CN108997034A - Decomposed starting agent of one kind and preparation method thereof - Google Patents
Decomposed starting agent of one kind and preparation method thereof Download PDFInfo
- Publication number
- CN108997034A CN108997034A CN201810910009.4A CN201810910009A CN108997034A CN 108997034 A CN108997034 A CN 108997034A CN 201810910009 A CN201810910009 A CN 201810910009A CN 108997034 A CN108997034 A CN 108997034A
- Authority
- CN
- China
- Prior art keywords
- decomposed
- starting
- major ingredient
- starting agent
- compound
- 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
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
- C05F17/20—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation using specific microorganisms or substances, e.g. enzymes, for activating or stimulating the treatment
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F11/00—Other organic fertilisers
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F3/00—Fertilisers from human or animal excrements, e.g. manure
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
- C12N1/00—Microorganisms, 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
- C12N1/14—Fungi; Culture media therefor
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
- C12N1/00—Microorganisms, 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
- C12N1/14—Fungi; Culture media therefor
- C12N1/16—Yeasts; Culture media therefor
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
- C12N1/00—Microorganisms, 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
- C12N1/20—Bacteria; Culture media therefor
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
Abstract
The present invention relates to a kind of decomposed starting agent and preparation method thereof, its raw material specifically includes that major ingredient, auxiliary material and composite microbial fermentation bacteria agent, a variety of composite bacterias such as the compound starting zymophyte, including bacillus, saccharomycete, Aspergillus and actinomyces are combined.After organic materials fermentation maturity abundant first, then numerous through scientific matching, mixing, starting, expansion again, keep functional microbial that there is certain amount and activity, peasant is allowed to use in most easy, easy-operating method, disposably reach expected fermentation, decompose, is decomposed, and has the effect of Releasing nutrient and diseases prevention suppression disease concurrently.Up to the decomposed starting agent.With starting, rapid, quick heating, constant temperature are stablized for decomposed starting agent of the present invention, the strong advantage of capacity of decomposition, and the characteristics of decomposed broad spectrum activity and tailored version can be carried out to gas chromatography material, the preparation method has easy to operate, it is easy to implement, the advantages that can be mass-produced and promote the use of.
Description
Technical field
The present invention relates to decomposing agent fields, in particular to a kind of decomposed starting agent and preparation method thereof.
Background technique
Organic materials is the general name of agricultural crop straw, agricultural production leftover bits and pieces or waste material, fowl and animal excrement, rubbish from cooking etc..
Currently, China has a large amount of organic materials because cannot get appropriate processing every year, and become agricultural, the serious pollution sources in rural area,
Urban and rural environment is influenced, brings huge pressure to ecological environment.Turn waste into wealth to organic materials, turn harm into good, to change
For that can provide organic fertilizer resource abundant for agricultural production, this processing technique is that current agricultural straw resource melts at hair
That manages is most simple and easy to do, and most effective harmless treatment mode can either eliminate pollution of a large amount of organic wastes to environment, again
Good organic fertilizer resource can be obtained, is conducive to green, Organic Farming, boosting rural economy development is to attack current, and benefit exists
It is long-range, benefit the key project of the people.
However traditional organic material composting technique is there are many drawbacks and technical bottleneck, limit organic material composting with
It promotes, wherein drawback includes: in decomposed technique
(1) the C/N ratio between different organic materials and nature difference are larger, can play decomposition strain and its
Suitable condition is also different, also lacks a kind of decomposing agent that can be used with wide spectrum at present, still needs in decomposed different organic materials
Different types of decomposing agent is used respectively, meanwhile, various decomposing agents are required than relatively severe condition, and competence exertion is best
Fermentation maturity effect.
(2) using decomposing agent processing organic materials when, troublesome operation sequence is generally required, the function of decomposing agent can be made
It can starting.
(3) traditional decomposing agent is when in use, also unreasonable often because use condition and method are undesirable, and leads
Cause effect undesirable.Although can need to prepare other objects when carrying out expanding numerous by expanding numerous uniformity to increase decomposing agent
Material, increases the technical difficulty of operation of user.
