CN111979158A - Compound microbial inoculum for food waste compost as well as preparation method and application thereof - Google Patents

Compound microbial inoculum for food waste compost as well as preparation method and application thereof Download PDF

Info

Publication number
CN111979158A
CN111979158A CN202010913510.3A CN202010913510A CN111979158A CN 111979158 A CN111979158 A CN 111979158A CN 202010913510 A CN202010913510 A CN 202010913510A CN 111979158 A CN111979158 A CN 111979158A
Authority
CN
China
Prior art keywords
liquid
seed
bacillus licheniformis
streptococcus thermophilus
paracoccus
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN202010913510.3A
Other languages
Chinese (zh)
Inventor
符春华
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Guangzhou Xiyi Dining Degraded Equipment Co ltd
Original Assignee
Guangzhou Xiyi Dining Degraded Equipment Co ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Guangzhou Xiyi Dining Degraded Equipment Co ltd filed Critical Guangzhou Xiyi Dining Degraded Equipment Co ltd
Priority to CN202010913510.3A priority Critical patent/CN111979158A/en
Publication of CN111979158A publication Critical patent/CN111979158A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • 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
    • C12N1/20Bacteria; Culture media therefor
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F17/00Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
    • C05F17/20Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation using specific microorganisms or substances, e.g. enzymes, for activating or stimulating the treatment
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F17/00Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
    • C05F17/80Separation, elimination or disposal of harmful substances during the treatment
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F9/00Fertilisers from household or town refuse
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F9/00Fertilisers from household or town refuse
    • C05F9/04Biological compost
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

Landscapes

  • Chemical & Material Sciences (AREA)
  • Health & Medical Sciences (AREA)
  • Organic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Biotechnology (AREA)
  • Microbiology (AREA)
  • Biochemistry (AREA)
  • Molecular Biology (AREA)
  • Wood Science & Technology (AREA)
  • Genetics & Genomics (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Zoology (AREA)
  • General Chemical & Material Sciences (AREA)
  • Tropical Medicine & Parasitology (AREA)
  • Bioinformatics & Cheminformatics (AREA)
  • Medicinal Chemistry (AREA)
  • Biomedical Technology (AREA)
  • Virology (AREA)
  • Toxicology (AREA)
  • General Engineering & Computer Science (AREA)
  • General Health & Medical Sciences (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Fertilizers (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The invention belongs to the technical field of environmental protection, and particularly relates to a compound microbial inoculum for food waste compost, and a preparation method and application thereof. The invention relates to a food waste compost compound microbial inoculum, which comprises the following components: the fermentation liquid of the bacillus licheniformis with a bacterium OD value of 0.3-0.9, the fermentation liquid of the paracoccus calorifaciens with a bacterium OD value of 0.3-0.9, the fermentation liquid of the streptococcus thermophilus with a bacterium OD value of 0.3-0.9 and the fermentation liquid of the pseudomonas alcaligenes with a bacterium OD value of 0.3-0.9. According to the invention, the bacillus licheniformis, the paracoccus mutilans, the streptococcus thermophilus and the pseudomonas alcaligenes are prepared into the compound microbial inoculum, so that the composting speed of the food wastes is greatly improved, the emission of malodor in the storage process is reduced, and the environment benefit is good.

