CN108503038A - A kind of zymotechnique of river sewage processing composite bacteria agent - Google Patents

A kind of zymotechnique of river sewage processing composite bacteria agent Download PDF

Info

Publication number
CN108503038A
CN108503038A CN201810198222.7A CN201810198222A CN108503038A CN 108503038 A CN108503038 A CN 108503038A CN 201810198222 A CN201810198222 A CN 201810198222A CN 108503038 A CN108503038 A CN 108503038A
Authority
CN
China
Prior art keywords
composite bacteria
bacteria agent
fermentation
river sewage
zymotechnique
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
CN201810198222.7A
Other languages
Chinese (zh)
Inventor
张友超
朱红霞
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.)
Jiangxi Yun Yao Biotechnology Co Ltd
Original Assignee
Jiangxi Yun Yao Biotechnology 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 Jiangxi Yun Yao Biotechnology Co Ltd filed Critical Jiangxi Yun Yao Biotechnology Co Ltd
Priority to CN201810198222.7A priority Critical patent/CN108503038A/en
Publication of CN108503038A publication Critical patent/CN108503038A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • 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
    • C12N1/14Fungi; Culture media therefor
    • C12N1/16Yeasts; Culture media therefor
    • 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
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia

Abstract

The invention discloses zymotechniques, including nitrobacteria, denitrifying bacteria, photosynthetic bacteria, bacillus subtilis, amino acid ferment bacterium etc. that a kind of river sewage handles composite bacteria agent, which is characterized in that the zymotechnique includes the following steps:Step 1 prepare culture medium, step 2 anaerobic fermentation, step 3 ventilating fermentation, step 4 domestication fermentation, step 5 prepare river sewage processing composite bacteria agent.The present invention is high using nanometer analysis for soybean powder nutritive value, and trace elements can fully keep bioactivity, enhance the nutrition diversity of matrix, is equipped with straw powder and increases content of cellulose, matrix nutrition ingredient is comprehensive, is conducive to the growth of probiotics.Using more wheel sewage and temperature acclimatisation breeding, realize that microbial inoculum flora survival rate and content are high, bioactivity and adaptable, with characteristic that is efficient, stable, quickly breeding, the harmful substances such as ammonia nitrogen in water body of degrading, quickly restore balance water body bacterium phase, purifying water body improves environment.Overcome the deficiencies in the prior art.

