnis 3g/L, N.F,USP MANNITOL 15g/L, glucose 23g/L, sodium-chlor 5g/L, and the pH value of liquid activation medium is 7.0; The liquid activation medium of inoculation denitrogenation ground bacillus, under temperature 60 C, shaking speed are 150r/min, cultivates 18h;
(2), by being seeded to through the denitrogenation ground bacillus of step (1) activation gained be equipped with in fermentor tank that volume ratio is the fermention medium of 60%, inoculum size is 3%; The solvent of fermention medium is distilled water, and solute component and concentration thereof are: peptone 8g/L, extractum carnis 2g/L, N.F,USP MANNITOL 15g/L, glucose 15g/L, sodium-chlor 5g/L, and the pH value of fermention medium is 7.0; The fermention medium of inoculation denitrogenation ground bacillus is under temperature 58 DEG C, mixing speed are 210r/min, enlarged culturing 24h, until the denitrogenation ground bacillus spore production rate in fermentor tank is more than 80%, denitrogenation ground bacillus carrier after fermentation is adsorbed, until living bacteria count reaches 5 × 10 9individual/gram, obtain the single bacterium powder of denitrogenation ground bacillus.
4. the preparation of the single bacterium powder of Geobacillus stearothermophilus
(1), the Geobacillus stearothermophilus on the test tube slant after purified is seeded to volume ratio is housed is in the triangular flask of liquid activation medium of 18%; The solvent of liquid activation medium is distilled water, and solute component and concentration thereof are: peptone 9g/L, yeast extract paste 8g/L, glucose 23g/L, sodium-chlor 5g/L, Bromothymol blue solution trace, and the pH value of liquid activation medium is 7.1; The liquid activation medium of inoculation Geobacillus stearothermophilus, under temperature 58 DEG C, shaking speed are 150r/min, cultivates 21h;
5. the preparation of microbiobacterial agent
Get and exert than halogen ground anaerobic genus bacillus 15 parts, thermophilic liquefaction genus bacillus 10 parts, hot denitrogenation ground bacillus 20 parts, Geobacillus stearothermophilus 25 parts, the mass fraction of single for above-mentioned each bacterial strain bacterium powder is fully mixed to get microbiobacterial agent.
Take four kinds of microbiobacterial agents that embodiment 1-4 is obtained, be seeded to respectively in the changing food waste of actual acquisition, observe the effect that microbial inoculum plays in actual applications, measure each index reduction rate of selected changing food waste.
Two, experimental technique
For examination changing food waste: initial water content is 49.24%, Contents of Main Components (in butt) is starch 49.14%, protein 17.51%, fat 22.27%, Mierocrystalline cellulose 1.47%, other 9.61%; Above-mentioned content is mass percent.
Get for examination changing food waste 5 parts, 300 kilograms every part, get the microbiobacterial agent 900g/ kind prepared in example 1-4; A microbial inoculum is corresponding aly puts into the integrated treatment facility of changing food waste together for examination changing food waste, after mixing at 55 DEG C aerobic fermentation 12h; The reduction rate for each component in examination changing food waste is measured, experiment repetition 3 times after fermentation ends.
Three, experimental result
1. adopt the experimental result of embodiment 1 microbiobacterial agent
(1), after measured, examination changing food waste reduction rate is in mass supplied to be 91.75% before and after process;
(2), after measured, for trying, starch reduction rate in naval vessels boats and ships changing food waste is 86.42%, protein reduction rate is 91.23%, fatty reduction rate is 84.96%, Mierocrystalline cellulose reduction rate is 89.57%.
2. adopt the experimental result of embodiment 2 microbiobacterial agent
(1), after measured, examination changing food waste reduction rate is in mass supplied to be 89.37% before and after process;
(2), after measured, for trying, starch reduction rate in changing food waste is 79.20%, protein reduction rate is 89.54%, fatty reduction rate is 80.73%, Mierocrystalline cellulose reduction rate is 97.62%.
3. adopt the experimental result of embodiment 3 microbiobacterial agent
(1), after measured, examination changing food waste reduction rate is in mass supplied to be 90.15% before and after process;
(2), after measured, for trying, starch reduction rate in changing food waste is 83.24%, protein reduction rate is 92.15%, fatty reduction rate is 89.12%, Mierocrystalline cellulose reduction rate is 88.75%.
4. adopt the experimental result of embodiment 4 microbiobacterial agent
(1), after measured, examination changing food waste reduction rate is in mass supplied to be 89.65% before and after process;
(2), after measured, for trying, starch reduction rate in changing food waste is 91.20%, protein reduction rate is 86.79%, fatty reduction rate is 85.46%, Mierocrystalline cellulose reduction rate is 91.02%.