Description

Compound microbial inoculum for food waste compost as well as preparation method and application thereof
Technical Field
The invention belongs to the technical field of environmental protection, and particularly relates to a compound microbial inoculum for food waste compost, and a preparation method and application thereof.
Background
The food waste has similar components with the kitchen waste, but has higher water content, nutrient components and grease components. On the one hand, the high water content characteristic of the food waste influences the normal operation of the existing household garbage transportation and transfer system, sanitary landfill system and household garbage incineration treatment system, the high oil content characteristic of the food waste also influences the normal operation of the leachate of the household garbage sanitary landfill system and the guide and discharge system of landfill gas, the existing household garbage treatment system lacks targeted solution measures for the inadaptability of the food waste characteristic, great pressure is caused to municipal household garbage treatment facilities, and the collection rate and the treatment rate of the food waste are low. On the other hand, the characteristics of high grease and high nutrient content of the food waste lead the non-standard treatment to be favorable.
At present, the food waste is degraded by adopting a composting method, so that the food waste is treated more thoroughly and resources are recycled. The composting refers to a technical method that under the conditions of certain temperature, humidity and pH, microorganisms decompose and oxidize organic solid wastes and automatically generate heat to kill pathogenic bacteria and grass seeds in raw materials to form a highly stable and humified fertilizer, so that the organic solid wastes are recycled and innoxious.
Composting is essentially a process of microbial action and therefore research on composting microbial agents is critical. At present, composting microbial inoculum applied to livestock and poultry manure (CN110184211A), composting microbial inoculum applied to straws (CN110699289A), composting microbial inoculum applied to municipal sludge (CN107032574A) and the like exist. For example, chinese patent CN106187335A discloses a composite microbial agent prepared from bacillus subtilis, bacillus coagulans or/and bacillus licheniformis for removing grease from kitchen waste.
Disclosure of Invention
The invention aims to provide a compound microbial inoculum for food waste compost as well as a preparation method and application thereof.
In order to achieve the purpose, the invention adopts the following technical scheme:
a compound microbial inoculum for food residue compost comprises the following components: the bacillus licheniformis fermentation liquor with the bacterial OD value of 0.3-0.9, the paracoccus calorigens fermentation liquor with the bacterial OD value of 0.3-0.9, the streptococcus thermophilus fermentation liquor with the bacterial OD value of 0.3-0.9 and the pseudomonas alcaligenes fermentation liquor with the bacterial OD value of 0.3-0.9. Bacillus licheniformis, Paracoccus calorigens, Streptococcus thermophilus and Pseudomonadaceae are all purchased from Guangdong province culture Collection and are numbered as GIM1.863, GIM1.487, GIM1.1808 and GIM 1.687.
The invention provides a preparation method of a complex microbial inoculum for food waste compost, which comprises the following steps:
s1) respectively preparing a bacillus licheniformis seed solution, a colleague paracoccus seed solution, a streptococcus thermophilus seed solution and an alcaligenes pseudomonad seed solution;
A. preparing a bacillus licheniformis seed solution: inoculating bacillus licheniformis to an LB liquid culture medium, and carrying out pure culture for 12-24 h at the temperature of 35-50 ℃ and the rotation speed of 120-160 rpm to obtain the bacillus licheniformis;
B. preparation of a strain paracoccus seed solution: inoculating the paracoccus benevolens to an LB liquid culture medium, and carrying out pure culture at the temperature of 35-50 ℃ and the rotation speed of 120-160 rpm for 12-24 h to obtain the paracoccus benevolens;
C. preparation of streptococcus thermophilus seed liquid: inoculating streptococcus thermophilus to an LB liquid culture medium, and carrying out pure culture for 12-24 h at the temperature of 35-50 ℃ and the rotation speed of 120-160 rpm to obtain streptococcus thermophilus;
D. preparing an alcaligenes pseudomonad seed solution: inoculating pseudomonas alcaligenes to an LB liquid culture medium, and carrying out pure culture for 12-24 h at the temperature of 35-50 ℃ and the rotating speed of 120-160 rpm to obtain the pseudomonas alcaligenes;