Description

A kind of zymotechnique of river sewage processing composite bacteria agent
Technical field
The present invention relates to the fermentations that a kind of bacteria agent technical field more particularly to a kind of river sewage handle composite bacteria agent Technique.
Background technology
The river sewage processing composite bacteria agent of the prior art is prepared using normal fermentation technique, fermentation process poor controllability, Profitable strain survival rate and content are low, bioactivity and bad adaptability.
The present invention is high using breaking cell wall analysis for soybean powder nutritive value, and the nanometer of breaking cell wall is finely pulverized to be made in raw material Trace elements can fully keep bioactivity, enhance the nutrition diversity of matrix, be equipped with straw powder and increase content of cellulose, matrix Nutritional ingredient is comprehensive, is conducive to the growth of probiotics.Using more wheel sewage and temperature acclimatisation breeding, microbial inoculum flora survival rate is realized With content height, bioactivity and adaptable, have efficiently, the characteristic stablizing, quickly breed, have using the disease-resistant decomposition of probiotics Evil substance, enhances aquatic products healthy growth, the harmful substances such as ammonia nitrogen in water body of degrading, and removal rate is primary to throw up to 97% or more As long as after putting river water body can be effectively improved within 6 days, algae reproduction is can inhibit, quickly restore balance water body bacterium phase, purifying water body, Improve environment.Overcome the deficiencies in the prior art.
Invention content
The purpose of the present invention is to provide the zymotechniques that a kind of river sewage handles composite bacteria agent, reasonably solve existing There is the river sewage processing composite bacteria agent of technology to be prepared using normal fermentation technique, fermentation process poor controllability, profitable strain is deposited Motility rate and content are low, bioactivity and bad adaptability, cannot fully river training water body the problem of.
The present invention adopts the following technical scheme that:
A kind of zymotechnique of river sewage processing composite bacteria agent, including it is nanometer analysis for soybean powder, straw powder, nitrobacteria, anti- Nitrobacteria, photosynthetic bacteria, bacillus subtilis, bacillus coagulans, lactic acid bacteria, amino acid ferment bacterium, saccharomycete, feature exist In,
A kind of zymotechnique of river sewage processing composite bacteria agent includes the following steps:
Step 1: preparing culture medium:Nanometer analysis for soybean powder of the grain size less than 50 nanometers will be crushed to and be crushed to grain size and be less than The straw powder of 200 mesh presses 1:1 quality is added the 50%-60%'s of the nanometer analysis for soybean powder and straw powder gross mass than mixing Water prepares culture medium,
Step 2: anaerobic fermentation:The culture medium is moved into and presses 1 in sealed fermenter:1 ratio inoculation nitrobacteria, Denitrifying bacteria, photosynthetic bacteria, bacillus subtilis, bacillus coagulans, lactic acid bacteria, amino acid ferment bacterium, saccharomycete room temperature are normal Pressure ferment 96 hours, prepares anaerobic fermentation composite bacteria agent,
Step 3: ventilating fermentation:The culture medium is moved into and presses 1 in ventilating fermentation pond:1 ratio inoculation nitrobacteria, Denitrifying bacteria, photosynthetic bacteria, bacillus subtilis, bacillus coagulans, lactic acid bacteria, amino acid ferment bacterium, saccharomycete room temperature are normal Pressure ferment 96 hours, ventilation stirring in every 4 hours 15 minutes, prepares ventilating fermentation composite bacteria agent,
Step 4: domestication fermentation:The anaerobic fermentation composite bacteria agent and the ventilating fermentation composite bacteria agent are merged one Normal temperature and pressure open culturing is played after 72 hours, the anaerobic fermentation composite bacteria agent is added and the ventilating fermentation composite bacteria agent is overall Long-pending 1/3 sanitary sewage domestication fermentation 96 hours, adds the anaerobic fermentation composite bacteria agent and the ventilating fermentation is compound After the 1/3 trade effluent domestication fermentation 96 hours of microbial inoculum total volume, the anaerobic fermentation composite bacteria agent and described logical is added The 1/3 aquiculture sewerage domestication fermentation of the compoiste fermented microbial inoculum total volume of wind 96 hours, prepares compound domesticated strain agent, described Domestication fermentation is that normal pressure is open type fermented,
Step 5: preparing river sewage processing composite bacteria agent:The compound domesticated strain agent is pressed 1:1 mass ratio adds Enter the culture medium, temperature control is 6-8 days open type fermented at 38 DEG C -45 DEG C, prepares river sewage processing composite bacteria agent, constitutes A kind of zymotechnique of the river sewage processing composite bacteria agent.
Further, the river sewage processing composite bacteria agent includes nitrobacteria, denitrifying bacteria, photosynthetic bacteria, withered grass Bacillus, bacillus coagulans, lactic acid bacteria, amino acid ferment bacterium, saccharomycete, 4,000,000,000 plants/ml of bacterial strain content.
Further, the temperature control of the domestication fermentation is even with 1 DEG C per hour of pace of change between 5 DEG C -50 DEG C Fast gradual change cycle.