Above for testing the more excellent proportioning of the changing food waste setting provided for this, according to the difference of protein, starch, fat, content of cellulose in changing food waste, the consumption of each component in microbial inoculum can be adjusted targetedly in the application process of reality.
In addition, when utilizing high temperature microbe facture to carry out fermentative processing to changing food waste, the mass ratio of microbiobacterial agent and changing food waste is not limited to above-mentioned citing, as long as in the quality of 1:250-500 than in scope, thermophilic fermentation temperature and aerobic fermentation time are also not limited to above-mentioned citing, as long as control within the scope of 55-65 DEG C, 12-15h.Those skilled in the art can determine mass ratio, the temperature of reaction and fermentation time etc. of microbiobacterial agent and changing food waste flexibly according to actual changing food waste situation.
Certainly; more than illustrate and be only preferred embodiment of the present invention; the present invention is not limited to enumerate above-described embodiment; should be noted that; any those of ordinary skill in the art are under the instruction of this specification sheets; made all equivalently to substitute, obvious variant, within the essential scope all dropping on this specification sheets, protection of the present invention ought to be subject to.

Claims (7)

1. a high temperature degradation changing food waste microbiobacterial agent, it is characterized in that, described microbial strains is composited by the strain raw material of following mass fraction: exert than halogen ground anaerobic genus bacillus 15-30 part, thermophilic liquefaction genus bacillus 10-25 part, hot denitrogenation ground bacillus 20-40 part, Geobacillus stearothermophilus 25-50 part.
2. a preparation method for high temperature degradation changing food waste microbiobacterial agent, is characterized in that, comprises following preparation process:
S1, will exert and carry out individual plant cultivation respectively than halogen ground anaerobic genus bacillus, thermophilic liquefaction genus bacillus, hot denitrogenation ground bacillus, Geobacillus stearothermophilus, then obtained individual plant bacterium colony is carried out activation culture according in the inoculum size access liquid nutrient medium of 10-20%, then volume ratio is housed is ferment in the fermentation equipment of 60-75% substratum by the bacterial classification access after activation;
Adsorbed by gained fermented liquid carrier, obtained living bacteria count is 5 × 10 9individual/gram exert bacterium powder more single than halogen ground anaerobic genus bacillus, thermophilic liquefaction genus bacillus, hot denitrogenation ground bacillus, Geobacillus stearothermophilus; Absorption carrier is diatomite;
S2, obtain and exert than halogen ground anaerobic genus bacillus 15-30 part, thermophilic liquefaction genus bacillus 10-25 part, hot denitrogenation ground bacillus 20-40 part, Geobacillus stearothermophilus 25-50 part, the mass fraction of single for above-mentioned each bacterial strain bacterium powder is fully mixed to get microbiobacterial agent.
3. the preparation method of a kind of high temperature degradation changing food waste microbiobacterial agent according to claim 2, is characterized in that, in described step s1, exerts and than the single bacterium powder preparation process of halogen ground anaerobic genus bacillus is:
S111, exerting on the test tube slant after purified be seeded to than halogen ground anaerobic genus bacillus volume ratio is housed is in the triangular flask of liquid activation medium of 10-20%; The solvent of liquid activation medium is distilled water, and solute component and concentration thereof are: peptone 8-12g/L, extractum carnis 2-4g/L, yeast extract paste 3-5g/L, Zulkovsky starch 15-35g/L, sodium-chlor 4-6g/L, and the pH value of liquid activation medium is 7.0-7.2; Inoculation exert than halogen ground anaerobic genus bacillus liquid activation medium temperature 55-65 DEG C, under shaking speed is 140-160r/min, cultivate 18-24h;
S112, will activate exerting to be seeded to than halogen ground anaerobic genus bacillus and being equipped with in fermentor tank that volume ratio is the fermention medium of 60-75% of gained through step s111, inoculum size is 2-4%; The solvent of fermention medium is distilled water, and solute component and concentration thereof are: peptone 8-12g/L, extractum carnis 2-4g/L, yeast extract paste 3-5g/L, Zulkovsky starch 15-35g/L, sodium-chlor 4-6g/L, and the pH value of fermention medium is 7.0-7.2; Inoculation exert than halogen ground anaerobic genus bacillus fermention medium temperature 55-65 DEG C, under mixing speed is 200-220r/min, enlarged culturing 20-30h, until in fermentor tank to exert than halogen ground anaerobic genus bacillus spore production rate be more than 80%, exerting after fermentation is adsorbed, until living bacteria count reaches 5 × 10 than halogen ground anaerobic genus bacillus carrier 9individual/gram, the single bacterium powder than halogen ground anaerobic genus bacillus must be exerted.