s2) respectively carrying out amplification culture on the Bacillus licheniformis seed liquid, the paragonium calophyllum seed liquid, the Streptococcus thermophilus seed liquid and the Pseudomonas alcaligenes seed liquid obtained in the step S1 to obtain a Bacillus licheniformis fermentation liquid, a paragonium calophyllum fermentation liquid, a Streptococcus thermophilus fermentation liquid and a Pseudomonas alcaligenes fermentation liquid;
A. preparing a bacillus licheniformis fermentation liquor; transferring the bacillus licheniformis seed liquid into a reactor filled with an LB liquid expanding culture medium, wherein the temperature is 35-50 ℃, and the aeration intensity is 25-75L/min to obtain the bacillus licheniformis seed liquid;
B. preparing a zymotic fluid of the ameliopsis paracoccus; transferring the paracoccus benevoleus seed liquid into a reactor filled with an LB liquid amplification culture medium, wherein the temperature is 35-50 ℃, and the aeration intensity is 25-75L/min to obtain the paracoccus benevoleus seed liquid;
C. preparing streptococcus thermophilus fermentation liquor; transferring the streptococcus thermophilus seed liquid into a reactor filled with an LB liquid amplification culture medium, wherein the temperature is 35-50 ℃, and the aeration intensity is 25-75L/min to obtain the streptococcus thermophilus seed liquid;
D. preparing fermentation liquor of pseudomonas alcaligenes: and (3) transferring the pseudomonas alcaligenes seed liquid into a reactor filled with an LB liquid expanding culture medium, wherein the temperature is 35-50 ℃, and the aeration intensity is 25-75L/min.
S3), mixing the fermentation liquor of the bacillus licheniformis, the fermentation liquor of the paracoccus mutilans, the fermentation liquor of the streptococcus thermophilus and the fermentation liquor of the pseudomonas alcaligenes in the step S2 according to the volume ratio of 1: 1: 1: 1, mixing to obtain the compound microbial inoculum.
Preferably, the LB liquid medium comprises the following components: 10-30 g/L of peptone, 5-8 g/L of yeast extract, 10-15 g/L of NaCl and 800-1000 mL of tap water.
Preferably, the LB liquid culture medium comprises the following components: 160-300 g/L of peptone, 80-100 g/L of yeast extract, 150-180 g/L of NaCl and 14-16L of tap water.
The invention also provides an application of the complex microbial inoculum for the food waste compost, which comprises the following steps:
(1) manually sorting the food waste by a conveyor belt to remove impurities such as disposable appliances, plastics, paper towels, metal objects and the like to obtain the treated food waste;
(2) squeezing and dewatering the treated food waste obtained in the step (1) to reduce the water content of the treated food waste to 50-90% to obtain compost substrate;
(3) and (3) conveying the compost substrate obtained in the step (2) to a compost box, adding a compound microbial inoculum with the mass ratio of the compost substrate being 0.01-1%, mixing and fermenting to obtain the compost.
Compared with the prior art, the invention has the following beneficial effects:
according to the invention, the bacillus licheniformis, the paracoccus mutilans, the streptococcus thermophilus and the pseudomonas alcaligenes are prepared into the compound microbial inoculum, the compound microbial inoculum is used for improving the composting speed and the decomposition degree of the food waste, and simultaneously the problem of malodor in the storage process of the food waste is solved, and the method is simple and efficient and has good environmental benefits.
Detailed Description
The present invention will be described in further detail with reference to the following examples. It should not be understood that the scope of the above-described subject matter of the present invention is limited to the following examples.
Example 1
A compound microbial inoculum for food residue compost comprises the following components: a bacillus licheniformis fermentation broth with a bacterial OD value of 0.4, a colleague paracoccus fermentation broth with a bacterial OD value of 0.4, a streptococcus thermophilus fermentation broth with a bacterial OD value of 0.8 and an alcaligenes pseudomonads fermentation broth with a bacterial OD value of 0.8.
The preparation method of the complex microbial inoculum for the food waste compost comprises the following steps:
s1) respectively preparing a bacillus licheniformis seed solution, a colleague paracoccus seed solution, a streptococcus thermophilus seed solution and an alcaligenes pseudomonad seed solution;
A. preparing a bacillus licheniformis seed solution: inoculating Bacillus licheniformis into an LB liquid culture medium, and carrying out pure culture for 12h at the temperature of 35 ℃ and the rotation speed of 120 rpm;
B. preparation of a strain paracoccus seed solution: inoculating paracoccus benomycini to an LB liquid culture medium, and carrying out pure culture at the temperature of 35 ℃ and the rotation speed of 120rpm for 12h to obtain the paracoccus benomycini extract;
