CN105581021A - Fast straw degradation agent as well as preparation method and application thereof - Google Patents

Fast straw degradation agent as well as preparation method and application thereof Download PDF

Info

Publication number
CN105581021A
CN105581021A CN201510989732.2A CN201510989732A CN105581021A CN 105581021 A CN105581021 A CN 105581021A CN 201510989732 A CN201510989732 A CN 201510989732A CN 105581021 A CN105581021 A CN 105581021A
Authority
CN
China
Prior art keywords
agent
fermentation
stalk
separated
preparation
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
CN201510989732.2A
Other languages
Chinese (zh)
Inventor
宋元
尚婷婷
徐会连
张吉萍
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.)
Beijing Yisheng Power Biotechnology Co Ltd
Original Assignee
Beijing Yisheng Power Biotechnology Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Beijing Yisheng Power Biotechnology Co Ltd filed Critical Beijing Yisheng Power Biotechnology Co Ltd
Priority to CN201510989732.2A priority Critical patent/CN105581021A/en
Publication of CN105581021A publication Critical patent/CN105581021A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F11/00Other organic fertilisers
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F9/00Fertilisers from household or town refuse
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05GMIXTURES OF FERTILISERS COVERED INDIVIDUALLY BY DIFFERENT SUBCLASSES OF CLASS C05; MIXTURES OF ONE OR MORE FERTILISERS WITH MATERIALS NOT HAVING A SPECIFIC FERTILISING ACTIVITY, e.g. PESTICIDES, SOIL-CONDITIONERS, WETTING AGENTS; FERTILISERS CHARACTERISED BY THEIR FORM
    • C05G3/00Mixtures of one or more fertilisers with additives not having a specially fertilising activity
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Pest Control & Pesticides (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)

Abstract

The invention discloses a fast straw degradation agent as well as a preparation method and an application thereof, relates to a method for testing or processing seeds, rhizomes or analogues before sowing or planting and aims to provide a fast straw degradation agent which is high in straw degradation speed, low in preparation cost and convenient to use as well as the preparation method and the application of the fast straw degradation agent. The preparation method of the fast straw degradation agent comprises steps as follows: anaerobic fermentation and aerobic fermentation are performed firstly, products of the anaerobic fermentation and the aerobic fermentation are mixed, the aerobic fermentation is performed again, and the fast straw degradation agent is prepared. The fast straw degradation agent can degrade straw rapidly, is applied to degradation of the straw in the field and can rapidly convert organic matters in the straw into nutritional substances absorbed by plants easily, so that soil fertility is improved and crop growth is promoted. The fast straw degradation agent as well as the preparation method and the application thereof is applied to the fields of straw degradation and composting fermentation.