Further, the river sewage processing composite bacteria agent is 5 DEG C -50 DEG C using adaptive temperature.The present invention's has Benefit has the technical effect that:
The invention discloses a kind of river sewage handle composite bacteria agent zymotechnique, reasonably solve the prior art River sewage processing composite bacteria agent using normal fermentation technique prepare, fermentation process poor controllability, profitable strain survival rate with Content is low, bioactivity and bad adaptability, cannot fully river training water body the problem of.
The present invention is high using breaking cell wall analysis for soybean powder nutritive value, and the nanometer of breaking cell wall is finely pulverized to be made in raw material Trace elements can fully keep bioactivity, enhance the nutrition diversity of matrix, be equipped with straw powder and increase content of cellulose, matrix Nutritional ingredient is comprehensive, is conducive to the growth of probiotics.Using more wheel sewage and temperature acclimatisation breeding, microbial inoculum flora survival rate is realized With content height, bioactivity and adaptable, have efficiently, the characteristic stablizing, quickly breed, have using the disease-resistant decomposition of probiotics Evil substance, enhances aquatic products healthy growth, the harmful substances such as ammonia nitrogen in water body of degrading, and removal rate is primary to throw up to 97% or more As long as after putting river water body can be effectively improved within 6 days, algae reproduction is can inhibit, quickly restore balance water body bacterium phase, purifying water body, Improve environment.Overcome the deficiencies in the prior art.
Specific implementation mode
By the following description of the embodiment, it will more contribute to public understanding of the invention, but can't should be by Shen Given specific embodiment of asking someone is considered as the limitation to technical solution of the present invention, any definition to component or technical characteristic Be changed and/or to overall structure make form and immaterial transformation is regarded as defined by technical scheme of the present invention Protection domain.
Embodiment
A kind of zymotechnique of river sewage processing composite bacteria agent, including it is nanometer analysis for soybean powder, straw powder, nitrobacteria, anti- Nitrobacteria, photosynthetic bacteria, bacillus subtilis, bacillus coagulans, lactic acid bacteria, amino acid ferment bacterium, saccharomycete, feature exist In,
A kind of zymotechnique of river sewage processing composite bacteria agent includes the following steps:
Step 1: preparing culture medium:Nanometer analysis for soybean powder of the grain size less than 50 nanometers will be crushed to and be crushed to grain size and be less than The straw powder of 200 mesh presses 1:1 quality is added the 50%-60%'s of the nanometer analysis for soybean powder and straw powder gross mass than mixing Water prepares culture medium,
Step 2: anaerobic fermentation:The culture medium is moved into and presses 1 in sealed fermenter:1 ratio inoculation nitrobacteria, Denitrifying bacteria, photosynthetic bacteria, bacillus subtilis, bacillus coagulans, lactic acid bacteria, amino acid ferment bacterium, saccharomycete room temperature are normal Pressure ferment 96 hours, prepares anaerobic fermentation composite bacteria agent,
Step 3: ventilating fermentation:The culture medium is moved into and presses 1 in ventilating fermentation pond:1 ratio inoculation nitrobacteria, Denitrifying bacteria, photosynthetic bacteria, bacillus subtilis, bacillus coagulans, lactic acid bacteria, amino acid ferment bacterium, saccharomycete room temperature are normal Pressure ferment 96 hours, ventilation stirring in every 4 hours 15 minutes, prepares ventilating fermentation composite bacteria agent,
Step 4: domestication fermentation:The anaerobic fermentation composite bacteria agent and the ventilating fermentation composite bacteria agent are merged one Normal temperature and pressure open culturing is played after 72 hours, the anaerobic fermentation composite bacteria agent is added and the ventilating fermentation composite bacteria agent is overall Long-pending 1/3 sanitary sewage domestication fermentation 96 hours, adds the anaerobic fermentation composite bacteria agent and the ventilating fermentation is compound After the 1/3 trade effluent domestication fermentation 96 hours of microbial inoculum total volume, the anaerobic fermentation composite bacteria agent and described logical is added The 1/3 aquiculture sewerage domestication fermentation of the compoiste fermented microbial inoculum total volume of wind 96 hours, prepares compound domesticated strain agent, described Domestication fermentation is that normal pressure is open type fermented,
Step 5: preparing river sewage processing composite bacteria agent:The compound domesticated strain agent is pressed 1:1 mass ratio adds Enter the culture medium, temperature control is 6-8 days open type fermented at 38 DEG C -45 DEG C, prepares river sewage processing composite bacteria agent.It completes A kind of implementation of the zymotechnique of the river sewage processing composite bacteria agent.
Certainly, the present invention can also have other various embodiments, without deviating from the spirit and substance of the present invention, Those skilled in the art can make various corresponding change and deformations according to the present invention, but these it is corresponding change and Deformation should all belong to the protection domain of appended claims of the invention.