Therefore, this field urgently proposes a kind of easy to operate, decomposed uniform and can be carried out to gas chromatography material decomposed
Broad spectrum activity decomposing agent or decomposed starting agent.
In view of this, the present invention is specifically proposed.
Summary of the invention
The first object of the present invention is to provide a kind of decomposed starting agent, passes through bacillus, saccharomycete, mould and unwrapping wire
Working in coordination between bacterium, so that rapid, quick heating, constant temperature are stable with starting when decomposed for the decomposed starting agent
Advantage, and strong, the decomposed thorough broad spectrum activity feature to gas chromatography material progress capacity of decomposition；
Further, bacillus of the present invention, saccharomycete, mould and actinomyces are respectively bacillus subtilis, make
Brewer yeast, Trichoderma viride and mycobacteria have the function of synergy in the digest process of organic materials, can be into one
Step improves the decomposed effect of organic materials；
Further, a large amount of organic materials is added in decomposed starting agent of the present invention as major ingredient, so that the corruption
Ripe starting agent when in use can be evenly dispersed, avoids decomposed uneven, it is preferable that the organic materials is selected from stalk, agricultural production
Product leftover bits and pieces and dregs of beans, oil cake etc., have the advantages that it is from a wealth of sources, cheap, turn waste into wealth；
Further, the auxiliary material in decomposed starting agent of the present invention is selected from compound fertilizer, urea, phosphate fertilizer, potash fertilizer, lime,
Carbon-nitrogen ratio, carbon-phosphorus ratio, pH value and the moisture that the decomposed starting agent can effectively be adjusted, to be mentioned for compound starting function bacterium
For good startup environment.
The second object of the present invention is to provide the preparation method of aforementioned decomposed starting agent, and the method passes through decomposed and expand
Numerous to can be prepared by decomposed starting agent, method is simple, is easy to implement, can be mass-produced, meanwhile, decomposed operation can decompose major ingredient
At the nutriment for being easy to be utilized by microorganism, expand numerous so that startup function bacterium massive amplification, therefore, gained starting agent are using
When it is capable of fast starting, be brought rapidly up and maintain the stabilization of temperature.
In order to realize above-mentioned purpose of the invention, the following technical scheme is adopted:
The raw material of a kind of decomposed starting agent, the decomposed starting agent includes major ingredient, compound starting function bacterium and auxiliary material, described
Compound starting function bacterium includes bacillus, saccharomycete, mould and actinomyces.
The function bacterium of decomposed starting agent of the present invention includes bacillus, saccharomycete, mould and actinomyces.Wherein, bud
Spore bacillus can be rapidly heated and be proliferated in decomposed beginning, can extracellular proteinase, amylase etc., in fast decoupled material
Degradable organic matter provides good environment for saccharomycete, mould and the proliferation of actinomyces, plays the role of quick start.
And saccharomycete and mould start recovery, proliferation after heating and start after easily biodegradable organics consumption to cellulose, pectin
It is decomposed Deng hardly possible decomposing organic matter, discharges heat, maintain the stabilization of temperature.And actinomyces have high temperature resistant, alkaline-resisting advantage,
There can be good degradation to cellulose etc. in the decomposed middle and later periods, the vigor decline of saccharomycete and mould, thus
It realizes to the lasting decomposed of organic materials.The present invention utilizes the mutualism between bacillus, saccharomycete, mould and actinomyces
Select finally to obtain decomposed starting agent of the present invention with having complementary functions.It is different from existing decomposed starting agent, it is of the present invention
Decomposed starting agent all has good decomposed effect to a variety of different organic materials.Wherein, for labile fowl and animal excrement, originally
Invention mainly rapidly can be decomposed and be utilized to it using the bacillus in decomposing agent, yeast, mould and actinomyces
Carry out auxiliary decomposition；And for being difficult to the straw-like materials decomposed, decomposing agent of the present invention is carried out first with bacillus
Heating and initial breakdown, are then decomposed using saccharomycete and the mould substance difficult to degrade to cellulose family, finally, in yeast
After bacterium and the decline of mould vigor, the degradation and corruption that the actinomyces of high temperature resistant and alkali resistance are last to carry out such as celluloses are utilized
It is ripe.Therefore, decomposed starting agent of the present invention has broad spectrum activity, and the good decomposed effect of decomposition can be played to gas chromatography material
Fruit.