C. preparation of streptococcus thermophilus seed liquid: inoculating streptococcus thermophilus into an LB liquid culture medium, and carrying out pure culture for 12h at the temperature of 35 ℃ and the rotation speed of 120 rpm;
D. preparing an alcaligenes pseudomonad seed solution: inoculating pseudomonas alcaligenes to an LB liquid culture medium, and carrying out pure culture for 12h at the temperature of 40 ℃ and the rotating speed of 120rpm to obtain the pseudomonas alcaligenes;
s2) respectively carrying out amplification culture on the Bacillus licheniformis seed liquid, the paragonium calophyllum seed liquid, the Streptococcus thermophilus seed liquid and the Pseudomonas alcaligenes seed liquid obtained in the step S1 to obtain a Bacillus licheniformis fermentation liquid, a paragonium calophyllum fermentation liquid, a Streptococcus thermophilus fermentation liquid and a Pseudomonas alcaligenes fermentation liquid;
A. preparing a bacillus licheniformis fermentation liquor; transferring the Bacillus licheniformis seed liquid into a reactor filled with LB liquid propagation culture medium, and aerating at 35 deg.C and aeration intensity of 35L/min;
B. preparing a zymotic fluid of the ameliopsis paracoccus; transferring the paracoccus benevoleus seed liquid into a reactor filled with an LB liquid amplification culture medium, wherein the temperature is 35 ℃, and the aeration intensity is 35L/min to obtain the paracoccus benevolens seed liquid;
C. preparing streptococcus thermophilus fermentation liquor; transferring the streptococcus thermophilus seed liquid into a reactor filled with an LB liquid amplification culture medium, wherein the temperature is 35 ℃, and the aeration intensity is 35L/min to obtain the streptococcus thermophilus seed liquid;
D. preparing fermentation liquor of pseudomonas alcaligenes: transferring the pseudomonas alcaligenes seed liquid into a reactor filled with LB liquid expanding culture medium, wherein the temperature is 35 ℃, and the aeration intensity is 35L/min.
S3), mixing the fermentation liquor of the bacillus licheniformis, the fermentation liquor of the paracoccus mutilans, the fermentation liquor of the streptococcus thermophilus and the fermentation liquor of the pseudomonas alcaligenes in the step S2 according to the volume ratio of 1: 1: 1: 1, mixing to obtain the compound microbial inoculum.
Wherein, the LB liquid culture medium comprises the following components: 10g/L of peptone, 5g/L of yeast extract, 10g/L of NaCl and 1000mL of tap water; the LB liquid expanding culture medium comprises the following components: 160g/L of peptone, 80g/L of yeast extract, 150g/L of NaCl and 14L of tap water.
The application of the complex microbial inoculum for the food waste compost comprises the following steps:
(1) manually sorting the food waste by a conveyor belt to remove impurities such as disposable appliances, plastics, paper towels, metal objects and the like to obtain the treated food waste;
(2) squeezing and dewatering the treated food waste obtained in the step (1) to reduce the water content of the treated food waste to 90% to obtain compost substrate;
(3) and (3) conveying the compost substrate obtained in the step (2) to a compost box, adding a compound microbial inoculum with the mass ratio of the compost substrate being 0.1%, mixing and fermenting to obtain the fertilizer.
Example 2
A compound microbial inoculum for food residue compost comprises the following components: a bacillus licheniformis fermentation broth with a bacterial OD value of 0.4, a colleague paracoccus fermentation broth with a bacterial OD value of 0.6, a streptococcus thermophilus fermentation broth with a bacterial OD value of 0.7 and an alcaligenes pseudomonads fermentation broth with a bacterial OD value of 0.7.
The preparation method of the complex microbial inoculum for the food waste compost comprises the following steps:
s1) respectively preparing a bacillus licheniformis seed solution, a colleague paracoccus seed solution, a streptococcus thermophilus seed solution and an alcaligenes pseudomonad seed solution;
A. preparing a bacillus licheniformis seed solution: inoculating Bacillus licheniformis into an LB liquid culture medium, and carrying out pure culture for 12h at 40 ℃ and a rotation speed of 120 rpm;
B. preparation of a strain paracoccus seed solution: inoculating paracoccus benomycini to an LB liquid culture medium, and carrying out pure culture at the temperature of 40 ℃ and the rotation speed of 120rpm for 12h to obtain the paracoccus benomycini extract;
C. preparation of streptococcus thermophilus seed liquid: inoculating streptococcus thermophilus into an LB liquid culture medium, and carrying out pure culture for 12h at the temperature of 40 ℃ and the rotation speed of 120 rpm;
