CN106906170A - Complex micro organism fungicide and its preparation method and application - Google Patents

Complex micro organism fungicide and its preparation method and application Download PDF

Info

Publication number
CN106906170A
CN106906170A CN201710304523.9A CN201710304523A CN106906170A CN 106906170 A CN106906170 A CN 106906170A CN 201710304523 A CN201710304523 A CN 201710304523A CN 106906170 A CN106906170 A CN 106906170A
Authority
CN
China
Prior art keywords
preparation
culture
medium
inoculated
activation
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
CN201710304523.9A
Other languages
Chinese (zh)
Inventor
唐晓声
邹权
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.)
Suntime Environmental Remediation Co ltd
Original Assignee
Suntime Environmental Remediation 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 Suntime Environmental Remediation Co ltd filed Critical Suntime Environmental Remediation Co ltd
Priority to CN201710304523.9A priority Critical patent/CN106906170A/en
Publication of CN106906170A publication Critical patent/CN106906170A/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
    • 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
    • C02F3/341Consortia of bacteria
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/007Contaminated open waterways, rivers, lakes or ponds

Abstract

The invention discloses a kind of complex micro organism fungicide and its preparation method and application, the complex micro organism fungicide includes pseudomonad preparation, acinetobacter calcoaceticus preparation, bacillus amyloliquefaciens preparation, Ko subtilis bar preparation, bacillus licheniformis preparation, Lactococcus lactis bacteria preparation, hydrogenlike silicon ion preparation, alkali lake enlightening thatch Salmonella preparation and Rhodopseudomonas palustris preparation.Preparation method is comprised the following steps:(1) complex micro organism fungicide component is prepared;(2) complex micro organism fungicide component is mixed in proportion, obtains complex micro organism fungicide.The complex micro organism fungicide can simultaneously decompose the growth of phosphorus element concentration and suppression algae in ammonia nitrogen and nitrate, reduction water body in different organic matters, degradation water.Carry out town and country river sewage in-situ immobilization using complex micro organism fungicide of the invention, with efficient, quick, non-secondary pollution, it is simple to operate the features such as, be conducive to large-scale promotion application.