Preferably, in decomposed starting agent as described above, the bacillus, saccharomycete, mould and actinomyces difference
For bacillus subtilis, saccharomyces cerevisiae, Trichoderma viride and mycobacteria.
It is well known that the optimum growing condition of different microorganisms is different, and there is likely to be antagonism works between microorganism
A large amount of screening test is carried out with, applicant, has given up numerous technical effects and has not reached expected antimicrobial composition, finally people's will out
Material ground obtains compound starting function bacterium of the present invention: bacillus subtilis, saccharomyces cerevisiae, Trichoderma viride and mycobacteria.Institute
It states the mutualism of compound starting function bacterium, have complementary functions, so that decomposed starting agent of the present invention has good decomposition decomposed
Effect.
Preferably, described to make it when in use can be evenly dispersed and decomposed in decomposed starting agent as described above
A large amount of major ingredients are added in decomposed starting agent, specifically, the major ingredient, compound starting function bacterium and auxiliary material be respectively as follows: major ingredient 85~
97.5 mass parts, 1~7.5 mass parts of 2.5~10 mass parts of compound starting function bacterium and auxiliary material；
Bacillus in the compound starting function bacterium, saccharomycete, mould and actinomyces mass ratio be 5~10:2~4:
1~3:1~3.
Preferably, in decomposed starting agent as described above, the major ingredient, compound starting function bacterium and auxiliary material are respectively as follows:
90 mass parts of major ingredient, 4 mass parts of 6 mass parts of compound starting function bacterium and auxiliary material；
Bacillus in the compound starting function bacterium, saccharomycete, mould and actinomyces mass ratio be 5:3:2:2.
Preferably, in decomposed starting agent as described above, the content of organic matter >=40%, nitrogen content >=5%, phosphorus content >=
2%, potassium content >=3%, water content≤30%.
Preferably, in decomposed starting agent as described above, total living bacteria count >=20 of the compound starting function bacterium
Hundred million/g, the bacillus >=1,000,000,000/g, the saccharomycete >=300,000,000/g, the mould >=200,000,000/g, the unwrapping wire
Bacterium >=200,000,000/g.
Preferably, in decomposed starting agent as described above, the major ingredient is organic materials；Preferably, the major ingredient choosing
From stalk, agricultural byproduct, dregs of beans or oil cake；It is highly preferred that the major ingredient is stalk, agricultural byproduct and dregs of beans；Most
Preferably, the mass ratio of the stalk, agricultural byproduct and dregs of beans is 20~50:40~70:3~12.
Preferably, in decomposed starting agent as described above, the auxiliary material is selected from compound fertilizer, urea, phosphate fertilizer, potash fertilizer, stone
One of ash is a variety of.The wherein addition of above-mentioned auxiliary material, enough carbon-nitrogen ratios for effectively adjusting the decomposed starting agent, carbon phosphorus
Than, pH value and moisture, to provide good startup environment for compound starting function bacterium.
The invention further relates to a kind of methods for preparing aforementioned decomposed starting agent, and the method is by the major ingredient, auxiliary material and answers
The mixing of startup function bacterium is closed, it is numerous to get the decomposed starting agent by decomposed and expansion.
Preferably, in the method as described above for preparing decomposed starting agent, the method is specifically included: by the major ingredient
It is mixed after crushing with the auxiliary material, addition part compound starting function bacterium is decomposed to major ingredient progress, later, crushes decomposed
Object is added remaining compound starting function bacterium, is uniformly mixed, expand it is numerous, expand it is numerous after to get the decomposed starting agent.
Preferably, in the method for preparing decomposed starting agent as described above, the complex function starting bacterium being added when decomposed is
The 1/3~1/2 of its total weight, the compound starting function bacterium being added when expanding numerous are the 1/2~2/3 of its total weight.