D. preparing an alcaligenes pseudomonad seed solution: inoculating pseudomonas alcaligenes to an LB liquid culture medium, and carrying out pure culture for 12h at the temperature of 40 ℃ and the rotating speed of 120rpm to obtain the pseudomonas alcaligenes;
s2) respectively carrying out amplification culture on the Bacillus licheniformis seed liquid, the paragonium calophyllum seed liquid, the Streptococcus thermophilus seed liquid and the Pseudomonas alcaligenes seed liquid obtained in the step S1 to obtain a Bacillus licheniformis fermentation liquid, a paragonium calophyllum fermentation liquid, a Streptococcus thermophilus fermentation liquid and a Pseudomonas alcaligenes fermentation liquid;
A. preparing a bacillus licheniformis fermentation liquor; transferring the Bacillus licheniformis seed liquid into a reactor filled with LB liquid propagation culture medium, and aerating at 35 deg.C and 50L/min;
B. preparing a zymotic fluid of the ameliopsis paracoccus; transferring the paracoccus benevoleus seed liquid into a reactor filled with an LB liquid amplification culture medium, wherein the temperature is 35 ℃, and the aeration intensity is 50L/min to obtain the paracoccus benevolens seed liquid;
C. preparing streptococcus thermophilus fermentation liquor; transferring the streptococcus thermophilus seed liquid into a reactor filled with an LB liquid amplification culture medium, wherein the temperature is 35 ℃, and the aeration intensity is 50L/min to obtain the streptococcus thermophilus seed liquid;
D. preparing fermentation liquor of pseudomonas alcaligenes: transferring the pseudomonas alcaligenes seed liquid into a reactor filled with LB liquid expanding culture medium, wherein the temperature is 35 ℃, and the aeration intensity is 50L/min.
S3), mixing the fermentation liquor of the bacillus licheniformis, the fermentation liquor of the paracoccus mutilans, the fermentation liquor of the streptococcus thermophilus and the fermentation liquor of the pseudomonas alcaligenes in the step S2 according to the volume ratio of 1: 1: 1: 1, mixing to obtain the compound microbial inoculum.
Wherein, the LB liquid culture medium comprises the following components: 10g/L of peptone, 8g/L of yeast extract, 15g/L of NaCl and 1000mL of tap water; the LB liquid expanding culture medium comprises the following components: 200g/L of peptone, 100g/L of yeast extract, 1180g/L of NaCl and 15L of tap water.
The application of the complex microbial inoculum for the food waste compost comprises the following steps:
(1) manually sorting the food waste by a conveyor belt to remove impurities such as disposable appliances, plastics, paper towels, metal objects and the like to obtain the treated food waste;
(2) squeezing and dewatering the treated food waste obtained in the step (1) to reduce the water content of the treated food waste to 90% to obtain compost substrate;
(3) and (3) conveying the compost substrate obtained in the step (2) to a compost box, adding a compound microbial inoculum with the mass ratio of the compost substrate being 0.1%, mixing and fermenting to obtain the fertilizer.
Example 3
A compound microbial inoculum for food residue compost comprises the following components: a bacillus licheniformis fermentation broth with a bacterial OD value of 0.8, a paracoccus lancinae fermentation broth with a bacterial OD value of 0.3, a streptococcus thermophilus fermentation broth with a bacterial OD value of 0.7, and an alcaligenes pseudomonad fermentation broth with a bacterial OD value of 0.6.
The preparation method of the complex microbial inoculum for the food waste compost comprises the following steps:
s1) respectively preparing a bacillus licheniformis seed solution, a colleague paracoccus seed solution, a streptococcus thermophilus seed solution and an alcaligenes pseudomonad seed solution;
A. preparing a bacillus licheniformis seed solution: inoculating Bacillus licheniformis into an LB liquid culture medium, and carrying out pure culture for 17h at 40 ℃ and 140 rpm;
B. preparation of a strain paracoccus seed solution: inoculating the paracoccus benevolens to an LB liquid culture medium, and carrying out pure culture for 17h at the temperature of 40 ℃ and the rotation speed of 140rpm to obtain the paracoccus benevolens;
C. preparation of streptococcus thermophilus seed liquid: inoculating streptococcus thermophilus to an LB liquid culture medium, and carrying out pure culture for 17h at the temperature of 35 ℃ and the rotation speed of 140 rpm;
D. preparing an alcaligenes pseudomonad seed solution: inoculating the pseudomonas alcaligenes to an LB liquid culture medium, and carrying out pure culture for 17h at the temperature of 40 ℃ and the rotating speed of 140 rpm;
s2) respectively carrying out amplification culture on the Bacillus licheniformis seed liquid, the paragonium calophyllum seed liquid, the Streptococcus thermophilus seed liquid and the Pseudomonas alcaligenes seed liquid obtained in the step S1 to obtain a Bacillus licheniformis fermentation liquid, a paragonium calophyllum fermentation liquid, a Streptococcus thermophilus fermentation liquid and a Pseudomonas alcaligenes fermentation liquid;