Description

Complex micro organism fungicide and its preparation method and application
Technical field
The invention belongs to technical field of environmental microorganism, it is related to a kind of for the compound micro- of town and country river sewage in-situ immobilization Bacteria agent and its preparation method and application.
Background technology
City river and lake be with human being's production and the closely coupled water environment of living, it is important as urban ecological system Part, with supply water source, improve environment, the functions, the life to city such as greenery patches, culture and education and amusement and leisure be provided State is built significant.But with the continuous quickening of urbanization process, urban population aggregation, economic activity frequency increasingly Numerous, industrial wastewater and sanitary sewage largely discharge increasing, and the random discarding of rubbish causes organic matter, ammonia nitrogen, total p and ses in water body Change the pollutants such as hydrogen to continue to increase, problem of environmental pollution is increasingly serious, the serious society for restricting city, economy and continuity of environment Development, while jeopardizing the healthy of the people.
The traditional means of removal water pollutant mainly have physics and chemical method, although administered in river course and lake pollution It is upper that there is certain effect, but there is also problem.Can such as Sediment Dredging in physical method have length to pollution of river thing The control of effect and the also presence dispute that whether had a negative impact to benthonic realm.Addition molysite in chemical flocculation treatment technology Promote phosphorus precipitation, add the methods such as lime denitrogenation, although instant effect, efficiency high, but easily cause secondary pollution.
Bioremediation technology is the new technology that the water pollutant that recent fast development is got up is repaired, and it is using specific Biological particularly microorganism is to the absorption of pollutant in water body, conversion or degrades, and reaches and slows down or finally eliminate water pollution, extensive The biological control measure of rehydration body ecological functions.Microorganism tool is because its cultivation cycle is short, growth and breeding is rapid, adaptable, conversion The features such as efficiency high, played an important role during polluted river water is administered.The work of microorganism remediation river sewage With mainly including:1) microorganism is Self substances, another aspect microorganism by assimilation meeting transform portion organic pollution Different biology enzyme energy fast degradation larger molecular organicses can be produced, degraded and removal to organic pollutants in water body is realized.2) Some amonifying bacterias, nitrobacteria and denitrifying bacteria can realize Water element with the ammonia nitrogen and nitrate in degradation water Biogeochemical cycle process, and finally make excessive nitrogen in water body that water body is escaped in the form of nitrogen.3) one slightly Biology can reduce phosphorus element concentration in water body by the metabolism of characteristic, and another aspect certain micro-organisms can be turned into by same With, the available phosphorus in water body is converted into the organophosphor of thalline itself, acted on by the transmission of food chain, in removal water body Phosphorus.4) by the synergy of complex microorganism, water body towel nitrogen, phosphorus recycling level are reduced, is pressed down by way of nutrient competition The growth of algae processed;Simultaneously by improving water body physicochemical environment, promote the growth of zooplankter population to grow, caught with zooplankter The mode for eating algae controls the growth of algae.
The patent of invention of Application No. 201410449850.X discloses a kind of composite microbial of Urban River Water pollution control Thing preparation and preparation method thereof, the method is by by acidophilus bacillus preparation, Candida tropicalis agent and withered grass bud pole Bacteria agent is prepared by mixing into complex micro organism fungicide, is suitable to city and asks that river COD and ammonia-nitrogen content are exceeded, river is dirty, hair Smelly to wait the reparation of pollution and administer, it can quickly repair water ecological setting, prevent secondary pollution of water, and can quickly recover water The self-purification function of body, clears up river bed sludge.
The patent of invention of Application No. 201510949257.6 discloses a kind of complex microorganism system for river regulation Agent, complex microorganism includes the pure coccus of nitrous acid, thiobacillus thiooxidant, Paracoccus denitrificans, bud pole bacterium, red spirillum, lactic acid bar Bacterium and saccharomyces cerevisiae.In complex micro organism fungicide input polluted-water, the water body smelly problem of nigrescence can be obviously improved, reduce water Matter ammonia nitrogen and total phosphorus content.
The patent of invention of Application No. 201310126043.X discloses a kind of microbial bacteria that sewage is asked for purifying Agent and preparation method thereof, it includes following components in parts by weight:20~40 parts of natto bud pole bacterium, 10~30 parts of nitrobacteria, 5~15 parts of white-rot fungi, 5~15 parts of pseudomonad, 10~40 parts of photosynthetic bacteria.The microbial bacterial agent has strong adaptability, energy It is quick to form dominant microflora, supplement water body original inhabitants bacterium.COD, NH3-N, total nitrogen, TP of polluted river water etc. can be reduced in input water, And can be deodorant except color.And noble and unsullied property biology enzyme can be produced, and suppressing the growth of harmful bacteria, accelerated decomposition residual bait, animals and plants are residual Body, with significant effects of purification quality.
It can be seen that, continue to explore microbial bacterial agent for the research of river regulation, it is expected to alleviate or thoroughly improves increasingly serious Water body environment pollution problem.
The content of the invention
The technical problem to be solved in the present invention is to overcome the deficiencies in the prior art, there is provided repaiied a kind of town and country river sewage original position Multiple complex micro organism fungicide, can decompose ammonia nitrogen and nitrate in different organic matters, degradation water, reduce phosphorus element in water body Concentration and the growth of suppression algae.
In order to solve the above technical problems, the present invention proposes following technical scheme:
A kind of complex micro organism fungicide, the complex micro organism fungicide includes pseudomonad preparation, acinetobacter calcoaceticus preparation, solution Bacillus amyloliquefacienses preparation, Ko subtilis bar preparation, bacillus licheniformis preparation, Lactococcus lactis bacteria preparation, hydrogenlike silicon ion system Agent, alkali lake enlightening thatch Salmonella preparation and Rhodopseudomonas palustris preparation.
Above-mentioned complex micro organism fungicide, it is preferred that pseudomonad is entrusted to be preserved in Chinese microorganism strain preservation management Member's meeting common micro-organisms center, deposit number is the pseudomonad of CGMCC No.13433.
Above-mentioned complex micro organism fungicide, it is preferred that the parts by volume of each component is in the complex micro organism fungicide:It is false single 5~15 parts of born of the same parents' bacteria preparation, 5~15 parts of acinetobacter calcoaceticus preparation, 5~15 parts of bacillus amyloliquefaciens preparation, bacillus subtilis system 5~15 parts of agent, 5~15 parts of bacillus licheniformis preparation, 5~15 parts of Lactococcus lactis bacteria preparation, hydrogenlike silicon ion preparation 5~15 Part, 5~15 parts of alkali lake enlightening thatch Salmonella preparation, 5~15 parts of Rhodopseudomonas palustris preparation.
Above-mentioned complex micro organism fungicide, it is preferred that in the complex micro organism fungicide, total clump count >=6.0 × 1010cfu/mL。
Above-mentioned complex micro organism fungicide, it is preferred that acinetobacter calcoaceticus are acinetobacter calcoaceticus CGMCC No.1.8587, solve starch Bacillus is bacillus amyloliquefaciens CGMCC No.1.7463, and Bacillus subtillis is Bacillus subtillis CGMCC No.1.2162, bacillus licheniformis are bacillus licheniformis CGMCC No.1.6510, and Lactococcus lactis are Lactococcus lactis CGMCC No.1.3920, hydrogenlike silicon ion is hydrogenlike silicon ion CGMCC No.1.2174, and alkali lake enlightening thatch Salmonella is alkali lake enlightening thatch Salmonella CGMCC No.1.6147, Rhodopseudomonas palustris is Rhodopseudomonas palustris CGMCC No.1.2351.
Used as a total inventive concept, the present invention also provides a kind of preparation method of above-mentioned complex micro organism fungicide, Comprise the following steps:
(1) pseudomonad is inoculated in solid slope culture medium I and is activated, activation pseudomonad is obtained;Then will Activation pseudomonad is inoculated in fluid nutrient medium I and is enlarged culture;It is inoculated in fermentation medium I, fermented culture system Obtain cell concentration and be not less than 3.0 × 109The pseudomonad preparation of cfu/mL;
(2) acinetobacter calcoaceticus are inoculated in solid slope culture medium II and are activated, activation acinetobacter calcoaceticus are obtained;Then will Activation acinetobacter calcoaceticus are inoculated in fluid nutrient medium II and are enlarged culture;It is inoculated in fermentation medium II, fermented culture Cell concentration is obtained and is not less than 5.0 × 107The acinetobacter calcoaceticus preparation of cfu/mL;
(3) bacillus amyloliquefaciens are inoculated in solid slope culture medium III and are activated, activation solution starch bud is obtained Spore bacillus;Then activation bacillus amyloliquefaciens are inoculated in fluid nutrient medium III and are enlarged culture;It is inoculated in fermentation training Support in base III, fermented culture is obtained cell concentration and is not less than 8.0 × 109The bacillus amyloliquefaciens preparation of cfu/mL;
(4) Bacillus subtillis is inoculated in solid slope culture medium IV and is activated, activation Ko subtilis bar is obtained Bacterium;Then activation Bacillus subtillis is inoculated in fluid nutrient medium IV and is enlarged culture;It is inoculated in fermentation medium IV In, fermented culture is obtained cell concentration and is not less than 6.0 × 109The Bacillus subtillis preparation of cfu/mL;
(5) bacillus licheniformis are inoculated in solid slope culture medium V and are activated, activation lichens brood cell's bar is obtained Bacterium;Then activation bacillus licheniformis are inoculated in fluid nutrient medium V and are enlarged culture;It is inoculated in fermentation medium V, Fermented culture is obtained cell concentration and is not less than 8.0 × 108The bacillus licheniformis preparation of cfu/mL;