Compared with prior art, the invention has the benefit that
(1) decomposed starting agent of the present invention have the advantages that starting rapidly, quick heating, temperature remain stable and can be with
Decomposed broad spectrum activity feature is carried out to gas chromatography material；Major ingredient in decomposed starting agent of the present invention can rise when in use
To evenly dispersed, decomposed non-uniform effect is avoided；The auxiliary material can effectively adjust it is described it is decomposed starting agent carbon-nitrogen ratio,
Carbon-phosphorus ratio, pH value and moisture, to provide good quick breeding environmental condition for compound starting function bacterium.
(2) preparation method of decomposed starting agent of the present invention can be prepared by decomposed starting agent, side by the way that decomposed and expansion is numerous
Method is simple, is easy to implement, can be mass-produced, meanwhile, major ingredient can be resolved into the battalion for being easy to be utilized by microorganism by decomposed operation
Substance is supported, expands numerous so that startup function bacterium massive amplification, therefore, gained starting agent has good living environment when in use,
Capable of fast starting, heating rapidly, and keeps stable temperature.
Detailed description of the invention
It, below will be to specific in order to illustrate more clearly of the specific embodiment of the invention or technical solution in the prior art
Embodiment or attached drawing needed to be used in the description of the prior art be briefly described, it should be apparent that, it is described below
Attached drawing is some embodiments of the present invention, for those of ordinary skill in the art, before not making the creative labor
It puts, is also possible to obtain other drawings based on these drawings.
Fig. 1 is temperature variations of decomposed starting agent during decomposed stalk described in embodiment 1.
Specific embodiment
Embodiment of the present invention is described in detail below in conjunction with embodiment, but those skilled in the art will
Understand, the following example is merely to illustrate the present invention, and is not construed as limiting the scope of the invention.It is not specified in embodiment specific
Condition person carries out according to conventional conditions or manufacturer's recommended conditions.Reagents or instruments used without specified manufacturer is
The conventional products obtained can be bought by city.
Embodiment 1
A kind of decomposed starting agent, is prepared from the following materials: 90 mass parts of major ingredient, 6 parts of compound starting function bacterium and auxiliary
4 parts of material；Wherein the major ingredient is stalk, agricultural byproduct and dregs of beans, mass ratio 7:11:1.5；The compound starting function
Energy bacterium is bacillus subtilis, saccharomyces cerevisiae, Trichoderma viride and mycobacteria, mass ratio 5:3:2:2；The auxiliary material is multiple
Hefei, urea, phosphate fertilizer, potash fertilizer and lime, mass ratio 1:1:1:1:5.
The preparation method of the decomposed starting agent is as follows: preparing the major ingredient, compound of mass fraction as described above respectively
Startup function bacterium and auxiliary material；The major ingredient is crushed, is uniformly mixed with auxiliary material, part compound starting function bacterium is added, mixing is equal
Even, decomposed 2 days, the additional amount of the compound starting function bacterium was the 1/3 of its total amount；Decomposed feed powder is broken, it is added remaining multiple
Startup function bacterium is closed, is uniformly mixed, expands numerous culture 3~5 days to get the decomposed starting agent.
Embodiment 2
Decomposed starting agent is prepared referring to 1 the method for embodiment, difference is only that: the major ingredient, compound starting function bacterium
Mass ratio with auxiliary material is 17:2:7.5；The mass ratio of stalk described in major ingredient, agricultural byproduct and dregs of beans is 20:7:3；It is multiple
The mass ratio for closing bacillus subtilis described in startup function bacterium, saccharomyces cerevisiae, Trichoderma viride and mycobacteria is 10:2:3:1；
The compound fertilizer, urea, phosphate fertilizer, potash fertilizer and lime, mass ratio 3:1:3:1:7；Compound starting function bacterium adds when decomposed
Dosage is the 1/2 of its total amount, and the decomposed time is 1.5 days, and expanding numerous time is 2 days.