A. preparing a bacillus licheniformis fermentation liquor; transferring the Bacillus licheniformis seed liquid into a reactor filled with LB liquid propagation culture medium, and aerating at 40 deg.C and aeration intensity of 35L/min;
B. preparing a zymotic fluid of the ameliopsis paracoccus; transferring the paracoccus benevoleus seed liquid into a reactor filled with an LB liquid amplification culture medium, and carrying out aeration at 40 ℃ and 35L/min to obtain the paracoccus benevolens seed liquid;
C. preparing streptococcus thermophilus fermentation liquor; transferring the streptococcus thermophilus seed liquid into a reactor filled with an LB liquid amplification culture medium, wherein the temperature is 35 ℃, and the aeration intensity is 35L/min to obtain the streptococcus thermophilus seed liquid;
D. preparing fermentation liquor of pseudomonas alcaligenes: transferring the pseudomonas alcaligenes seed liquid into a reactor filled with LB liquid expanding culture medium, and carrying out aeration at 40 ℃ and 30L/min to obtain the pseudomonas alcaligenes seed liquid.
S3), mixing the fermentation liquor of the bacillus licheniformis, the fermentation liquor of the paracoccus mutilans, the fermentation liquor of the streptococcus thermophilus and the fermentation liquor of the pseudomonas alcaligenes in the step S2 according to the volume ratio of 1: 1: 1: 1, mixing to obtain the compound microbial inoculum.
Wherein, the LB liquid culture medium comprises the following components: peptone 20g/L, yeast extract 8g/L, NaCl 15g/L, tap water 1000 mL; the LB liquid expanding culture medium comprises the following components: 300g/L of peptone, 100g/L of yeast extract, 170g/L of NaCl and 15L of tap water.
The application of the complex microbial inoculum for the food waste compost comprises the following steps:
(1) manually sorting the food waste by a conveyor belt to remove impurities such as disposable appliances, plastics, paper towels, metal objects and the like to obtain the treated food waste;
(2) squeezing and dewatering the treated food waste obtained in the step (1) to reduce the water content of the treated food waste to 90% to obtain compost substrate;
(3) and (3) conveying the compost substrate obtained in the step (2) to a compost box, adding a compound microbial inoculum with the mass ratio of the compost substrate being 0.1%, mixing and fermenting to obtain the fertilizer.
Comparative example 1
Similar to example 1, the difference is that the L.carnosus fermentation broth is not added, and the total addition of the complex microbial inoculum is kept unchanged.
Comparative example 2
Similar to example 1, except that no Pseudomonas alcaligenes fermentation broth was added, the total amount of the compounded microbial inoculum was kept constant.
Experiment I, determination of maturity
1.1 subjects: examples/comparative examples/commercial complex inocula.
1.2 Experimental methods: the change degree of the organic matter content reflects the important indexes of the composting quality and the process, and the total amount of the organic matter is burned for 8 hours at 550 ℃.
TABLE 1
Figure BDA0002664198230000081
Figure BDA0002664198230000091
As can be seen from Table 1, the treatment effect of the complex microbial inoculum of the invention is better than that of the commercial complex microbial inoculum along with the increase of time.
Second experiment, odor measurement
1.1 subjects: examples/comparative examples/commercial complex inocula.
1.2 Experimental methods: gas generated in the process of degrading the food wastes is judged through smell sense, 5 persons in each group are scored, and the average value and the standard deviation are calculated.
And (4) judging the standard:
and (4) judging the standard:
90< X.ltoreq.100: without bad smell
80< X < 90: the smell is weak, and the strength and the type of the gas cannot be distinguished
70< X is less than or equal to 80: can judge which smell
60< X is less than or equal to 70: obviously smells the smell
50< X < 60: strong smell
X < 50: strong smell, unacceptable
TABLE 2
Figure BDA0002664198230000092
Figure BDA0002664198230000101
The foregoing embodiments are merely illustrative of the principles and utilities of the present invention and are not intended to limit the invention. Any person skilled in the art can modify or change the above-mentioned embodiments without departing from the spirit and scope of the present invention. Accordingly, it is intended that all equivalent modifications or changes be made by those skilled in the art without departing from the spirit and technical spirit of the present invention, and be covered by the appended claims.