(6) Lactococcus lactis are inoculated in solid slope culture medium VI and are activated, activation Lactococcus lactis are obtained;So Activation Lactococcus lactis are inoculated in fluid nutrient medium VI afterwards and are enlarged culture;It is inoculated in fermentation medium VI, through hair Ferment culture is obtained cell concentration and is not less than 7.0 × 105The Lactococcus lactis bacteria preparation of cfu/mL;
(7) hydrogenlike silicon ion is inoculated in solid slope culture medium VII and is activated, activation hydrogenlike silicon ion is obtained; Then activation hydrogenlike silicon ion is inoculated in fluid nutrient medium VII and is enlarged culture;It is inoculated in fermentation medium VII, Fermented culture is obtained cell concentration and is not less than 8.0 × 107The hydrogenlike silicon ion preparation of cfu/mL;
(8) alkali lake enlightening thatch Salmonella is inoculated in solid slope culture medium IIX and is activated, activation alkali lake enlightening Ci Shi is obtained Bacterium;Then activation alkali lake enlightening thatch Salmonella is inoculated in fluid nutrient medium IIX and is enlarged culture;It is inoculated in fermentation medium In IIX, fermented culture is obtained cell concentration and is not less than 6.0 × 107The alkali lake enlightening thatch Salmonella preparation of cfu/mL;
(9) Rhodopseudomonas palustris is inoculated in solid slope culture medium IX and is activated, the activation red vacation in marsh is obtained Monad;Then activation Rhodopseudomonas palustris is inoculated in fluid nutrient medium IX and is enlarged culture;It is inoculated in fermentation training Support in base IX, fermented culture is obtained cell concentration and is not less than 4.0 × 107The Rhodopseudomonas palustris preparation of cfu/mL;
(10) pseudomonad preparation, acinetobacter calcoaceticus preparation, step (3) obtained in step (2) obtained in step (1) are obtained Bacillus amyloliquefaciens preparation, Bacillus subtillis preparation, bacillus licheniformis obtained in step (5) obtained in step (4) Preparation, Lactococcus lactis bacteria preparation, hydrogenlike silicon ion preparation, alkali obtained in step (8) obtained in step (7) obtained in step (6) After lake enlightening thatch Salmonella preparation and Rhodopseudomonas palustris preparation obtained in step (9) proportionally mix, complex microorganism is obtained Microbial inoculum.
The preparation method of above-mentioned complex micro organism fungicide, it is preferred that in the solid medium I, 1g/ containing peptone 100mL, dusty yeast 1.5g/100mL, glucose 2g/100mL, dipotassium hydrogen phosphate 0.1g/100mL, agar 2g/100mL, pH value 6 ~8;In the solid medium II, 1.5g/100mL containing peptone, glucose 1g/100mL, sodium chloride 0.5g/100mL, fine jade Fat 2g/100mL, pH value 6.5~7.5;In the solid medium III, 1g/100mL containing tryptone, yeast extract 0.5g/ 100mL, sodium chloride 1g/100mL, agar 2g/100mL, pH value 6~8;In the solid medium IV, 1g/ containing tryptone 100mL, yeast extract 0.5g/100mL, sodium chloride 1g/100mL, agar 2g/100mL, pH value 6~8;The solid medium V In, 1g/100mL containing peptone, yeast extract 0.5g/100mL, sodium chloride 1g/100mL, agar 2g/100mL, pH value 6~8;Institute In stating solid medium VI, 0.5g/100mL containing beef extract, peptone 0.5g/100mL, yeast extract 0.5g/100mL, tomato juice 5g/100mL, glucose 1.0g/100mL, calcium bicarbonate 1.0g/100mL, agar 2g/100mL, pH value 4~6.5;The solid In culture medium VII, 0.5g/100mL containing beef extract, peptone 0.5g/100mL, yeast extract 0.5g/100mL, agar 2g/ 100mL, pH value 6.5~7.5;In the solid medium IIX, 1g/100mL containing glucose, sodium acetate 0.2g/100mL, yeast Cream 0.5g/100mL, ammonium chloride 0.25g/100mL, agar 2g/100mL, pH value 6.5~7.5;In the solid medium IX, 1g/100mL containing glucose, sodium acetate 0.2g/100mL, yeast extract 0.5g/100mL, biotin 0.01g/100mL, magnesium sulfate 0.02g/100mL, agar 2g/100mL, pH value 6.5~7.5.
The preparation method of above-mentioned complex micro organism fungicide, it is preferred that in the fluid nutrient medium I, 1.5g/ containing glucose 100mL, yeast extract 0.5g/100mL, peptone 1g/100mL, potassium dihydrogen phosphate 0.05g/100mL, magnesium sulfate 0.04g/ 100mL;In the fluid nutrient medium II, 1.5g/100mL containing glucose, yeast extract 0.5g/100mL, peptone 1g/100mL, Sodium chloride 0.5g/100mL;In fluid nutrient medium III, 2.5g/100mL containing glucose, yeast extract 0.2g/100mL, biphosphate Potassium 0.02g/100mL;In the fluid nutrient medium IV, 2.5g/100mL containing glucose, yeast extract 0.2g/100mL, biphosphate Potassium 0.02g/100mL;In the fluid nutrient medium V, 2.0g/100mL containing glycerine, yeast extract 0.5g/100mL, corn pulp 1.5g/ 100mL, potassium dihydrogen phosphate 0.02g/100mL;In the fluid nutrient medium VI, 2.0g/100mL containing glucose, yeast extract 0.5g/ 100mL, corn pulp 1.5g/100mL, potassium dihydrogen phosphate 0.02g/100mL, calcium bicarbonate 1.0g/100mL;The Liquid Culture In base VII, 2.0g/100mL containing glucose, corn pulp 1.5g/100mL, ammonium sulfate 1.0g/100mL, sodium glutamate 0.2g/ 100mL, potassium dihydrogen phosphate 0.02g/100mL;In the fluid nutrient medium IIX, 1g/100mL containing glucose, sodium acetate 0.5g/ 100mL, yeast extract 0.5g/100mL, ammonium chloride 0.5g/100mL, potassium nitrate 0.2g/100mL, magnesium sulfate 0.02g/100mL, phosphorus Sour hydrogen dipotassium 0.05g/100mL;In the fluid nutrient medium IX, 1.0g/100mL containing glucose, sodium acetate 1.0g/100mL, ferment Female cream 0.5g/100mL, ammonium chloride 0.5g/100mL, magnesium sulfate 0.05g/100mL, dipotassium hydrogen phosphate 0.02g/100mL.
The preparation method of above-mentioned complex micro organism fungicide, it is preferred that in the fermentation medium I, containing glucose 0.5~ 5g/100mL, 0.5~4g/100mL of yeast extract, 1.0~6g/100mL of analysis for soybean powder, 0.01~0.1g/100mL of potassium dihydrogen phosphate, 0.01~0.1g/100mL of magnesium sulfate;In the fermentation medium II, containing 0.5~5g/100mL of glucose, yeast extract 0.3~ 3g/100mL, (NH4)2SO40.1~2.0g/100mL, 0.1~1g/100mL of sodium citrate, 0.01~0.5g/ of magnesium sulfate 100mL;In the fermentation medium III, containing 0.5~5.0g/100mL of molasses, 0.3~3.0g/100mL of brown sugar, yeast extract 0.2 ~2.0/100mL, 0.5~5.0/100mL of corn pulp, 0.01~0.05g/100mL of potassium dihydrogen phosphate, magnesium sulfate 0.005~ 0.05g/100mL;In the fermentation medium IV, containing 0.5~5.0g/100mL of molasses, 0.5~5.0g/100mL of brown sugar, soya bean 0.5~3.0g/100mL of powder, 1.0~5.0g/100mL of corn pulp, 0.01~0.1g/100mL of potassium dihydrogen phosphate;The fermentation training In foster base V, containing 1.0~5.0g/100mL of glycerine, 1.0~5.0/100mL of molasses, 1.0~5.0g/100mL of corn pulp, analysis for soybean powder 0.5~3.0g/100mL, 0.01~0.1g/100mL of potassium dihydrogen phosphate, 0.01~0.1g/100mL of magnesium sulfate;The fermentation training In foster base VI, containing 1.0~5.0g/100mL of glucose, 1.0~5.0g/100mL of yeast extract, 1.0~5.0/100mL of corn pulp, 0.01~0.1g/100mL of potassium dihydrogen phosphate, 0.5~2.0g/100mL of calcium bicarbonate, 0.2~2.0g/100mL of citric acid;It is described In fermentation medium, containing 1.0~5.0g/100mL of glucose, 1.0~5.0g/100mL of corn pulp, 1.0~5.0g/ of ammonium sulfate 100mL, 0.1~1.5g/100mL of sodium glutamate, 0.01~0.1g/100mL of potassium dihydrogen phosphate;In the fermentation medium IIX, Containing 1.0~5.0g/100mL of glucose, 0.5~2.0g/100mL of sodium acetate, 1.0~5.0g/100mL of yeast extract, ammonium chloride 0.5 ~2.0g/100mL, 0.05~0.5g/100mL of potassium nitrate, 0.01~0.1g/100mL of magnesium sulfate, dipotassium hydrogen phosphate 0.01~ 0.1g/100mL, 0.1~1.0g/100mL of sodium potassium tartrate tetrahydrate;In the fermentation medium IX, containing 0.2~2.0g/ of glucose 100mL, 0.2~2.0g/100mL of sodium acetate, 0.2~2.0g/100mL of yeast extract, 0.2~2.0g/100mL of ammonium chloride, sulfuric acid 0.01~0.1g/100mL of magnesium, 0.01~0.1g/100mL of dipotassium hydrogen phosphate.
Preferably, in the step (1), the activation condition is:30~38 DEG C, 48~72h of activation culture;The expansion Condition of culture is:Under rotary shaker 180rpm rotating speeds, 30 DEG C of culture 48h;The fermentation culture conditions are:Rotatably shaking Under bed 100~200rpm rotating speeds, 30~38 DEG C of 48~96h of culture.
Preferably, in the step (2), the activation condition is:30~38 DEG C, 48~72h of activation culture;The expansion Condition of culture is:Under rotary shaker 180rpm rotating speeds, 30 DEG C of culture 48h;The fermentation culture conditions are:Rotatably shaking Under bed 100~160rpm rotating speeds, 30~38 DEG C of 49~120h of culture.
Preferably, in the step (3), the activation condition is:32~38 DEG C, 48~72h of activation culture;The expansion Condition of culture is:Under rotary shaker 160rpm rotating speeds, 30 DEG C of culture 48h;The fermentation culture conditions are:Rotatably shaking Under bed 100~200rpm rotating speeds, 30~38 DEG C of 48~120h of culture.
Preferably, in the step (4), the activation condition is:32~38 DEG C, 48~72h of activation culture;The expansion Condition of culture is:Under rotary shaker 150rpm rotating speeds, 37 DEG C of culture 48h;The fermentation culture conditions are:Rotatably shaking Under bed 100~200rpm rotating speeds, 32~38 DEG C of 48~120h of culture.
Preferably, in the step (5), the activation condition is:32~38 DEG C, 48~72h of activation culture;The expansion Condition of culture is:Under rotary shaker 150rpm rotating speeds, 37 DEG C of culture 48h;The fermentation culture conditions are:Rotatably shaking Under bed 100~200rpm rotating speeds, 30~38 DEG C of 48~120h of culture.
Preferably, in the step (6), the activation condition is:32~38 DEG C, 48~72h of activation culture;The expansion Condition of culture is:Under rotary shaker 150rpm rotating speeds, 35 DEG C of culture 72h;The fermentation culture conditions are:Rotatably shaking Under bed 30~100rpm rotating speeds, 28~38 DEG C of 72~200h of culture.
Preferably, in the step (7), the activation condition is:32~38 DEG C, 48~72h of activation culture;The expansion Condition of culture is:Under rotary shaker 150rpm rotating speeds, 32 DEG C of culture 72h;The fermentation culture conditions are:Rotatably shaking Under bed 100~200rpm rotating speeds, 28~38h DEG C of 72~200h of culture.
Preferably, in the step (8), the activation condition is:32~38 DEG C, 72~96h of activation culture;The expansion Condition of culture is:Under rotary shaker 150rpm rotating speeds, 32 DEG C of culture 72h;The fermentation culture conditions are:Rotatably shaking Under bed 50~100rpm rotating speeds, 30~38 DEG C of 72~160h of culture.
Preferably, in the step (9), the activation condition is:32~38 DEG C, 72~96h of activation culture;The expansion Condition of culture is:Under rotary shaker 50rpm rotating speeds, 32 DEG C of culture 96h;The fermentation culture conditions are:Rotatably shaking Under bed 50~100rpm rotating speeds, 32~38 DEG C of 100~200h of culture.
Used as a total inventive concept, the present invention also provides a kind of above-mentioned complex micro organism fungicide or above-mentioned compound The application of complex micro organism fungicide prepared by the preparation method of microbial bacterial agent in the river sewage in-situ immobilization of town and country.