Embodiment 3
Decomposed starting agent is prepared referring to 1 the method for embodiment, difference is only that: the major ingredient, compound starting function bacterium
Mass ratio with auxiliary material is 85:2.5:1；The mass ratio of stalk described in major ingredient, agricultural byproduct and dregs of beans is 50:40:12；
Bacillus subtilis described in compound starting function bacterium, saccharomyces cerevisiae, Trichoderma viride and mycobacteria mass ratio be 5:4:1:
3；The compound fertilizer, urea, phosphate fertilizer, potash fertilizer and lime, mass ratio 1:3:1:3:3；Compound starting function bacterium when decomposed
Additive amount is the 1/2 of its total amount, and the decomposed time is 3 days, and expanding numerous time is 3 days.
Comparative example 1
Decomposed starting agent is prepared referring to 1 the method for embodiment, difference is only that, is not added in the compound starting function bacterium
Add bacillus subtilis.
Comparative example 2
Ginseng makes 1 the method for embodiment and prepares decomposed starting agent, and difference is only that, is not added in the compound starting function bacterium
Add saccharomyces cerevisiae.
Comparative example 3
Ginseng makes 1 the method for embodiment and prepares decomposed starting agent, and difference is only that, is not added in the compound starting function bacterium
Add Trichoderma viride.
Comparative example 4
Ginseng makes 1 the method for embodiment and prepares decomposed starting agent, and difference is only that, is not added in the compound starting function bacterium
Add mycobacteria.
Comparative example 5
Decomposed starting agent is prepared referring to 1 the method for embodiment, difference is only that, substituted with bacillus amyloliquefaciens described in
Bacillus subtilis.
Comparative example 6
Decomposed starting agent is prepared referring to 1 the method for embodiment, difference is only that, substitutes Trichoderma viride with Trichoderma harzianum.
Comparative example 7
Decomposed starting agent is prepared referring to 1 the method for embodiment, difference is only that, substitutes mycobacteria with small single-cell bacteria.
Experimental example 1
Detect Examples 1 to 3 and the decomposed starting organic matter of agent of comparative example 5~7, nitrogen, phosphorus, potassium, water content with
And viable count.Specific detection method is referring to NY525-2012, NY884-2012, NY/T798-2015 and GB20287-2006.
Specific testing result is as shown in table 1.According to experimental result described in table 1 it is found that the decomposed starting agent of the embodiment of the present invention 1~3
The degree of decomposition of middle organic matter is high, fertilizer efficiency is good, and the expanding effect of each microorganism is good, and in the decomposed starting agent of comparative example 5~7
There are antagonisms between microorganism, and expanding effect is bad, while the degree of decomposition of organic matter is low, and fertilizer efficiency is poor.
The indices of the decomposed starting agent of table 1
Experimental example 2
The decomposed starting agent of embodiment 1 and comparative example 1~4 is used for decomposed corn stover, rice processing fent, pig
Excrement it is decomposed.Specific decomposed method is as follows:
Firstly, corn stover, rice processing fent are crushed, or by pig manure separating dry space from moist space；Secondly, by the straw
Stalk, leftover bits and pieces, pig manure tiling, spread decomposed starting agent, are uniformly mixed, adjust moisture and carbon-nitrogen ratio, stack fermentation；In fermentation process
In, throw and turn over and check, when it meets the standard of NY525-2012.The decomposed starting agent and corn stover, rice are processed
Mass ratio between leftover bits and pieces or the pig manure of separating dry space from moist space is 4.5:100
Specific testing result is as shown in table 1.According to experimental data shown in table 2 it is found that decomposed described in the embodiment of the present invention 1 open
Dynamic agent all has good decomposed effect to various decomposing agents, shows broad spectrum activity.And decomposed starting agent is to straw described in comparative example 1
Stalk, agricultural byproduct have preferable degradation, but poor to the degradation effect of fowl and animal excrement, and 2~4 pairs of fowl of comparative example
Animal manure just has preferable degradation, but poor to the degradation effect of stalk and agricultural byproduct.