4. the preparation method of a kind of high temperature degradation changing food waste microbiobacterial agent according to claim 2, is characterized in that, in described step s1, the single bacterium powder preparation process of thermophilic liquefaction genus bacillus is:
S121, the thermophilic liquefaction genus bacillus on the test tube slant after purified is seeded to volume ratio is housed is in the triangular flask of liquid activation medium of 10-20%; The solvent of liquid activation medium is distilled water, solute component and concentration thereof are: peptone 8-12g/L, extractum carnis 2-4g/L, tween 80 20-35ml/L, N.F,USP MANNITOL 15-25g/L, yeast extract paste 5-10g/L, glucose 15-25g/L, sodium-chlor 4-6g/L, and the pH value of liquid activation medium is 7.0-7.2; The liquid activation medium inoculating thermophilic liquefaction genus bacillus temperature 55-60 DEG C, under shaking speed 140-160r/min, cultivate 18-24h;
S122, to be seeded to by the thermophilic liquefaction genus bacillus activating gained to be equipped with in fermentor tank that volume ratio is the fermention medium of 60-75% through step s121, inoculum size is 2-4%; The solvent of fermention medium is distilled water, solute component and concentration thereof are: peptone 8-12g/L, extractum carnis 2-4g/L, tween 80 20-35ml/L, N.F,USP MANNITOL 15-25g/L, yeast extract paste 5-10g/L, glucose 15-25g/L, sodium-chlor 4-6g/L, and the pH value of fermention medium is 7.0-7.2; The fermention medium inoculating thermophilic liquefaction genus bacillus temperature 55-62 DEG C, under mixing speed is 200-220r/min, enlarged culturing 24-36h, until the thermophilic liquefaction genus bacillus spore production rate in fermentor tank is more than 80%, thermophilic liquefaction genus bacillus carrier after fermentation is adsorbed, until living bacteria count reaches 5 × 10 9individual/gram, obtain the single bacterium powder of thermophilic liquefaction genus bacillus.
5. the preparation method of a kind of high temperature degradation changing food waste microbiobacterial agent according to claim 2, is characterized in that, in described step s1, the single bacterium powder preparation process of hot denitrogenation ground bacillus is:
S131, the denitrogenation ground bacillus on the test tube slant after purified is seeded to volume ratio is housed is in the triangular flask of liquid activation medium of 10-25%; The solvent of liquid activation medium is distilled water, and solute component and concentration thereof are: peptone 8-12g/L, extractum carnis 2-4g/L, N.F,USP MANNITOL 15-25g/L, glucose 15-25g/L, sodium-chlor 4-6g/L, and the pH value of liquid activation medium is 7.0-7.2; The liquid activation medium of inoculation denitrogenation ground bacillus temperature 55-65 DEG C, under shaking speed is 140-160r/min, cultivate 18-24h;
S132, be seeded to be equipped with activating the denitrogenation ground bacillus of gained through step s131 in fermentor tank that volume ratio is the fermention medium of 60-75%, inoculum size is 2-4%; The solvent of fermention medium is distilled water, and solute component and concentration thereof are: peptone 8-12g/L, extractum carnis 2-4g/L, N.F,USP MANNITOL 15-25g/L, glucose 15-25g/L, sodium-chlor 4-6g/L, and the pH value of fermention medium is 7.0-7.2; The fermention medium of inoculation denitrogenation ground bacillus temperature 55-65 DEG C, under mixing speed is 200-220r/min, enlarged culturing 24-40h, until the denitrogenation ground bacillus spore production rate in fermentor tank is more than 80%, denitrogenation ground bacillus carrier after fermentation is adsorbed, until living bacteria count reaches 5 × 10 9individual/gram, obtain the single bacterium powder of denitrogenation ground bacillus.
6. the preparation method of a kind of high temperature degradation changing food waste microbiobacterial agent according to claim 2, is characterized in that, in described step s1, the single bacterium powder preparation process of Geobacillus stearothermophilus is:
S141, the Geobacillus stearothermophilus on the test tube slant after purified is seeded to volume ratio is housed is in the triangular flask of liquid activation medium of 10-20%; The solvent of liquid activation medium is distilled water, solute component and concentration thereof are: peptone 8-12g/L, yeast extract paste 5-10g/L, glucose 15-25g/L, sodium-chlor 4-6g/L, Bromothymol blue solution trace, and the pH value of liquid activation medium is 7.0-7.2; The liquid activation medium of inoculation Geobacillus stearothermophilus temperature 55-65 DEG C, under shaking speed is 140-160r/min, cultivate 18-24h;
S142, be seeded to be equipped with activating the Geobacillus stearothermophilus of gained through step s141 in fermentor tank that volume ratio is the fermention medium of 60-75%, inoculum size is 2-4%; The solvent of fermention medium is distilled water, and solute component and concentration thereof are: peptone 8-12g/L, yeast extract paste 5-10g/L, glucose 15-25g/L, sodium-chlor 4-6g/L, Bromothymol blue solution trace, and the pH value of fermention medium is 7.0-7.2; The fermention medium of inoculation Geobacillus stearothermophilus temperature 55-65 DEG C, under mixing speed is 200-220r/min, enlarged culturing 24-40h, until the Geobacillus stearothermophilus spore production rate in fermentor tank is more than 80%, Geobacillus stearothermophilus carrier after fermentation is adsorbed, until living bacteria count reaches 5 × 10 9individual/gram, obtain the single bacterium powder of Geobacillus stearothermophilus.