Description

Stalk speed is separated agent and its preparation method and application
Technical field
The present invention relates to a kind of method of testing or process seed, rhizome or analog before sowing or plantation.
Background technology
At present, the method for Treating straw is alkalization, ammoniation process mostly both at home and abroad, and the shortcoming of this method is that cost is high, and benefit is low,Also useful microbial technique Treating straw, is mainly cellulose-decomposing bacterium and lactic acid bacteria are main, and effect is unstable. It is mainlyFermented cellulosic and starch, produce organic acid. Said method not only manufacturing conditions is had relatively high expectations, and range of application is mainly to useCarry out fermented feed for ruminant. And the microorganism fungus kind that biotechnology Treating straw aspect is used is now mostly comparatively single,Microorganism species is more consistent.
Summary of the invention
The technical problem to be solved in the present invention is to provide the stalk speed that a kind of straw degradative speed is fast, cost of manufacture is low, easy to useSeparate agent and its preparation method and application.
A kind of stalk speed of the present invention is separated the preparation method of agent, comprises the following steps:
One, anaerobic fermentation: the raw material of anaerobic fermentation is stirred, pack closed container into, fermentation 3-5 days, makes anaerobism and send outFerment product (feature fermenting: there is obvious white hypha in the superiors); In using small-sized fermentation bucket, must have softPlastic inner cap, the screw lid of then screwing on; Main equipment is also so, must be fully airtight;
Two, the aerobic fermentation first step: after maize pulp and wheat bran are mixed, regulate water content to 20-35%, according to maize pulp and branThe 5-15% of skin total amount adds the bacterial classification of aerobic fermentation, ventilates, is stirred aerobe fermentation 1-3 days, makes aerobic fermentation head product;
Three, aerobic fermentation second step: be that 2:1 will make in the anaerobic fermentation product making in step 1 and step 2 according to mass ratioThe aerobic fermentation head product obtaining mixes, and regulates water content to 30-55%; Then put into stirring-type aerobic fermentation equipment, every5-8h stirs once, stirs 20-25min at every turn, the oxygenation that simultaneously ventilates, and the process of aerobic fermentation is the mistake of slowly drying simultaneouslyJourney, treats that water content is down to 10-25%, makes stalk speed and separates agent;
The raw material of described anaerobic fermentation comprises according to mass fraction: 200-300 part dregs of beans, 200-300 part wheat bran, 100-200 partBacterial classification, 5-10 part molasses and 200-300 part water of ground rice, 5-10 part anaerobic fermentation;
The bacterial classification of described anaerobic fermentation is: sarcina methanica (MethanosarcinaKluyverandvanNiel), Zhan Shi breastBacillus (LactobacillusJensenii), core Fusobacterium (FusobacteriumNucleatum), propionibacterium freudenreichiiAnd beef-steak fungus (FistullnHepatica) (PropionibacteriumFreudennreichii);
In described aerobic fermentation, the mass ratio of maize pulp and wheat bran is 1:3-2:1;
The bacterial classification of described aerobic fermentation is: the white yellow pore fungi (Anomolomaalbolutescens (Romell) that intends becoming&K.H.Larss.), aspergillus niger (Aspergillusniger), product yellowish fiber monad (CellulomonasFlavigena), stearothermophilus budSpore bacillus (BacillusStearothermophilus), Butyrivibrio fibrisolvens (ButyrivibrioFibrisolvens), thermophilic unwrapping wireBacterium (ThermophilicActinomycetes) and yellow product look streptomycete (Flavochromogenes).
The bacterial classification of described aerobic fermentation is mainly above-mentioned a few class bacterium, wherein produces yellowish fiber monad, Butyrivibrio fibrisolvens for decomposingCellulosic mushroom, feature is aerobic, produces high heat, so material to stir, ventilation oxygen; It is high that cellulose decomposition reachesAfter peak, temperature declines, and enters the decomposition in next stage; The white yellow mushroom of pore fungi into decomposition lignin of intending becoming, decomposes quiteIn the lignin of animal skeleton, common microorganism does not have this ability, only has some wood-rotting fungis can take on this task.
Preferably, stalk speed of the present invention is separated the preparation method of agent, and the raw material of described anaerobic fermentation comprises according to mass fraction: 220-280Bacterial classification, 6-8 part molasses and 230-270 part of part dregs of beans, 220-280 part wheat bran, 120-180 part ground rice, 7-9 part anaerobic fermentationWater.
Preferably, stalk speed of the present invention is separated the preparation method of agent, and the raw material of described anaerobic fermentation comprises according to mass fraction: 250Part dregs of beans, 250 parts of wheat brans, 150 parts of ground rice, the bacterial classification of 8 parts of anaerobic fermentations, 7 parts of molasses and 250 parts of water.
Stalk speed of the present invention is separated agent, and the preparation method who separates agent for above-mentioned arbitrary stalk speed makes.
Stalk speed of the present invention is separated the application of agent, for fast degradation stalk.
The fast application of separating agent of stalk of the present invention, comprises the following steps: in stalk, accesses stalk speed and separates agent, the agent of stalk speed solutionAddition is 40-50kg/t, impels stalk to decompose, and makes fertilizer; Also the solution agent of stalk speed and the stalk that mix can be imbeddedUnder soil, above planting vegetable, be improved ground temperature, and the gas discharging has the effect of carbon dioxide fertilization in greenhouse.
Stalk speed of the present invention is separated the application of agent, as compost introduction.