The decomposed effect of the decomposed starting agent of table 2
Experimental example 3
The temperature change of decomposed starting agent compost during rotted pig manure (experimental example 2) described in embodiment 1 is detected, specifically
Testing result is referring to Fig. 1.Result is it is found that decomposed starting agent of the present invention can be rapidly heated to 70~80 according to Fig. 1
DEG C, and maintain to stablize by the temperature in entire digest process.
Finally, it should be noted that the above embodiments are only used to illustrate the technical solution of the present invention., rather than its limitations；To the greatest extent
Present invention has been described in detail with reference to the aforementioned embodiments for pipe, but those skilled in the art should understand that: its
It is still possible to modify the technical solutions described in the foregoing embodiments, or to some or all of the technical features
It is equivalently replaced；And these are modified or replaceed, various embodiments of the present invention skill that it does not separate the essence of the corresponding technical solution
The range of art scheme.
Claims (10)
1. a kind of decomposed starting agent, which is characterized in that it is described it is decomposed starting agent raw material include major ingredient, compound starting function bacterium and
Auxiliary material, the compound starting function bacterium include bacillus, saccharomycete, mould and actinomyces.
2. decomposed starting agent according to claim 1, which is characterized in that the bacillus, saccharomycete, mould and unwrapping wire
Bacterium is respectively bacillus subtilis, S. cervisiae, Trichoderma viride and mycobacteria.
3. decomposed starting agent according to claim 1, which is characterized in that the major ingredient, compound starting function bacterium and auxiliary material
It is respectively as follows: 85~97.5 mass parts of major ingredient, 1~7.5 mass parts of 2.5~10 mass parts of compound starting function bacterium and auxiliary material；It is described
Bacillus in compound starting function bacterium, saccharomycete, mould and actinomyces mass ratio be 5~10:2~4:1~3:1~3.
4. decomposed starting agent according to claim 3, which is characterized in that the major ingredient, compound starting function bacterium and auxiliary material
It is respectively as follows: 90 mass parts of major ingredient, 4 mass parts of 6 mass parts of compound starting function bacterium and auxiliary material；Bud in the compound starting function bacterium
Spore bacillus, saccharomycete, mould and actinomyces mass ratio be 5:3:2:2.
5. decomposed starting agent according to claim 1, which is characterized in that in the decomposed starting agent:
The content of organic matter >=40%, nitrogen content >=5%, phosphorus content >=2%, potassium content >=3%, moisture content≤30%.
6. decomposed starting agent according to claim 1, which is characterized in that in the decomposed starting agent:
Total living bacteria count >=2,000,000,000/g of the compound starting function bacterium, the bacillus >=1,000,000,000/g, saccharomycete
>=3 hundred million/g, mould >=300,000,000/g, actinomyces >=200,000,000/g.
7. decomposed starting agent according to claim 1, which is characterized in that the major ingredient is organic materials；Preferably, described
Major ingredient is selected from agricultural crop straw, agricultural byproduct, dregs of beans or oil cake；It is highly preferred that the major ingredient is agricultural crop straw, agricultural production
Product leftover bits and pieces and dregs of beans；Most preferably, the mass ratio of the stalk, agricultural byproduct and dregs of beans is 20~50:40~70:3
~12.
8. decomposed starting agent according to claim 1, which is characterized in that the auxiliary material be selected from compound fertilizer, urea, phosphate fertilizer,
One of potash fertilizer and lime are a variety of.
9. a kind of method for preparing the decomposed starting agent of any one of claim 1~8, which is characterized in that the method is by institute
Major ingredient, auxiliary material and the mixing of compound starting function bacterium are stated, it is numerous to get the decomposed starting agent by decomposed and expansion.