Claims (4)

1. a kind of zymotechnique of river sewage processing composite bacteria agent, including nanometer analysis for soybean powder, straw powder, nitrobacteria, anti-nitre Change bacterium, photosynthetic bacteria, bacillus subtilis, bacillus coagulans, lactic acid bacteria, amino acid ferment bacterium, saccharomycete, feature exists In,
A kind of zymotechnique of river sewage processing composite bacteria agent includes the following steps:
Step 1: preparing culture medium:Nanometer analysis for soybean powder of the grain size less than 50 nanometers will be crushed to and be crushed to grain size and be less than 200 mesh Straw powder press 1:For 1 quality than mixing, prepared by the water that the 50%-60% of the nanometer analysis for soybean powder and straw powder gross mass is added Culture medium,
Step 2: anaerobic fermentation:The culture medium is moved into and presses 1 in sealed fermenter:1 ratio is inoculated with nitrobacteria, anti-nitre Change bacterium, photosynthetic bacteria, bacillus subtilis, bacillus coagulans, lactic acid bacteria, amino acid ferment bacterium, saccharomycete normal temperature and pressure hair Ferment 96 hours, prepares anaerobic fermentation composite bacteria agent,
Step 3: ventilating fermentation:The culture medium is moved into and presses 1 in ventilating fermentation pond:1 ratio is inoculated with nitrobacteria, anti-nitre Change bacterium, photosynthetic bacteria, bacillus subtilis, bacillus coagulans, lactic acid bacteria, amino acid ferment bacterium, saccharomycete normal temperature and pressure hair Ferment 96 hours, ventilation stirring in every 4 hours 15 minutes, prepares ventilating fermentation composite bacteria agent,
Step 4: domestication fermentation:The anaerobic fermentation composite bacteria agent and the ventilating fermentation composite bacteria agent are merged often After normal temperature and pressure open culturing 72 hours, the anaerobic fermentation composite bacteria agent and the ventilating fermentation composite bacteria agent total volume is added 1/3 sanitary sewage domestication fermentation 96 hours, adds the anaerobic fermentation composite bacteria agent and the ventilating fermentation composite bacteria agent After the 1/3 trade effluent domestication of total volume is fermented 96 hours, the anaerobic fermentation composite bacteria agent and ventilation hair are added The 1/3 aquiculture sewerage domestication fermentation of ferment composite bacteria agent total volume 96 hours, prepares compound domesticated strain agent, the domestication Fermentation is that normal pressure is open type fermented,
Step 5: preparing river sewage processing composite bacteria agent:The compound domesticated strain agent is pressed 1:Described in 1 mass ratio is added Culture medium, temperature control is 6-8 days open type fermented at 38 DEG C -45 DEG C, prepares river sewage processing composite bacteria agent, constitutes described one The zymotechnique of kind river sewage processing composite bacteria agent.
2. a kind of zymotechnique of river sewage processing composite bacteria agent according to claim 1, which is characterized in that the river Sewage disposal composite bacteria agent includes nitrobacteria, denitrifying bacteria, photosynthetic bacteria, bacillus subtilis, bacillus coagulans, lactic acid Bacterium, amino acid ferment bacterium, saccharomycete, 4,000,000,000 plants/ml of bacterial strain content.
3. a kind of zymotechnique of river sewage processing composite bacteria agent according to claim 1, which is characterized in that the domestication The temperature control of fermentation is recycled between being 5 DEG C -50 DEG C with the at the uniform velocity gradual change of 1 DEG C per hour of pace of change.
4. a kind of zymotechnique of river sewage processing composite bacteria agent according to claim 1, which is characterized in that the river Sewage disposal composite bacteria agent is 5 DEG C -50 DEG C using adaptive temperature.
CN201810198222.7A 2018-03-09 2018-03-09 A kind of zymotechnique of river sewage processing composite bacteria agent Pending CN108503038A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810198222.7A CN108503038A (en) 2018-03-09 2018-03-09 A kind of zymotechnique of river sewage processing composite bacteria agent

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810198222.7A CN108503038A (en) 2018-03-09 2018-03-09 A kind of zymotechnique of river sewage processing composite bacteria agent

Publications (1)

Publication Number Publication Date
CN108503038A true CN108503038A (en) 2018-09-07

Family

ID=63377477

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810198222.7A Pending CN108503038A (en) 2018-03-09 2018-03-09 A kind of zymotechnique of river sewage processing composite bacteria agent

Country Status (1)

Country Link
CN (1) CN108503038A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113322203A (en) * 2021-05-31 2021-08-31 青岛万慧源环保科技有限公司 Composite microbial inoculum for aerobic denitrification and preparation method thereof
CN113564088A (en) * 2021-09-16 2021-10-29 张相润 Culture method for reducing eutrophication strains in aquaculture
US11629083B2 (en) * 2019-10-31 2023-04-18 Tongji University Organic composite powder carrier and application thereof in enhanced biological denitrification of municipal wastewater treatment