Preferably, the application includes phosphorus element in ammonia nitrogen and nitrate, the reduction water body in decomposing organic matter, degradation water Concentration and/or the growth of suppression algae.
Compared with prior art, the advantage of the invention is that:
1st, complex micro organism fungicide of the invention, can simultaneously decompose the ammonia nitrogen and nitre in different organic matters, degradation water Base nitrogen, the growth for reducing phosphorus element concentration and suppression algae in water body.Town and country are carried out using complex micro organism fungicide of the invention River sewage in-situ immobilization, with efficient, quick, non-secondary pollution, it is simple to operate the features such as, be conducive to large-scale promotion should With.
2nd, the pseudomonad CGMCC No.13433 that complex micro organism fungicide of the invention is included are applicants by screening A kind of efficient heterotrophic nitrification-aerobic denitrification bacterial strain for obtaining, and have efficient phenol degrading performance concurrently.Heterotrophic nitrification performance Measurement result shows that the bacterial strain has clearance very high, and intermediate product NO3-N and NO2-N accumulation for ammonia nitrogen Seldom;Aerobic denitrification capability measurement result shows that the bacterial strain can be fine by nitrate nitrogen and nitrite nitrogen under aerobic conditions Removal, and intermediate product cumulant is few, non-secondary pollution.Meanwhile, SBR is applied to after bacterial strain Amplification Culture, and (batch-type is lived Property sludge) technique, there is clearance higher to Ammonia Nitrogen in Municipal Wastewater, total nitrogen and COD, in sanitary sewage and other are each Planting during polluted-water is administered has application value very high.Phenol degrading performance study result shows that phenol concentration is 0- 100mg/L is interval, and clearance can reach more than 95%, 100-200mg/L intervals, and it is left that a step clearance can also reach 80% The right side, therefore, the bacterial strain has extraordinary in the water process of the exceeded simultaneous phenol pollution of ammonia nitrogen of industrial or agricultural and underground water or improvement Application prospect.
Biomaterial preservation information
Pseudomonad (Pseudomonas sp.) of the invention, is preserved in China Microbiological bacterium on December 7th, 2016 Plant preservation administration committee's common micro-organisms center (CGMCC), address:Yard 1, BeiChen xi Road, Chaoyang District, Beijing City 3, China Institute of microbiology of the academy of sciences, postcode:100101.The title of the bacterial strain is:Meng Shi pseudomonad PS02, Classification And Nomenclature is Pseudomonas monteilii PS02, deposit number is:CGMCC No.13433.
Specific embodiment
Below in conjunction with Figure of description and specific preferred embodiment, the invention will be further described, but not therefore and Limit the scope of the invention.
Embodiment 1:Screening and performance measurement, culture and the preservation of pseudomonad CGMCC No.13433
(1) screening and performance measurement of pseudomonad CGMCC No.13433
The pseudomonad CGMCC No.13433 are from the treatment tank of Shanghai in activated sludge obtained by isolation and selection A kind of efficient heterotrophic nitrification-aerobic denitrification bacterium, pseudomonad, preservation are accredited as through Chinese microorganism strain collection In China Committee for Culture Collection of Microorganisms's common micro-organisms center.Specific screening process is as follows:
Activated sludge takes the treatment tank into the treatment tank of Shanghai, and 5mL muddy water mixed solutions are taken from the activated sludge Into the heterotrophic nitrification culture medium of 45mL sterilizings.The formula of heterotrophic nitrification culture medium is:(NH4)2SO40.945g/L, citric acid Sodium 6.536g/L, MgSO4·7H2O 1g/L, NaCl 0.12g/L, MnSO4·H2O 0.01g/L, FeSO4·7H2O 0.02g/ L, KH2PO40.2g/L, Na2HPO40.3g/L, pH 7.0~7.5.It is subsequently placed in 30 DEG C, the gas bath shaking table enrichment training of 200rpm Support 12h.After pregnant solution is carried out into gradient dilution, heterotrophic nitrification solid medium (agar 20g/L, remaining composition are spread evenly across With heterotrophic nitrification culture medium).After cultivating 1d in 30 DEG C of constant incubators, picking form monoclonal of different sizes is rule pure Numbering preservation after change, more than 10 strain bacterial strains are obtained through primary dcreening operation.
By above primary dcreening operation inoculation to bromthymol blue (BTB) isolation medium.The formula of BTB culture mediums is:KNO3 1g/L, sodium succinate 8.5g/L, MgSO4·7H2O 1g/L, CaCl20.15g/L, FeSO4·7H2O 0.05g/L, KH2PO4 0.25g/L, Na2HPO40.3g/L, 1%BTB 1mL, agar 20g/L, pH 7.0~7.5.1gBTB is dissolved in 100ml absolute ethyl alcohols Obtain final product 1%BTB ethanol solutions.After cultivating 1d in 30 DEG C of constant incubators, there is the bacterium of blue halos in picking surrounding media Strain to BTB culture mediums, line is purified and numbering preservation.
From flat board picking colony to enriched medium, the formula of enriched medium is:Glucose 6g/L, dusty yeast 12g/L, MgSO4·7H2O 2.5g/L, CaCl20.5g/L, KH2PO42.5g/L, pH 7.0.30 DEG C of gas bath shaking table 200rpm cultivate 12h, 1% (volume ratio) bacterium solution centrifuge washing is taken, nitrification culture medium is seeded to.Nitrify culture medium formula be:(NH4)2SO4 0.945g/L, sodium citrate 16.34g/L, MgSO4·7H2O 1g/L, KH2PO40.2g/L, Na2HPO40.3g/L.30 DEG C, 200rpm Shaking cultures, period sampling measuring ammonia nitrogen (NH4 +- N), nitrate (NO3 -- N) and nitrite (NO2 -- N) concentration, By the heterotrophic nitrification performance for analyzing the clearance of total nitrogen (TN) to judge bacterial strain.Fig. 1 is pseudomonad CGMCC No.13433 To the removal effect figure of ammonia nitrogen, as seen from Figure 1, pseudomonad CGMCC No.13433 possess good nitrogen removal performance, 24h When reach 98.7% to nitrogen removal rate, and nitrate nitrogen and nitrite nitrogen as intermediate product is seldom accumulated, and cumulant exists 0.02mg/L or so.
To enriched medium, 30 DEG C of gas bath shaking table 200rpm cultivate 12h to the good bacterium colony of picking Nitrification, take 1% (volume Than) bacterium solution centrifuge washing, it is seeded to denitrification culture medium.Denitrification culture medium prescription is:KNO30.722g/L, sodium citrate 6.128g/L, MgSO4·7H2O 1g/L, KH2PO40.25g/L, Na2HPO40.3g/L.30 DEG C, 200rpm Shaking cultures are fixed Phase is measured by sampling ammonia nitrogen (NH4 +- N), nitrate (NO3 -- N) and nitrite (NO2 -- N) concentration, by analyzing total nitrogen (TN) Clearance judge the aerobic denitrification capability of bacterial strain.Fig. 2 is removals of the pseudomonad CGMCC No.13433 to nitrate Design sketch, as seen from Figure 2, pseudomonad CGMCC No.13433 have good nitrogen removal performance, with nitrate as only During one nitrogen source, its denitrification percent reaches 99.7%.
(2) cultivate
The culture medium for using for:Glucose 1.5g/100mL, yeast extract 0.5g/100mL, peptone 1g/100mL, phosphoric acid Potassium dihydrogen 0.05g/100mL, magnesium sulfate 0.04g/100mL.Pseudomonad CGMCC No.13433 are inoculated in above-mentioned culture medium In, under rotary shaker 150rpm rotating speeds, 32 DEG C of culture 24h obtain final product the seed for being suitable to inoculation.
(3) preserve
Added by the glycerine of high-temperature sterilization in cultured pseudomonad seed in step (2), glycerine is in seed liquor In concentration be 30% (V/V), be placed on -80 DEG C of Refrigerator stores.
Embodiment 2
The preparation of the complex micro organism fungicide of town and country river sewage in-situ immobilization
(1) pseudomonad CGMCC No.13433 seeds are taken, is inoculated in solid medium I, activated culture, activate bar Part is:37 DEG C, activation culture 48h is obtained activation pseudomonad CGMCC No.13433;Then will activation pseudomonad CGMCC No.13433 is inoculated in fluid nutrient medium I and is enlarged culture, and Amplification Culture condition is:In rotary shaker 180rpm rotating speeds Under, 30 DEG C of culture 48h;The pseudomonad seed that will be enlarged by culture is inoculated in fermentation medium I by the 10% of fermentating liquid volume, Under rotary shaker 150rpm rotating speeds, after 32 DEG C of culture 96h, pseudomonad preparation is obtained, pseudomonad cell concentration is 4.0 ×109cfu/mL。
Wherein, in solid medium I, 1g/100mL containing peptone, dusty yeast 1.5g/100mL, glucose 2g/100mL, Dipotassium hydrogen phosphate 0.1g/100mL, agar 2g/100mL, pH value 6~8;
In fluid nutrient medium I, 1.5g/100mL containing glucose, yeast extract 0.5g/100mL, peptone 1g/100mL, phosphoric acid Potassium dihydrogen 0.05g/100mL, magnesium sulfate 0.04g/100mL;
In fermentation medium I, 2g/100mL containing glucose, yeast extract 1.5g/100mL, analysis for soybean powder 2/100mL, di(2-ethylhexyl)phosphate Hydrogen potassium 0.02g/100mL, magnesium sulfate 0.01g/100mL.
(2) acinetobacter calcoaceticus CGMCC No.1.8587 are taken, is inoculated in solid medium, activated culture, activation condition For:37 DEG C, activation culture 60h is obtained activation acinetobacter calcoaceticus;Then activation acinetobacter calcoaceticus are inoculated in into fluid nutrient medium II is carried out Amplification Culture;Amplification Culture condition is:Under rotary shaker 180rpm rotating speeds, 30 DEG C of culture 48h;Will be enlarged by the motionless of culture Bacillus seed is inoculated in fermentation medium II by the 10% of fermentating liquid volume, under rotary shaker 160rpm rotating speeds, 32 DEG C After culture 96h, acinetobacter calcoaceticus preparation is obtained, acinetobacter calcoaceticus cell concentration is 8.0 × 107cfu/mL。
Wherein, in solid medium II, 1.5g/100mL containing peptone, glucose 1g/100mL, sodium chloride 0.5g/ 100mL, agar 2g/100mL, pH value 6.5~7.5;
In fluid nutrient medium II, 1.5g/100mL containing glucose, yeast extract 0.5g/100mL, peptone 1g/100mL, chlorine Change sodium 0.5g/100mL;
In fermentation medium II, 3g/100mL containing glucose, yeast extract 1.5g/100mL, (NH4)2SO40.5g/100mL, Sodium citrate 0.2g/100mL, magnesium sulfate 0.02g/100mL.
(3) bacillus amyloliquefaciens CGMCC No.1.7463 are taken, is inoculated in solid medium, activated culture, activation Condition is:37 DEG C, activation culture 48h is obtained activation bacillus amyloliquefaciens;Then activation bacillus amyloliquefaciens are inoculated in Fluid nutrient medium III is enlarged culture;Amplification Culture condition is:Under rotary shaker 160rpm rotating speeds, 30 DEG C of cultures 48h;The bacillus amyloliquefaciens seed that will be enlarged by culture is inoculated in fermentation medium III by the 10% of fermentating liquid volume, Under rotary shaker 160rpm rotating speeds, after 30 DEG C of culture 72h, bacillus amyloliquefaciens preparation, bacillus amyloliquefaciens body is obtained Concentration is 9.0 × 109cfu/mL。