10. according to the method described in claim 9, it is characterized in that, the method specifically includes: by the major ingredient by crushing
It is mixed afterwards with the auxiliary material, addition part compound starting function bacterium is decomposed to major ingredient progress, later, crushes decomposed object, is added surplus
Remaining compound starting function bacterium, be uniformly mixed, expand it is numerous, expand it is numerous after to get the decomposed starting agent；Preferably, decomposed
When be added complex function starting bacterium be its total weight 1/3~1/2, the compound starting function bacterium being added when expanding numerous be its gross weight
The 1/2~2/3 of amount.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201810910009.4A CN108997034A (en) | 2018-08-10 | 2018-08-10 | Decomposed starting agent of one kind and preparation method thereof |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201810910009.4A CN108997034A (en) | 2018-08-10 | 2018-08-10 | Decomposed starting agent of one kind and preparation method thereof |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN108997034A true CN108997034A (en) | 2018-12-14 |
Family
ID=64595080
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201810910009.4A Pending CN108997034A (en) | 2018-08-10 | 2018-08-10 | Decomposed starting agent of one kind and preparation method thereof |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN108997034A (en) |
Citations (13)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2011044279A2 (en) * | 2009-10-06 | 2011-04-14 | Bio Architecture Lab, Inc. | Microbial systems for producing commodity chemicals |
| CN102382768A (en) * | 2011-09-29 | 2012-03-21 | 武汉施瑞福生物技术有限公司 | Microbial straw decomposition additive as well as preparation method and application thereof |
| CN102531766A (en) * | 2011-09-15 | 2012-07-04 | 北京世纪阿姆斯生物技术股份有限公司 | Microbial decomposing agent and production method thereof |
| CN102617199A (en) * | 2012-04-06 | 2012-08-01 | 东北农业大学 | Preparation method for straw-decomposing inoculant capable of reducing heavy metal pollution |
| CN103342609A (en) * | 2013-07-17 | 2013-10-09 | 成都华隆生物科技有限公司 | Straw thoroughly-decomposing microbial inoculum capable of being preserved for long time under normal temperature condition |
| CN103387428A (en) * | 2013-07-22 | 2013-11-13 | 四川沃达丰生物科技有限公司 | Preparation method for organic material decomposition agent |
| CN103911310A (en) * | 2013-01-07 | 2014-07-09 | 鹤壁市人元生物技术发展有限公司 | Organic material decomposing agent and its preparation method |
| CN104403971A (en) * | 2014-11-28 | 2015-03-11 | 蒋小春 | Straw decomposing agent and preparation method thereof |
| CN105385637A (en) * | 2015-12-17 | 2016-03-09 | 青州伟格生物科技有限公司 | Functional microorganism decomposing agent and preparation method and application thereof |
| CN105461415A (en) * | 2014-08-20 | 2016-04-06 | 朱崇靖 | Double fermented green bioorganic fertilizer |
| CN106479937A (en) * | 2016-12-06 | 2017-03-08 | 秦皇岛领先康地农业技术有限公司 | A kind of purposes of the organic matter decomposing inoculant with deodorant, getting fat function and preparation method thereof with it |
| CN107254420A (en) * | 2017-06-26 | 2017-10-17 | 中国科学院微生物研究所 | One bacillus subtilis and its application |
| CN107365725A (en) * | 2017-08-01 | 2017-11-21 | 山东农大肥业科技有限公司 | A kind of organic matter decomposing inoculant and preparation method thereof |
-
2018
- 2018-08-10 CN CN201810910009.4A patent/CN108997034A/en active Pending
Patent Citations (13)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2011044279A2 (en) * | 2009-10-06 | 2011-04-14 | Bio Architecture Lab, Inc. | Microbial systems for producing commodity chemicals |
| CN102531766A (en) * | 2011-09-15 | 2012-07-04 | 北京世纪阿姆斯生物技术股份有限公司 | Microbial decomposing agent and production method thereof |
| CN102382768A (en) * | 2011-09-29 | 2012-03-21 | 武汉施瑞福生物技术有限公司 | Microbial straw decomposition additive as well as preparation method and application thereof |
| CN102617199A (en) * | 2012-04-06 | 2012-08-01 | 东北农业大学 | Preparation method for straw-decomposing inoculant capable of reducing heavy metal pollution |