Claims (5)

1. A compound microbial inoculum for food residue compost is characterized by comprising the following components: the fermentation liquid of the bacillus licheniformis with a bacterium OD value of 0.3-0.9, the fermentation liquid of the paracoccus calorifaciens with a bacterium OD value of 0.3-0.9, the fermentation liquid of the streptococcus thermophilus with a bacterium OD value of 0.3-0.9 and the fermentation liquid of the pseudomonas alcaligenes with a bacterium OD value of 0.3-0.9.
2. The preparation method of the food waste compost microbial inoculum according to claim 1, which is characterized by comprising the following steps:
s1) respectively preparing a bacillus licheniformis seed solution, a colleague paracoccus seed solution, a streptococcus thermophilus seed solution and an alcaligenes pseudomonad seed solution;
A. preparing a bacillus licheniformis seed solution: inoculating bacillus licheniformis to an LB liquid culture medium, and carrying out pure culture for 12-24 h at the temperature of 35-50 ℃ and the rotation speed of 120-160 rpm to obtain the bacillus licheniformis;
B. preparation of a strain paracoccus seed solution: inoculating the paracoccus benevolens to an LB liquid culture medium, and carrying out pure culture for 12-24 h at the temperature of 35-50 ℃ and the rotating speed of 120-160 rpm to obtain the paracoccus benevolens;
C. preparation of streptococcus thermophilus seed liquid: inoculating streptococcus thermophilus to an LB liquid culture medium, and carrying out pure culture for 12-24 h at the temperature of 35-50 ℃ and the rotating speed of 120-160 rpm to obtain streptococcus thermophilus;
D. preparing an alcaligenes pseudomonad seed solution: inoculating pseudomonas alcaligenes to an LB liquid culture medium, and carrying out pure culture for 12-24 h at the temperature of 35-50 ℃ and the rotating speed of 120-160 rpm to obtain the pseudomonas alcaligenes;
s2) respectively carrying out amplification culture on the Bacillus licheniformis seed liquid, the paragonium calophyllum seed liquid, the Streptococcus thermophilus seed liquid and the Pseudomonas alcaligenes seed liquid obtained in the step S1 to obtain a Bacillus licheniformis fermentation liquid, a paragonium calophyllum fermentation liquid, a Streptococcus thermophilus fermentation liquid and a Pseudomonas alcaligenes fermentation liquid;
A. preparing a bacillus licheniformis fermentation liquor; transferring the bacillus licheniformis seed liquid into a reactor filled with an LB liquid expanding culture medium, wherein the temperature is 35-50 ℃, and the aeration intensity is 25-75L/min to obtain the bacillus licheniformis seed liquid;
B. preparing a zymotic fluid of the ameliopsis paracoccus; transferring the paracoccus benevoleus seed liquid into a reactor filled with an LB liquid culture medium for amplification, wherein the temperature is 35-50 ℃, and the aeration intensity is 25-75L/min to obtain the paracoccus benevoleus seed liquid;
C. preparing streptococcus thermophilus fermentation liquor; transferring the streptococcus thermophilus seed liquid into a reactor filled with an LB liquid expanding culture medium, wherein the temperature is 35-50 ℃, and the aeration intensity is 25-75L/min to obtain the streptococcus thermophilus seed liquid;
D. preparing fermentation liquor of pseudomonas alcaligenes: and (3) transferring the pseudomonas alcaligenes seed liquid into a reactor filled with an LB liquid expanding culture medium, wherein the temperature is 35-50 ℃, and the aeration intensity is 25-75L/min.
S3), mixing the fermentation liquor of the bacillus licheniformis, the fermentation liquor of the paramylococcus benomyelii, the fermentation liquor of the streptococcus thermophilus and the fermentation liquor of the pseudomonas alcaligenes in the step S2 according to the volume ratio of 1: 1: 1: 1, mixing to obtain the compound microbial inoculum.
3. The preparation method of the food waste compost complex microbial inoculum according to claim 2, wherein the LB liquid culture medium comprises the following components: 10-30 g/L of peptone, 5-8 g/L of yeast extract, 10-15 g/L of NaCl and 800-1000 mL of tap water.
4. The preparation method of the complex microbial inoculum for food residue compost as claimed in claim 2, wherein the LB liquid culture medium comprises the following components: 160-300 g/L of peptone, 80-100 g/L of yeast extract, 150-180 g/L of NaCl and 14-16L of tap water.
5. The application of the complex microbial inoculum for food waste compost according to any one of claims 1 to 4, which is characterized by comprising the following steps:
(1) manually sorting the food waste by a conveyor belt to remove impurities such as disposable appliances, plastics, paper towels, metal objects and the like to obtain the treated food waste;
(2) squeezing and dewatering the treated food waste obtained in the step (1) to reduce the water content of the treated food waste to 50-90% to obtain compost substrate;
(3) and (3) conveying the compost substrate obtained in the step (2) to a compost box, adding a compound microbial inoculum with the mass ratio of the compost substrate being 0.01-1%, mixing and fermenting to obtain the compost.
CN202010913510.3A 2020-09-03 2020-09-03 Compound microbial inoculum for food waste compost as well as preparation method and application thereof Pending CN111979158A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202010913510.3A CN111979158A (en) 2020-09-03 2020-09-03 Compound microbial inoculum for food waste compost as well as preparation method and application thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202010913510.3A CN111979158A (en) 2020-09-03 2020-09-03 Compound microbial inoculum for food waste compost as well as preparation method and application thereof