Wherein, in solid medium III, 1g/100mL containing tryptone, yeast extract 0.5g/100mL, sodium chloride 1g/ 100mL, agar 2g/100mL, pH value 6~8;
In fluid nutrient medium III, 2.5g/100mL containing glucose, yeast extract 0.2g/100mL, potassium dihydrogen phosphate 0.02g/ 100mL;
In fermentation medium III, molasses 1.5g/100mL, brown sugar 1.0g/100mL, yeast extract 1.5/100mL, corn pulp 1.5/100mL, potassium dihydrogen phosphate 0.02g/100mL, magnesium sulfate 0.01g/100mL.
(4) Bacillus subtillis CGMCC No.1.2162 are taken, is inoculated in solid medium, activated culture activates bar Part is:37 DEG C, activation culture 60h is obtained activation Bacillus subtillis;Then activation Bacillus subtillis is inoculated in liquid training Support base IV and be enlarged culture;Amplification Culture condition is:Under rotary shaker 150rpm rotating speeds, 37 DEG C of culture 48h;Will be enlarged by The Bacillus subtillis seed of culture is inoculated in fermentation medium IV by the 5% of fermentating liquid volume, in rotary shaker Under 180rpm rotating speeds, after 37 DEG C of culture 72h, Bacillus subtillis preparation is obtained, Bacillus subtillis bulk concentration is 8.0 × 109cfu/mL。
Wherein, in solid medium IV, 1g/100mL containing tryptone, yeast extract 0.5g/100mL, sodium chloride 1g/ 100mL, agar 2g/100mL, pH value 6~8;
In fluid nutrient medium IV, 2.5g/100mL containing glucose, yeast extract 0.2g/100mL, potassium dihydrogen phosphate 0.02g/ 100mL;
In fermentation medium IV, 2.0g/100mL containing molasses, brown sugar 1.5g/100mL, analysis for soybean powder 2.0g/100mL, corn Slurry 1.5g/100mL, potassium dihydrogen phosphate 0.02g/100mL.
(5) bacillus licheniformis CGMCC No.1.6510 are taken, is inoculated in solid medium, activated culture activates bar Part is:35 DEG C, activation culture 48h;Activation bacillus licheniformis are obtained;Then activation bacillus licheniformis are inoculated in liquid training Support base V and be enlarged culture;Amplification Culture condition is:Under rotary shaker 150rpm rotating speeds, 37 DEG C of culture 48h;Will be enlarged by The bacillus licheniformis seed of culture is inoculated in fermentation medium V by the 10% of fermentating liquid volume, in rotary shaker Under 160rpm rotating speeds, after 32 DEG C of culture 96h, bacillus licheniformis preparations is obtained, bacillus licheniformis cell concentration is 1.0 × 109cfu/mL。
Wherein, in solid medium V, 1g/100mL containing peptone, yeast extract 0.5g/100mL, sodium chloride 1g/100mL, Agar 2g/100mL, pH value 6~8;
In fluid nutrient medium V, 2.0g/100mL containing glycerine, yeast extract 0.5g/100mL, corn pulp 1.5g/100mL, phosphoric acid Potassium dihydrogen 0.02g/100mL;
In fermentation medium V, 2.0g/100mL containing glycerine, molasses 1.5/100mL, corn pulp 3.0g/100mL, analysis for soybean powder 1.5g/100mL, potassium dihydrogen phosphate 0.03g/100mL, magnesium sulfate 0.02g/100mL.
(6) extracting lactic acid galactococcus CGMCC No.1.3920, are inoculated in solid medium, activated culture, activation condition For:37 DEG C, activation culture 72h is obtained activation Lactococcus lactis;Then activation Lactococcus lactis are inoculated in fluid nutrient medium VI It is enlarged culture;Amplification Culture condition is:Under rotary shaker 150rpm rotating speeds, 35 DEG C of culture 72h;Will be enlarged by culture Lactococcus lactis seed is inoculated in fermentation medium VI by the 10% of fermentating liquid volume, under rotary shaker 50rpm rotating speeds, After 32 DEG C of culture 150h, Lactococcus lactis bacteria preparation is obtained, Lactococcus lactis cell concentration is 8.0 × 105cfu/mL。
Wherein, in solid medium VI, 0.5g/100mL containing beef extract, peptone 0.5g/100mL, yeast extract 0.5g/ 100mL, tomato juice 5g/100mL, glucose 1.0g/100mL, calcium bicarbonate 1.0g/100mL, agar 2g/100mL, pH value 4~ 6.5;
In fluid nutrient medium VI, 2.0g/100mL containing glucose, yeast extract 0.5g/100mL, corn pulp 1.5g/100mL, Potassium dihydrogen phosphate 0.02g/100mL, calcium bicarbonate 1.0g/100mL;
In fermentation medium VI, 2.5g/100mL containing glucose, yeast extract 2.0g/100mL, corn pulp 3.0/100mL, phosphorus Acid dihydride potassium 0.02g/100mL, calcium bicarbonate 1.0g/100mL, citric acid 0.5g/100mL.
(7) hydrogenlike silicon ion CGMCC No.1.2174 are taken, is inoculated in solid medium, activated culture, activation condition For:35 DEG C, activation culture 72h;Activation hydrogenlike silicon ion is obtained;Then activation hydrogenlike silicon ion is inoculated in fluid nutrient medium VII is enlarged culture;Amplification Culture condition is:Under rotary shaker 150rpm rotating speeds, 32 DEG C of culture 72h;Will be enlarged by training Foster hydrogenlike silicon ion seed is inoculated in fermentation medium VII by the 10% of fermentating liquid volume, in rotary shaker 150rpm Under rotating speed, after 32 DEG C of culture 96h, hydrogenlike silicon ion preparation is obtained, hydrogenlike silicon ion cell concentration is 9.0 × 107cfu/mL。
Wherein, in solid medium VII, 0.5g/100mL containing beef extract, peptone 0.5g/100mL, yeast extract 0.5g/ 100mL, agar 2g/100mL, pH value 6.5~7.5;
In fluid nutrient medium VII, 2.0g/100mL containing glucose, corn pulp 1.5g/100mL, ammonium sulfate 1.0g/100mL, Sodium glutamate 0.2g/100mL, potassium dihydrogen phosphate 0.02g/100mL;
In fermentation medium VII, 3.0g/100mL containing glucose, corn pulp 2.0g/100mL, ammonium sulfate 1.5g g/ 100mL, sodium glutamate 1.5g/100mL, potassium dihydrogen phosphate 0.02g/100mL.
(8) alkali lake enlightening thatch Salmonella CGMCC No.1.6147 are taken, is inoculated in solid medium, activated culture, activate bar Part is:32 DEG C, activation culture 96h is obtained activation alkali lake enlightening thatch Salmonella;Then activation alkali lake enlightening thatch Salmonella is inoculated in liquid training Support base IIX and be enlarged culture;Amplification Culture condition is:Under rotary shaker 150rpm rotating speeds, 32 DEG C of culture 72h;To expand The alkali lake enlightening thatch Salmonella seed of big culture is inoculated in fermentation medium IIX by the 15% of fermentating liquid volume, in rotary shaker Under 50rpm rotating speeds, after 30 DEG C of culture 120h, alkali lake enlightening thatch Salmonella preparation is obtained, alkali lake enlightening thatch Salmonella cell concentration is 7.0 × 107cfu/mL。
Wherein, in solid medium IIX, 1g/100mL containing glucose, sodium acetate 0.2g/100mL, yeast extract 0.5g/ 100mL, ammonium chloride 0.25g/100mL, agar 2g/100mL, pH value 6.5~7.5;
In fluid nutrient medium IIX, 1g/100mL containing glucose, sodium acetate 0.5g/100mL, yeast extract 0.5g/100mL, chlorine Change ammonium 0.5g/100mL, potassium nitrate 0.2g/100mL, magnesium sulfate 0.02g/100mL, dipotassium hydrogen phosphate 0.05g/100mL;
Described fermentation medium IIX components are as follows:Glucose 2.0g/100mL, sodium acetate 1.5g/100mL, yeast extract 1.0g/100mL, ammonium chloride 1.5g/100mL, potassium nitrate 0.2g/100mL, magnesium sulfate 0.03g/100mL, dipotassium hydrogen phosphate 0.02g/100mL, sodium potassium tartrate tetrahydrate 0.2g/100mL.
(9) Rhodopseudomonas palustris CGMCC No.1.2351 are taken, is inoculated in solid medium IX, activated culture is living Change condition is:32 DEG C, activation culture 96h is obtained activation Rhodopseudomonas palustris;Then will activation Rhodopseudomonas palustris inoculation Culture is enlarged in fluid nutrient medium IX, Amplification Culture condition is:Under rotary shaker 50rpm rotating speeds, 32 DEG C of cultures 96h;The Rhodopseudomonas palustris seed that will be enlarged by culture is inoculated in fermentation medium IX by the 15% of fermentating liquid volume, in rotation Under rotatable shaking table 50rpm rotating speeds, after 32 DEG C of culture 160h, Rhodopseudomonas palustris preparation, Rhodopseudomonas palustris thalline is obtained Concentration is 5.0 × 107cfu/mL。
Wherein, in solid medium IX, 1g/100mL containing glucose, sodium acetate 0.2g/100mL, yeast extract 0.5g/ 100mL, biotin 0.01g/100mL, magnesium sulfate 0.02g/100mL, agar 2g/100mL, pH value 6.5~7.5;
In fluid nutrient medium IX, 1.0g/100mL containing glucose, sodium acetate 1.0g/100mL, yeast extract 0.5g/100mL, Ammonium chloride 0.5g/100mL, magnesium sulfate 0.05g/100mL, dipotassium hydrogen phosphate 0.02g/100mL;
In fermentation medium IX, 1.5g/100mL containing glucose, sodium acetate 1.0g/100mL, yeast extract 1.5g/100mL, Ammonium chloride 0.5g/100mL, magnesium sulfate 0.05g/100mL, dipotassium hydrogen phosphate 0.02g/100mL.
(10) by 15 parts of pseudomonad preparation, 10 parts of acinetobacter calcoaceticus preparation, step obtained in step (2) obtained in step (1) Suddenly 8 parts of bacillus amyloliquefaciens preparation obtained in (3), 12 parts of Bacillus subtillis preparation, step (5) obtained in step (4) are made 8 parts of bacillus licheniformis preparation, 15 parts of Lactococcus lactis bacteria preparation, class ball obtained in step (7) obtained in step (6) it is red thin 12 parts of bacteria preparation, 10 parts of alkali lake enlightening thatch Salmonella preparation obtained in step (8) and Rhodopseudomonas palustris preparation obtained in step (9) 10 parts of mixing, are obtained complex micro organism fungicide, and 7.5 × 10 are approximately equal to containing viable count10cfu/mL。
Embodiment 3
Application of the complex micro organism fungicide in town and country river sewage in-situ immobilization
Suburb of Shanghai river course, river is in black, distributes strong stink, and COD, ammonia nitrogen and total phosphorus are exceeded.Taken from the river course 2L water samples, add liquid composite microbial microbial inoculum 2mL, every three days with microbial inoculum once, the Zhou Tianhou of continuous dosing three, measurement result table Bright, water body COD drops to 15.3mg/L by delivering the 265mg/L before microorganism;Ammonia-nitrogen content is by under preprosthetic 16.8mg/L It is down to 0.69mg/L;Total nitrogen drops to 0.97 by 31.53mg/L;Total phosphorus drops to 0.23 by 2.82mg/L, the water body after reparation People's Republic of China's water environment quality standard V class water standards are reached.Be demonstrated by obvious water remediation effect (see Table 1)
Repairing effect of the complex micro organism fungicide of table 1 to river sewage
COD(mg/L) NH3-N(mg/L) Total nitrogen (mg/L) Total phosphorus (mg/L)
River sewage before processing 265 16.8 31.53 2.82
Plus after microbial bacterial agent treatment 15.3 0.69 0.97 0.23
Clearance 94.22% 95.89% 96.23% 91.84%
The above is only the preferred embodiment of the present invention, and protection scope of the present invention is not limited merely to above-mentioned implementation Example.All technical schemes belonged under thinking of the present invention belong to protection scope of the present invention.It is noted that for the art Those of ordinary skill for, improvements and modifications under the premise without departing from the principles of the invention, these improvements and modifications also should It is considered as protection scope of the present invention.