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP2364955A1 (en) * 2008-12-10 2011-09-14 Takurou Fujita Nitrate-removing bioreactor, method for forming nitrate-removing biofilm, and nitrate-removing method
CN102250768A (en) * 2011-06-01 2011-11-23 康源绿洲微生物技术(北京)有限公司 Method for preparing enzyme and bacterium composite agent for treating sewage and sludge
CN106701633A (en) * 2017-01-22 2017-05-24 哈尔滨明慧生物技术开发有限公司 Compound bactericide for treating sewage and sewage treatment method thereof

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP2364955A1 (en) * 2008-12-10 2011-09-14 Takurou Fujita Nitrate-removing bioreactor, method for forming nitrate-removing biofilm, and nitrate-removing method
CN102250768A (en) * 2011-06-01 2011-11-23 康源绿洲微生物技术(北京)有限公司 Method for preparing enzyme and bacterium composite agent for treating sewage and sludge
CN106701633A (en) * 2017-01-22 2017-05-24 哈尔滨明慧生物技术开发有限公司 Compound bactericide for treating sewage and sewage treatment method thereof

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US11629083B2 (en) * 2019-10-31 2023-04-18 Tongji University Organic composite powder carrier and application thereof in enhanced biological denitrification of municipal wastewater treatment
CN113322203A (en) * 2021-05-31 2021-08-31 青岛万慧源环保科技有限公司 Composite microbial inoculum for aerobic denitrification and preparation method thereof
CN113564088A (en) * 2021-09-16 2021-10-29 张相润 Culture method for reducing eutrophication strains in aquaculture

Similar Documents

Publication Publication Date Title
CN101139560B (en) Process for producing feeding micro-ecological preparation by solid fermentation of brewery mash with various bacterium and fermentation culture medium thereof
CN105218177B (en) The method for preparing composite microbic bacterial fertilizer using silkworm excrement fermentation
CN103395890A (en) Microbial preparation for improving freshwater aquaculture water body and preparation method thereof
CN101816371B (en) High-protein straw feed and preparation method thereof
CN103184174B (en) Production method of bacillus subtilis biological agent used for sodium humate-containing feed in medium
CN101885640B (en) Method for preparing mushroom medium by using microbial composite bacteria
CN110437000A (en) A kind of microbial manure and its preparation method and application
CN104326774A (en) Method for preparing microbial liquid fertilizer fermented animal dung transformed organic fertilizer
CN108503038A (en) A kind of zymotechnique of river sewage processing composite bacteria agent
CN108148791A (en) A kind of probiotics preparation for improving water quality in aquaculture and preparation method thereof
CN104293719B (en) Fast decomposing agent for fermentation bed aging padding, organic fertilizer and production method of organic fertilizer
CN109971682A (en) A kind of EM bacterium solution for aquaculture and preparation method thereof and application
CN101857469A (en) Preparation process for golf course lawn slow-release bio-organic fertilizer produced by three continuous fermentations
CN111990529A (en) Microbial fermentation method for preparing insect soluble liquid by utilizing hermetia illucens larvae and application
CN112205274A (en) Rice seedling raising matrix based on various agricultural wastes and preparation method thereof
CN102406068A (en) Method for preparing microbial fermented feed capable of keeping intestinal health of pigs
CN103319269B (en) Chicken manure, pig manure and pleurotus eryngii mushroom bran-containing organic fertilizer and preparation method thereof
CN106146200A (en) A kind of method utilizing ight soil and organic waste production biological organic fertilizer
CN105076715A (en) Microecological feed additive fermentation production method by using waste dross for enzymolysis of multiple bacteria
CN109988023A (en) A kind of production technology of novel microbial organic fertilizer special for rice
CN107779416A (en) A kind of high-efficiency fermenting bed complex micro organism fungicide
CN103205388B (en) Method for producing viable bacteria of bacillus licheniformis by high-density solid fermentation
CN116874316A (en) Method for high-value conversion of agricultural waste by cooperation of hermetia illucens and microorganisms
CN108424872A (en) A kind of preparation method of aquaculture composite bacteria agent
CN110818510A (en) Efficient organic biological bacterial fertilizer for soil improvement

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
RJ01 Rejection of invention patent application after publication

Application publication date: 20180907