7. the using method of a high temperature degradation changing food waste microbiobacterial agent, adopt high temperature degradation changing food waste microbiobacterial agent as claimed in claim 1, it is characterized in that, microbiobacterial agent is fully mixed according to the ratio that mass ratio is 1:250-500 with changing food waste, at 55-65 DEG C, aerobic fermentation 12-15h.
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Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106167743A (en) * 2016-06-30 2016-11-30 山东胜伟园林科技有限公司 A kind of containing exerting than the dredging agent of halogen ground anaerobic bacillus cereus and the application in salt discharge hidden pipe thereof
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CN107325991A (en) * 2017-08-28 2017-11-07 广州惜福生态科技有限公司 Composite bacteria agent of degraded kitchen garbage and preparation method thereof and the plastics and the clean method of foam class waste polluted by kitchen garbage
CN109734486A (en) * 2019-02-15 2019-05-10 陕西天仁雪农业科技有限公司 A kind of kitchen garbage devil liquor recovery utilizes processing method
CN111014252A (en) * 2019-12-26 2020-04-17 上海申旺生态科技有限责任公司 High-temperature garbage degradation treatment method based on microbial flora
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Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
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
CN102911869A (en) * 2012-10-25 2013-02-06 王欢 Microorganism mixed culture for degrading kitchen wastes, method for producing microorganism mixed culture for degrading kitchen wastes and method for degrading wastes through utilizing culture
CN103272361A (en) * 2013-05-15 2013-09-04 钱臻 Active biological complexing agent for degradation and digestion of organic wet garbage and preparation method of active biological complexing agent
CN103468616A (en) * 2013-09-23 2013-12-25 青岛蔚蓝生物集团有限公司 Microbial agent capable of degrading garbage

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
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
CN102911869A (en) * 2012-10-25 2013-02-06 王欢 Microorganism mixed culture for degrading kitchen wastes, method for producing microorganism mixed culture for degrading kitchen wastes and method for degrading wastes through utilizing culture
CN103272361A (en) * 2013-05-15 2013-09-04 钱臻 Active biological complexing agent for degradation and digestion of organic wet garbage and preparation method of active biological complexing agent
CN103468616A (en) * 2013-09-23 2013-12-25 青岛蔚蓝生物集团有限公司 Microbial agent capable of degrading garbage

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CN106167743A (en) * 2016-06-30 2016-11-30 山东胜伟园林科技有限公司 A kind of containing exerting than the dredging agent of halogen ground anaerobic bacillus cereus and the application in salt discharge hidden pipe thereof
CN106986694A (en) * 2017-04-18 2017-07-28 奥为(天津)环保科技有限公司 A kind of preparation method containing high concentration potassium solubilizing bacteria organic fertilizer
CN107032836A (en) * 2017-04-18 2017-08-11 奥为(天津)环保科技有限公司 A kind of preparation method containing high concentration phosphate solubilizing bacteria organic fertilizer
CN107325991A (en) * 2017-08-28 2017-11-07 广州惜福生态科技有限公司 Composite bacteria agent of degraded kitchen garbage and preparation method thereof and the plastics and the clean method of foam class waste polluted by kitchen garbage
CN109734486A (en) * 2019-02-15 2019-05-10 陕西天仁雪农业科技有限公司 A kind of kitchen garbage devil liquor recovery utilizes processing method
CN111014252A (en) * 2019-12-26 2020-04-17 上海申旺生态科技有限责任公司 High-temperature garbage degradation treatment method based on microbial flora
CN112175875A (en) * 2020-10-13 2021-01-05 蛋壳城矿环保科技发展(广州)有限公司 Preparation method and application of ultrahigh-temperature aerobic composite biological agent
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
CN113800961A (en) * 2021-09-17 2021-12-17 杭州五蕴环保科技有限公司 Kitchen microbial agent prepared from waste edible fungus sticks and preparation method and application thereof

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