Claims (10)

1. a kind of complex micro organism fungicide, it is characterised in that the complex micro organism fungicide includes pseudomonad preparation, non-lever Bacteria preparation, bacillus amyloliquefaciens preparation, Ko subtilis bar preparation, bacillus licheniformis preparation, Lactococcus lactis bacteria preparation, class ball Red bacteria preparation, alkali lake enlightening thatch Salmonella preparation and Rhodopseudomonas palustris preparation.
2. complex micro organism fungicide according to claim 1, it is characterised in that pseudomonad is to be preserved in China Microbiological Culture presevation administration committee common micro-organisms center, deposit number is the pseudomonad of CGMCC No.13433.
3. complex micro organism fungicide according to claim 1, it is characterised in that each component in the complex micro organism fungicide Parts by volume be:5~15 parts of pseudomonad preparation, 5~15 parts of acinetobacter calcoaceticus preparation, 5~15 parts of bacillus amyloliquefaciens preparation, 5~15 parts of bacillus subtilis formulation, 5~15 parts of bacillus licheniformis preparation, 5~15 parts of Lactococcus lactis bacteria preparation, class ball are red 5~15 parts of bacteria preparation, 5~15 parts of alkali lake enlightening thatch Salmonella preparation, 5~15 parts of Rhodopseudomonas palustris preparation.
4. complex micro organism fungicide according to claim 1, it is characterised in that in the complex micro organism fungicide, total bacterium Fall number >=6.0 × 1010cfu/mL。
5. the complex micro organism fungicide according to any one of Claims 1 to 4, it is characterised in that acinetobacter calcoaceticus are not lever Bacterium CGMCC No.1.8587, bacillus amyloliquefaciens are bacillus amyloliquefaciens CGMCC No.1.7463, Bacillus subtillis It is Bacillus subtillis CGMCC No.1.2162, bacillus licheniformis are bacillus licheniformis CGMCC No.1.6510, lactic acid Galactococcus is Lactococcus lactis CGMCC No.1.3920, and hydrogenlike silicon ion is hydrogenlike silicon ion CGMCC No.1.2174, alkali lake Enlightening thatch Salmonella is alkali lake enlightening thatch Salmonella CGMCC No.1.6147, and Rhodopseudomonas palustris is Rhodopseudomonas palustris CGMCC No.1.2351。
6. a kind of preparation method of complex micro organism fungicide as described in any one of Claims 1 to 5, comprises the following steps:
(1) pseudomonad is inoculated in solid slope culture medium I and is activated, activation pseudomonad is obtained;Then will activation Pseudomonad is inoculated in fluid nutrient medium I and is enlarged culture;It is inoculated in fermentation medium I, fermented culture is obtained bacterium Bulk concentration is not less than 3.0 × 109The pseudomonad preparation of cfu/mL;
(2) acinetobacter calcoaceticus are inoculated in solid slope culture medium II and are activated, activation acinetobacter calcoaceticus are obtained;Then will activation Acinetobacter calcoaceticus are inoculated in fluid nutrient medium II and are enlarged culture;It is inoculated in fermentation medium II, fermented culture is obtained Cell concentration is not less than 5.0 × 107The acinetobacter calcoaceticus preparation of cfu/mL;
(3) bacillus amyloliquefaciens are inoculated in solid slope culture medium III and are activated, activation solution starch gemma bar is obtained Bacterium;Then activation bacillus amyloliquefaciens are inoculated in fluid nutrient medium III and are enlarged culture;It is inoculated in fermentation medium In III, fermented culture is obtained cell concentration and is not less than 8.0 × 109The bacillus amyloliquefaciens preparation of cfu/mL;
(4) Bacillus subtillis is inoculated in solid slope culture medium IV and is activated, activation Bacillus subtillis is obtained;So Activation Bacillus subtillis is inoculated in fluid nutrient medium IV afterwards and is enlarged culture;It is inoculated in fermentation medium IV, passes through Fermented and cultured is obtained cell concentration and is not less than 6.0 × 109The Bacillus subtillis preparation of cfu/mL;
(5) bacillus licheniformis are inoculated in solid slope culture medium V and are activated, activation bacillus licheniformis are obtained;So Activation bacillus licheniformis are inoculated in fluid nutrient medium V afterwards and are enlarged culture;It is inoculated in fermentation medium V, through hair Ferment culture is obtained cell concentration and is not less than 8.0 × 108The bacillus licheniformis preparation of cfu/mL;
(6) Lactococcus lactis are inoculated in solid slope culture medium VI and are activated, activation Lactococcus lactis are obtained;Then will Activation Lactococcus lactis are inoculated in fluid nutrient medium VI and are enlarged culture;It is inoculated in fermentation medium VI, fermented training Support prepared cell concentration and be not less than 7.0 × 105The Lactococcus lactis bacteria preparation of cfu/mL;
(7) hydrogenlike silicon ion is inoculated in solid slope culture medium VII and is activated, activation hydrogenlike silicon ion is obtained;Then Activation hydrogenlike silicon ion is inoculated in fluid nutrient medium VII and is enlarged culture;It is inoculated in fermentation medium VII, through hair Ferment culture is obtained cell concentration and is not less than 8.0 × 107The hydrogenlike silicon ion preparation of cfu/mL;
(8) alkali lake enlightening thatch Salmonella is inoculated in solid slope culture medium IIX and is activated, activation alkali lake enlightening thatch Salmonella is obtained; Then activation alkali lake enlightening thatch Salmonella is inoculated in fluid nutrient medium IIX and is enlarged culture;It is inoculated in fermentation medium IIX In, fermented culture is obtained cell concentration and is not less than 6.0 × 107The alkali lake enlightening thatch Salmonella preparation of cfu/mL;
(9) Rhodopseudomonas palustris is inoculated in solid slope culture medium IX and is activated, the activation red false unit cell in marsh is obtained Bacterium;Then activation Rhodopseudomonas palustris is inoculated in fluid nutrient medium IX and is enlarged culture;It is inoculated in fermentation medium In IX, fermented culture is obtained cell concentration and is not less than 4.0 × 107The Rhodopseudomonas palustris preparation of cfu/mL;
(10) by pseudomonad preparation, the obtained solution of acinetobacter calcoaceticus preparation, step (3) obtained in step (2) obtained in step (1) Bacillus amyloliquefacienses preparation, Bacillus subtillis preparation obtained in step (4), bacillus licheniformis preparation obtained in step (5), Lactococcus lactis bacteria preparation, hydrogenlike silicon ion preparation, alkali lake enlightening thatch obtained in step (8) obtained in step (7) obtained in step (6) After Salmonella preparation and Rhodopseudomonas palustris preparation obtained in step (9) proportionally mix, complex micro organism fungicide is obtained.
7. the preparation method of complex micro organism fungicide according to claim 6, it is characterised in that the solid medium I In, 1g/100mL containing peptone, dusty yeast 1.5g/100mL, glucose 2g/100mL, dipotassium hydrogen phosphate 0.1g/100mL, agar 2g/100mL, pH value 6~8;In the solid medium II, 1.5g/100mL containing peptone, glucose 1g/100mL, sodium chloride 0.5g/100mL, agar 2g/100mL, pH value 6.5~7.5;In the solid medium III, 1g/100mL containing tryptone, Yeast extract 0.5g/100mL, sodium chloride 1g/100mL, agar 2g/100mL, pH value 6~8;In the solid medium IV, containing pancreas Peptone 1g/100mL, yeast extract 0.5g/100mL, sodium chloride 1g/100mL, agar 2g/100mL, pH value 6~8;The solid In culture medium V, 1g/100mL containing peptone, yeast extract 0.5g/100mL, sodium chloride 1g/100mL, agar 2g/100mL, pH value 6 ~8;In the solid medium VI, 0.5g/100mL containing beef extract, peptone 0.5g/100mL, yeast extract 0.5g/100mL, Tomato juice 5g/100mL, glucose 1.0g/100mL, calcium bicarbonate 1.0g/100mL, agar 2g/100mL, pH value 4~6.5;Institute In stating solid medium VII, 0.5g/100mL containing beef extract, peptone 0.5g/100mL, yeast extract 0.5g/100mL, agar 2g/100mL, pH value 6.5~7.5;In the solid medium IIX, 1g/100mL containing glucose, sodium acetate 0.2g/100mL, Yeast extract 0.5g/100mL, ammonium chloride 0.25g/100mL, agar 2g/100mL, pH value 6.5~7.5;The solid medium IX In, 1g/100mL containing glucose, sodium acetate 0.2g/100mL, yeast extract 0.5g/100mL, biotin 0.01g/100mL, sulphur Sour magnesium 0.02g/100mL, agar 2g/100mL, pH value 6.5~7.5.
8. the preparation method of complex micro organism fungicide according to claim 7, it is characterised in that the fluid nutrient medium I In, 1.5g/100mL containing glucose, yeast extract 0.5g/100mL, peptone 1g/100mL, potassium dihydrogen phosphate 0.05g/100mL, Magnesium sulfate 0.04g/100mL;In the fluid nutrient medium II, 1.5g/100mL containing glucose, yeast extract 0.5g/100mL, albumen Peptone 1g/100mL, sodium chloride 0.5g/100mL;In fluid nutrient medium III, 2.5g/100mL containing glucose, yeast extract 0.2g/ 100mL, potassium dihydrogen phosphate 0.02g/100mL;In the fluid nutrient medium IV, 2.5g/100mL containing glucose, yeast extract 0.2g/ 100mL, potassium dihydrogen phosphate 0.02g/100mL;In the fluid nutrient medium V, 2.0g/100mL containing glycerine, yeast extract 0.5g/ 100mL, corn pulp 1.5g/100mL, potassium dihydrogen phosphate 0.02g/100mL;In the fluid nutrient medium VI, 2.0g/ containing glucose 100mL, yeast extract 0.5g/100mL, corn pulp 1.5g/100mL, potassium dihydrogen phosphate 0.02g/100mL, calcium bicarbonate 1.0g/ 100mL;In the fluid nutrient medium VII, 2.0g/100mL containing glucose, corn pulp 1.5g/100mL, ammonium sulfate 1.0g/ 100mL, sodium glutamate 0.2g/100mL, potassium dihydrogen phosphate 0.02g/100mL;In the fluid nutrient medium IIX, containing glucose 1g/100mL, sodium acetate 0.5g/100mL, yeast extract 0.5g/100mL, ammonium chloride 0.5g/100mL, potassium nitrate 0.2g/100mL, Magnesium sulfate 0.02g/100mL, dipotassium hydrogen phosphate 0.05g/100mL;In the fluid nutrient medium IX, 1.0g/ containing glucose 100mL, sodium acetate 1.0g/100mL, yeast extract 0.5g/100mL, ammonium chloride 0.5g/100mL, magnesium sulfate 0.05g/100mL, phosphorus Sour hydrogen dipotassium 0.02g/100mL.
9. the preparation method of the complex micro organism fungicide according to any one of claim 6~8, it is characterised in that the hair In ferment culture medium I, containing 0.5~5g/100mL of glucose, 0.5~4g/100mL of yeast extract, 1.0~6g/100mL of analysis for soybean powder, phosphorus Acid dihydride 0.01~0.1g/100mL of potassium, 0.01~0.1g/100mL of magnesium sulfate;In the fermentation medium II, containing glucose 0.5~5g/100mL, yeast extract 0.3~3g/100mL, (NH4)2SO40.1~2.0g/100mL, 0.1~1g/ of sodium citrate 100mL, 0.01~0.5g/100mL of magnesium sulfate;In the fermentation medium III, containing 0.5~5.0g/100mL of molasses, brown sugar 0.3~3.0g/100mL, 0.2~2.0/100mL of yeast extract, 0.5~5.0/100mL of corn pulp, potassium dihydrogen phosphate 0.01~ 0.05g/100mL, 0.005~0.05g/100mL of magnesium sulfate;In the fermentation medium IV, containing 0.5~5.0g/ of molasses 100mL, 0.5~5.0g/100mL of brown sugar, 0.5~3.0g/100mL of analysis for soybean powder, 1.0~5.0g/100mL of corn pulp, di(2-ethylhexyl)phosphate 0.01~0.1g/100mL of hydrogen potassium;In the fermentation medium V, containing 1.0~5.0g/100mL of glycerine, molasses 1.0~5.0/ 100mL, 1.0~5.0g/100mL of corn pulp, 0.5~3.0g/100mL of analysis for soybean powder, 0.01~0.1g/100mL of potassium dihydrogen phosphate, 0.01~0.1g/100mL of magnesium sulfate;In the fermentation medium VI, containing 1.0~5.0g/100mL of glucose, yeast extract 1.0~ 5.0g/100mL, 1.0~5.0/100mL of corn pulp, 0.01~0.1g/100mL of potassium dihydrogen phosphate, 0.5~2.0g/ of calcium bicarbonate 100mL, 0.2~2.0g/100mL of citric acid;In the fermentation medium, containing 1.0~5.0g/100mL of glucose, corn pulp 1.0~5.0g/100mL, 1.0~5.0g/100mL of ammonium sulfate, 0.1~1.5g/100mL of sodium glutamate, potassium dihydrogen phosphate 0.01 ~0.1g/100mL;In the fermentation medium IIX, containing 1.0~5.0g/100mL of glucose, 0.5~2.0g/ of sodium acetate 100mL, 1.0~5.0g/100mL of yeast extract, 0.5~2.0g/100mL of ammonium chloride, 0.05~0.5g/100mL of potassium nitrate, sulfuric acid 0.01~0.1g/100mL of magnesium, 0.01~0.1g/100mL of dipotassium hydrogen phosphate, 0.1~1.0g/100mL of sodium potassium tartrate tetrahydrate;It is described In fermentation medium IX, containing 0.2~2.0g/100mL of glucose, 0.2~2.0g/100mL of sodium acetate, 0.2~2.0g/ of yeast extract 100mL, 0.2~2.0g/100mL of ammonium chloride, 0.01~0.1g/100mL of magnesium sulfate, 0.01~0.1g/ of dipotassium hydrogen phosphate 100mL。
10. as described in a kind of complex micro organism fungicide or any one of claim 6~9 as described in any one of Claims 1 to 5 The application of complex micro organism fungicide prepared by the preparation method of complex micro organism fungicide in the river sewage in-situ immobilization of town and country.
CN201710304523.9A 2017-05-03 2017-05-03 Complex micro organism fungicide and its preparation method and application Pending CN106906170A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710304523.9A CN106906170A (en) 2017-05-03 2017-05-03 Complex micro organism fungicide and its preparation method and application