| CN103911310A (en) * | 2013-01-07 | 2014-07-09 | 鹤壁市人元生物技术发展有限公司 | Organic material decomposing agent and its preparation method |
| CN103342609A (en) * | 2013-07-17 | 2013-10-09 | 成都华隆生物科技有限公司 | Straw thoroughly-decomposing microbial inoculum capable of being preserved for long time under normal temperature condition |
| CN103387428A (en) * | 2013-07-22 | 2013-11-13 | 四川沃达丰生物科技有限公司 | Preparation method for organic material decomposition agent |
| CN105461415A (en) * | 2014-08-20 | 2016-04-06 | 朱崇靖 | Double fermented green bioorganic fertilizer |
| CN104403971A (en) * | 2014-11-28 | 2015-03-11 | 蒋小春 | Straw decomposing agent and preparation method thereof |
| CN105385637A (en) * | 2015-12-17 | 2016-03-09 | 青州伟格生物科技有限公司 | Functional microorganism decomposing agent and preparation method and application thereof |
| CN106479937A (en) * | 2016-12-06 | 2017-03-08 | 秦皇岛领先康地农业技术有限公司 | A kind of purposes of the organic matter decomposing inoculant with deodorant, getting fat function and preparation method thereof with it |
| CN107254420A (en) * | 2017-06-26 | 2017-10-17 | 中国科学院微生物研究所 | One bacillus subtilis and its application |
| CN107365725A (en) * | 2017-08-01 | 2017-11-21 | 山东农大肥业科技有限公司 | A kind of organic matter decomposing inoculant and preparation method thereof |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN101786911B (en) | Microorganism and enzyme powder composite biological agent for microbial organic fertilizer | |
| CN103980019B (en) | A kind of cultural solid organic waste mesopilous organisms zymotechnique and application | |
| Abdel-Rahman et al. | Biotechnological application of thermotolerant cellulose-decomposing bacteria in composting of rice straw | |
| CN104177137B (en) | A kind of microbial straw composing agent and preparation method thereof | |
| CN101629156B (en) | Microbial agent and soil modifying agent produced by fermentation thereof | |
| CN101643718B (en) | Microbial strain agent and organic fertilizers fermented by same | |
| CN101306962B (en) | Kitchen waste compost method using germ bran as conditioner | |
| CN103304285B (en) | Microbial agent and preparation method as well as application thereof | |
| CN106927977A (en) | A kind of charcoal base organic fertilizer and preparation method thereof | |
| CN103087968B (en) | Production technique of organic fertilizer | |
| CN101165008B (en) | Vegetable residual strain microorganism-earthworm multiple step inoculation conversion method | |
| CN103833464A (en) | Nutritive growth-promoting disease-resistant pest-resistant drought-resistant water-retention bio-organic fertilizer and preparation method thereof | |
| CN105967956A (en) | Ecological organic fermented fertilizer and preparation method thereof | |
| CN102503608B (en) | Method for preparing organic fertilizer from agricultural wastes | |
| CN104016799A (en) | Straw corrosion promoting microbial inoculant-coated biological organic fertilizer and preparation method thereof | |
| CN102643120A (en) | Preparation method of organic fertilizer | |
| CN105746028A (en) | Straw decomposing field-returning method capable of effectively reducing environmental pollution | |
| CN106258896A (en) | A kind of pepper seedling raising medium | |
| CN102180737A (en) | Method for producing organic compound fertilizer by fermenting agricultural organic waste | |
| CN105085113A (en) | Preparation method of crop straw organic fertilizer | |
| CN104230401A (en) | Treatment method of kitchen garbage | |
| CN104761369A (en) | Compound biofertilizer and preparation technology thereof | |
| KR101553073B1 (en) | Decoposing method for organic sludge | |
| CN106588261A (en) | Tea seed shell organic fertilizer and preparation method thereof | |
| CN102180716A (en) | Method for producing organic compound fertilizer by fermenting animal manure |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| PB01 | Publication | ||
| PB01 | Publication | ||
| SE01 | Entry into force of request for substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| RJ01 | Rejection of invention patent application after publication |
Application publication date: 20181214 |
|
| RJ01 | Rejection of invention patent application after publication |