Publications (1)

Publication Number Publication Date
CN111979158A true CN111979158A (en) 2020-11-24

Family

ID=73448409

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202010913510.3A Pending CN111979158A (en) 2020-09-03 2020-09-03 Compound microbial inoculum for food waste compost as well as preparation method and application thereof

Country Status (1)

Country Link
CN (1) CN111979158A (en)

Citations (8)

* 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
CN102985392A (en) * 2010-03-23 2013-03-20 比奥麦克斯私人控股有限公司 Treatment of organic waste
CN103103147A (en) * 2012-07-18 2013-05-15 大连理工大学 Mercurial paracoccus strain simultaneously having denitrification and iron reduction functions as well as cultivation method and application of mercurial paracoccus strain
KR20150066228A (en) * 2013-12-06 2015-06-16 (주)범안에코 A method of organic waste treatment using microbial carriers
CN104894007A (en) * 2015-05-12 2015-09-09 安徽农业大学 Compound microorganism preparation, preparing method and application of compound microorganism preparation to processing animal carcasses
CN106187335A (en) * 2016-07-13 2016-12-07 江门市地尔汉宇电器股份有限公司 A kind of oil removing preparation for changing food waste high-efficiency aerobic compost and preparation method thereof
CN110343631A (en) * 2019-05-06 2019-10-18 南开大学 A kind of kitchen garbage bio-fermentation agents and application
CN111440749A (en) * 2020-05-27 2020-07-24 中国科学院城市环境研究所 Pseudomonas pseudoalcaligenes sp.H3, screening method and application

Patent Citations (8)

* 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
CN102985392A (en) * 2010-03-23 2013-03-20 比奥麦克斯私人控股有限公司 Treatment of organic waste
CN103103147A (en) * 2012-07-18 2013-05-15 大连理工大学 Mercurial paracoccus strain simultaneously having denitrification and iron reduction functions as well as cultivation method and application of mercurial paracoccus strain
KR20150066228A (en) * 2013-12-06 2015-06-16 (주)범안에코 A method of organic waste treatment using microbial carriers
CN104894007A (en) * 2015-05-12 2015-09-09 安徽农业大学 Compound microorganism preparation, preparing method and application of compound microorganism preparation to processing animal carcasses
CN106187335A (en) * 2016-07-13 2016-12-07 江门市地尔汉宇电器股份有限公司 A kind of oil removing preparation for changing food waste high-efficiency aerobic compost and preparation method thereof
CN110343631A (en) * 2019-05-06 2019-10-18 南开大学 A kind of kitchen garbage bio-fermentation agents and application
CN111440749A (en) * 2020-05-27 2020-07-24 中国科学院城市环境研究所 Pseudomonas pseudoalcaligenes sp.H3, screening method and application

Similar Documents

Publication Publication Date Title
Ryckeboer et al. A survey of bacteria and fungi occurring during composting and self-heating processes
CN107586745B (en) Livestock manure compost deodorization nitrogen-retention strain, microbial inoculum and preparation method and application thereof
CN108456650B (en) Compound microbial deodorant bacterial agent and preparation method and application thereof
KR101161670B1 (en) Mixed strain for treating food waste and method for treating food waste using the same
CN101787350B (en) Functional composite biological agent for high-efficiency degradation of household refuses and application thereof
JP6342434B2 (en) Improved digestion of biosolids in wastewater
JP2004248618A (en) Bacterial group symbiotically living with fungus used for treating organic material and its application
JP2005538826A (en) Digestion method of sludge in water purification
CN112094782A (en) Composite microbial inoculum for degrading kitchen garbage and preparation method thereof
KR100679754B1 (en) Method and apparatus for decomposing sludge using alkalophilic strain
CN116041093A (en) Kitchen waste treating agent and kitchen waste treating method
KR100805036B1 (en) Novel Bacillus cereus ENB-02 strain having foodwaste decompositing capability and microbial agent
AU732311B2 (en) A method of preparing a microbial culture for wastewater treatment
JPH10151434A (en) Treating device for organic waste and treatment thereof
KR19990065800A (en) Wastewater Treatment Microorganisms and Microbial Agents
CN113151246B (en) Perishable garbage degradation microbial inoculum and application thereof
CN111979158A (en) Compound microbial inoculum for food waste compost as well as preparation method and application thereof
CN113403223B (en) Composite high Wen Junji and application thereof in plastic degradation
CN101555462B (en) Bacteria agent for deeply processing phenylamine oil refinery effluent and preparation method thereof
WO2005051868A1 (en) Procedure for composting of communal waste water sludge
US5925556A (en) Method of degrading polylactic acid resin using staphylococcus hominis and staphylococcus epidermidis
CN111979156A (en) Microbial composition for high-temperature fermentation treatment of municipal sludge and application thereof
CN111925968A (en) Compound microbial inoculum for kitchen waste composting and preparation method and application thereof
CN106085923B (en) A kind of preparation method and application of bacillus amyloliquefaciens and its biological flocculant
CN111893079A (en) Compound microbial inoculum for vegetable market garbage compost as well as preparation method and application thereof

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20201124

RJ01 Rejection of invention patent application after publication