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710304523.9A CN106906170A (en) 2017-05-03 2017-05-03 Complex micro organism fungicide and its preparation method and application

Publications (1)

Publication Number Publication Date
CN106906170A true CN106906170A (en) 2017-06-30

Family

ID=59210357

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710304523.9A Pending CN106906170A (en) 2017-05-03 2017-05-03 Complex micro organism fungicide and its preparation method and application

Country Status (1)

Country Link
CN (1) CN106906170A (en)

Cited By (24)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107354105A (en) * 2017-07-06 2017-11-17 安徽瑞驰兰德生物科技有限公司 A kind of complex microbial inoculum and preparation method thereof and the system for administering sewage
CN108220203A (en) * 2018-03-06 2018-06-29 上海海洋大学 A kind of fermentation medium of hydrogenlike silicon ion
CN108342346A (en) * 2018-05-14 2018-07-31 中国科学院生态环境研究中心 One plant of Meng Shi pseudomonad and its application
CN108531432A (en) * 2018-05-14 2018-09-14 大江环境股份有限公司 A kind of application of the microbial inoculum comprising Meng Shi pseudomonads in purifying sulfurous gas
CN108795829A (en) * 2018-07-11 2018-11-13 金福赛(北京)生物科技有限公司 Bacillus subtilis and its application in microbial inoculum and pork pig feed
CN108823121A (en) * 2018-06-04 2018-11-16 江西省林业科学院 A kind of complex microbial inoculum and application method promoting camphor tree growth of seedling
CN109055252A (en) * 2017-11-13 2018-12-21 鼎正新兴生物技术(天津)有限公司 A kind of heterotrophic nitrification-aerobic denitrification complex microorganism preparations and preparation method thereof
CN109205795A (en) * 2017-12-21 2019-01-15 向勇 A kind of compound nitrifier and its production method
CN109420671A (en) * 2017-08-29 2019-03-05 中国石油化工股份有限公司 Soil remediation composition and application and geobiont repair method
CN109576184A (en) * 2018-12-25 2019-04-05 重庆融极环保工程有限公司 A kind of complex microbial inoculum for waste water of basic printing and dyeing processing
CN109678614A (en) * 2019-02-28 2019-04-26 广西地源之本生物科技有限公司 A kind of biology-Organic-inorganic composite nutrient solution and preparation method thereof
CN109897803A (en) * 2019-03-22 2019-06-18 北京好实沃生物技术有限公司 A kind of aquatic products probiotics and its preparation method and application
CN110106106A (en) * 2019-04-08 2019-08-09 云南忱朋科技发展有限公司 Complex micro organism fungicide and its application in strawberry cultivating
CN110468081A (en) * 2019-09-17 2019-11-19 湖南艾布鲁环保科技股份有限公司 Composite bacteria agent and its preparation method and application
CN110846254A (en) * 2019-11-27 2020-02-28 深圳大学 Compound microbial agent for denitrification and preparation method and application thereof
CN111548974A (en) * 2020-06-04 2020-08-18 中原环保股份有限公司 Microbial preparation for artificial lake water, preparation method and application of microbial preparation for water treatment
CN111925955A (en) * 2020-07-02 2020-11-13 河海大学 Composite solid particles prepared from autotrophic and heterotrophic denitrifying bacteria and preparation method thereof
CN111961624A (en) * 2020-08-25 2020-11-20 四川省食品发酵工业研究设计院 Compound microbial agent for efficiently degrading nitrogen and phosphorus and preparation method and application thereof
CN113186132A (en) * 2021-05-07 2021-07-30 广东丽豪生物农业有限公司 Microbial agent suitable for corn planting and application
CN113308393A (en) * 2021-04-20 2021-08-27 上田环境修复有限公司 Preparation for degrading ammonia nitrogen and total nitrogen and preparation method thereof
CN113913324A (en) * 2021-09-01 2022-01-11 郑州轻工业大学 Composite microbial inoculum for efficient deodorization of biological filter and preparation method thereof
CN113998832A (en) * 2020-11-02 2022-02-01 呼伦贝尔东北阜丰生物科技有限公司 Method for advanced treatment of total nitrogen in amino acid wastewater
CN114437956A (en) * 2020-11-05 2022-05-06 中石化石油工程技术服务有限公司 Microbial composition for efficiently degrading human excrement and application thereof
CN117417061A (en) * 2023-12-19 2024-01-19 临沂市环境保护科学研究所有限公司 Composite treating agent for high-concentration ammonia nitrogen sewage and preparation method thereof

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102815792A (en) * 2012-04-01 2012-12-12 浙江绿凯环保科技有限公司 Microbe-enzyme composite preparation used for restoring water in urban and rural polluted river, and its preparation method
CN105779344A (en) * 2016-03-29 2016-07-20 江苏蓝星化工环保股份有限公司 Composite microbial agent
CN106047772A (en) * 2016-08-09 2016-10-26 湖北凌卓生物工程有限公司 Composite microbial agent for treating high-ammonia-nitrogen sewage and preparation method and application thereof
CN106222105A (en) * 2016-07-28 2016-12-14 唐清池 A kind of process sanitary sewage complex microorganism preparations and preparation method thereof
CN106587559A (en) * 2016-12-29 2017-04-26 王恩琦 Sludge anaerobic digestion method

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102815792A (en) * 2012-04-01 2012-12-12 浙江绿凯环保科技有限公司 Microbe-enzyme composite preparation used for restoring water in urban and rural polluted river, and its preparation method
CN105779344A (en) * 2016-03-29 2016-07-20 江苏蓝星化工环保股份有限公司 Composite microbial agent
CN106222105A (en) * 2016-07-28 2016-12-14 唐清池 A kind of process sanitary sewage complex microorganism preparations and preparation method thereof
CN106047772A (en) * 2016-08-09 2016-10-26 湖北凌卓生物工程有限公司 Composite microbial agent for treating high-ammonia-nitrogen sewage and preparation method and application thereof
CN106587559A (en) * 2016-12-29 2017-04-26 王恩琦 Sludge anaerobic digestion method

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
刘立立等: "好氧反硝化细菌LKX-1的分离、鉴定及初步应用研究", 《山东农业科学》 *
郭艳丽等: "一株轻度嗜盐反硝化菌的分离鉴定及特性", 《应用与环境生物学报》 *

Cited By (33)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107354105A (en) * 2017-07-06 2017-11-17 安徽瑞驰兰德生物科技有限公司 A kind of complex microbial inoculum and preparation method thereof and the system for administering sewage
CN109420671A (en) * 2017-08-29 2019-03-05 中国石油化工股份有限公司 Soil remediation composition and application and geobiont repair method
CN109055252A (en) * 2017-11-13 2018-12-21 鼎正新兴生物技术(天津)有限公司 A kind of heterotrophic nitrification-aerobic denitrification complex microorganism preparations and preparation method thereof
CN109205795A (en) * 2017-12-21 2019-01-15 向勇 A kind of compound nitrifier and its production method
CN108220203A (en) * 2018-03-06 2018-06-29 上海海洋大学 A kind of fermentation medium of hydrogenlike silicon ion
CN108220203B (en) * 2018-03-06 2021-03-02 上海海洋大学 Fermentation medium of rhodobacter sphaeroides and application of fermentation medium in fermentation production of rhodobacter sphaeroides
CN108531432A (en) * 2018-05-14 2018-09-14 大江环境股份有限公司 A kind of application of the microbial inoculum comprising Meng Shi pseudomonads in purifying sulfurous gas
CN108342346A (en) * 2018-05-14 2018-07-31 中国科学院生态环境研究中心 One plant of Meng Shi pseudomonad and its application
CN108531432B (en) * 2018-05-14 2020-09-29 大江环境股份有限公司 Application of microbial inoculum containing pseudomonas monteilii in purifying sulfur-containing gas
CN108342346B (en) * 2018-05-14 2019-12-17 中国科学院生态环境研究中心 Pseudomonas monteilii and application thereof
CN108823121A (en) * 2018-06-04 2018-11-16 江西省林业科学院 A kind of complex microbial inoculum and application method promoting camphor tree growth of seedling
CN108823121B (en) * 2018-06-04 2021-09-07 江西省林业科学院 Microbial compound inoculant for promoting growth of camphor tree seedlings and use method
CN108795829A (en) * 2018-07-11 2018-11-13 金福赛(北京)生物科技有限公司 Bacillus subtilis and its application in microbial inoculum and pork pig feed
CN108795829B (en) * 2018-07-11 2021-07-06 金福赛(北京)生物科技有限公司 Bacillus subtilis and application thereof in microbial inoculum and pork pig feed
CN109576184A (en) * 2018-12-25 2019-04-05 重庆融极环保工程有限公司 A kind of complex microbial inoculum for waste water of basic printing and dyeing processing
CN109678614A (en) * 2019-02-28 2019-04-26 广西地源之本生物科技有限公司 A kind of biology-Organic-inorganic composite nutrient solution and preparation method thereof
CN109897803A (en) * 2019-03-22 2019-06-18 北京好实沃生物技术有限公司 A kind of aquatic products probiotics and its preparation method and application
CN109897803B (en) * 2019-03-22 2021-02-02 北京好实沃生物技术有限公司 Aquatic probiotic and preparation method and application thereof
CN110106106A (en) * 2019-04-08 2019-08-09 云南忱朋科技发展有限公司 Complex micro organism fungicide and its application in strawberry cultivating
CN110468081A (en) * 2019-09-17 2019-11-19 湖南艾布鲁环保科技股份有限公司 Composite bacteria agent and its preparation method and application
CN110846254A (en) * 2019-11-27 2020-02-28 深圳大学 Compound microbial agent for denitrification and preparation method and application thereof
CN111548974A (en) * 2020-06-04 2020-08-18 中原环保股份有限公司 Microbial preparation for artificial lake water, preparation method and application of microbial preparation for water treatment
CN111925955A (en) * 2020-07-02 2020-11-13 河海大学 Composite solid particles prepared from autotrophic and heterotrophic denitrifying bacteria and preparation method thereof
CN111961624A (en) * 2020-08-25 2020-11-20 四川省食品发酵工业研究设计院 Compound microbial agent for efficiently degrading nitrogen and phosphorus and preparation method and application thereof
CN111961624B (en) * 2020-08-25 2023-05-16 四川省食品发酵工业研究设计院有限公司 Composite microbial agent for efficiently degrading nitrogen and phosphorus as well as preparation method and application thereof
CN113998832A (en) * 2020-11-02 2022-02-01 呼伦贝尔东北阜丰生物科技有限公司 Method for advanced treatment of total nitrogen in amino acid wastewater
CN114437956A (en) * 2020-11-05 2022-05-06 中石化石油工程技术服务有限公司 Microbial composition for efficiently degrading human excrement and application thereof
CN113308393A (en) * 2021-04-20 2021-08-27 上田环境修复有限公司 Preparation for degrading ammonia nitrogen and total nitrogen and preparation method thereof
CN113186132A (en) * 2021-05-07 2021-07-30 广东丽豪生物农业有限公司 Microbial agent suitable for corn planting and application
CN113913324A (en) * 2021-09-01 2022-01-11 郑州轻工业大学 Composite microbial inoculum for efficient deodorization of biological filter and preparation method thereof
CN113913324B (en) * 2021-09-01 2023-06-30 郑州轻工业大学 Composite microbial inoculant for efficient deodorization of biological filter and preparation method thereof
CN117417061A (en) * 2023-12-19 2024-01-19 临沂市环境保护科学研究所有限公司 Composite treating agent for high-concentration ammonia nitrogen sewage and preparation method thereof
CN117417061B (en) * 2023-12-19 2024-03-01 临沂市环境保护科学研究所有限公司 Composite treating agent for high-concentration ammonia nitrogen sewage and preparation method thereof

Similar Documents

Publication Publication Date Title
CN106906170A (en) Complex micro organism fungicide and its preparation method and application
CN102924134B (en) Alga microorganism fertilizer agent and preparation method thereof
CN105420147A (en) Compound microbial preparation for treating black and odorous rivers through strengthened calcium nitrate
CN104667320B (en) Composite microbial deodorant for treating household garbage and preparation method of deodorant
CN110331105A (en) A kind of sewage treatment composite bacteria agent and preparation method thereof
CN108165509B (en) Compound micro-ecological preparation and preparation method thereof for the black smelly water harnessing in river
CN102286376B (en) Microbial inoculum for high-efficiency fermenting bed and preparation method thereof
CN105368745A (en) Composite microbial preparation for treating black and odorous river and preparation method thereof
CN104293694A (en) Preparation method for sludge aerobic composting composite inoculum
CN104178433B (en) A kind of complex microorganism preparations of Urban River Water pollution control and preparation method thereof
CN106520627A (en) Microbial sludge deodorizer and preparation method thereof
CN104152377B (en) The aerobic denitrifying bacteria of heavy metal tolerance and application thereof
CN103205382A (en) Microbial agent for purifying river wastewater and preparation method of microbial agent
CN103695317B (en) There is the production method of the efficient phosphate-solubilizing penicillium oxalicum microbial inoculum of heavy metal tolerance characteristic
CN106745828A (en) A kind of broad-spectrum biological preparation administered for black and odorous water and its application method
CN105132300A (en) Method for preparing natural water ecological purification microbial inoculum
CN103937695A (en) Composite biological bacterial agent for treating livestock and poultry breeding wastewater and manufacturing method thereof
CN104017754A (en) Microbial water purifying agent and preparation method thereof
CN106987536A (en) Complex micro organism fungicide for river regulation and its preparation method and application
CN102021118A (en) Preparation method of liquid inoculant of aboriginal probiotic bacillus megaterium, bacillus mucilaginosus and azotobacter chroococcum
CN106635883A (en) Composite microbial preparation for treating watercourse organic matter
CN104787899A (en) Bacterial inhibition type water purifier for marine aquaculture and preparation method thereof
CN103642703B (en) There is the production method of the efficient phosphate-solubilizing aspergillus japonicus microbial inoculum of heavy metal tolerance characteristic
CN106187331A (en) One utilizes fowl and animal excrement to prepare complex microorganism ecology bacterial manure and method thereof
CN102745821B (en) Compound microorganism bacterium agent used for sludge reduction, 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
CB02 Change of applicant information
CB02 Change of applicant information

Address after: 213000 2188 Longcheng Road, Zhong Lou District, Changzhou, Jiangsu

Applicant after: Shanda Environmental Restoration Co., Ltd.

Address before: 213000 No. 2188 Longcheng Avenue, Zhonglou District, Changzhou City, Jiangsu Province

Applicant before: SUNTIME ENVIRONMENTAL REMEDIATION CO., LTD.

RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20170630