Step as compost introduction is: stalk speed of the present invention separated to agent and directly mixes with fermented manure material requested,Addition is 5-10kg/t, can promote the decomposition of cellulose and lignin, produces high temperature, kills harmful organism, decomposes poisonousMaterial, improves microbial diversity, promotes nutrient validation.
Stalk speed of the present invention is separated the application of agent, as garbage degradation agent.
As the step of garbage degradation agent be: stalk speed of the present invention is separated to agent directly and domestic garbage mixing even, addition is60-100g/kg. In domestic garbage, add this biologic product, promote organic decomposition, degraded harmful substance, canProduce fertilizer. Other contains cellulosic rubbish and adds this biologic product can make waste reduction, makes later processing more squareJust. Especially rural area, family can be placed one the bottomless bulky refuse bucket of lid, is often sprinkled into this biologic product, decomposes rubbishRubbish and elimination peculiar smell, final product is the fertilizer of high-quality.
Stalk speed of the present invention is separated the application of agent, as biological organic fertilizer.
Stalk speed of the present invention is separated agent and be can be used as biological organic fertilizer, and the plastic shed soil of especially excessive use chemical fertilizer, uses the present inventionStalk speed separate agent, can improve diversity of soil microorganism, activating soil, provides available nutrient, promotes soil trace elementUtilizability, suppress the breeding of pathogen, thereby reach diseases prevention, the object of high-quality and high yield. Execute in the time of upper soll layer,Can suppress the germination of weed seed, reach weeding object.
Step as biological organic fertilizer is: after harvesting this season crop wheat or corn, a large amount of discarded stalk residues are layered on field, everyMu residual stalk slag field is spread fertilizer over the fields stalk speed of the present invention and is separated agent 50-80kg, spreads fertilizer over the fields rear shallow turning over, and it is mixed with stalk slag. Can be fastSpeed is decomposed large Tanaka's stalk residue, as the nutrient of next batch of crop; And improve diversity of soil microorganism, promote the micro-life of soilThe breeding of thing. Microorganism by the organic decomposition of its movable acceleration, is enriched the nutrient in soil, for next batch of crop provides againThe trace elements such as N, P, K, promote germination and root growth. Meanwhile, can also improve the porosity of soil, make soilBecome loose, improve the ecological environment of root system, promote the growth of root system, improve the waterlogging ability of crop.
Stalk speed of the present invention is separated agent and its preparation method and application and is with the difference of prior art:
The preparation method that stalk of the present invention speed is separated agent combines by two kinds of fermentation patterns of anaerobic and aerobic, multiple aerobic with detestThe microorganism of oxygen is in conjunction with use, and multiple-microorganism has formed complicated and stable microecosystem, mentioned microorganism in the present inventionAfter mixing with large Tanaka's stalk in its growth course the organic secretion of generation as hydrolase, invertase, amylase, protease,Polygalacturonase, lysine, butyric acid etc., then under the effect of various enzymes, enzymolysis is monose. Finally not only cellulose,Cell membrane, cytoplasm change nutriment (glucose, fructose, sucrose, protein, amino acid) into, and cell membrane is brokenBad, nutrition discharges in born of the same parents, then forms respectively ammonium salt and nitrate through ammoniation, nitrification, finally makes straw feed turnRate increases substantially. Being applied in field can increase edaphon source, as effective fertilizer of plant growth in the coming year, is plantGood biological carbon nitrogenous fertilizer is provided.
Detailed description of the invention
By following examples, stalk speed of the present invention being separated to agent and its preparation method and application is further described.
Embodiment 1
The stalk speed of the present embodiment is separated agent and is prepared according to the following steps:
One, anaerobic fermentation: the raw material of anaerobic fermentation is stirred, pack closed container into, ferment 5 days, make anaerobic fermentationProduct;
Two, the aerobic fermentation first step: after maize pulp and wheat bran are mixed, regulate water content to 35%, add the bacterium of aerobic fermentationKind, ventilate, be stirred aerobe fermentation 3 days, make aerobic fermentation head product;
Three, aerobic fermentation second step: be that 2:1 will make in the anaerobic fermentation product making in step 1 and step 2 according to mass ratioThe aerobic fermentation head product obtaining mixes, and regulates water content to 30%; Then put into stirring-type aerobic fermentation equipment, every 5hStir once, stir 20min at every turn, the oxygenation that simultaneously ventilates, treats that water content is down to 10%, makes stalk speed and separates agent;
The raw material of anaerobic fermentation is: bacterial classification, molasses and the water of dregs of beans, wheat bran, ground rice, anaerobic fermentation;
The bacterial classification of anaerobic fermentation is: sarcina methanica, Lactobacillus Jensenii, core Fusobacterium, propionibacterium freudenreichii and beef-steak fungus;
The bacterial classification of aerobic fermentation is: white yellow intend becoming pore fungi, aspergillus niger, product yellowish fiber monad, bacillus stearothermophilus, moltenFiber butyric acid vibrios, thermophilic actinomycete and yellow product look streptomycete;
The amount of each raw material is in sequence number in table 1, table 21,3,5 above.
Embodiment 2
The stalk speed of the present embodiment is separated agent and is prepared according to the following steps:
One, anaerobic fermentation: the raw material of anaerobic fermentation is stirred, pack closed container into, ferment 3 days, make anaerobic fermentationProduct;
Two, the aerobic fermentation first step: after maize pulp and wheat bran are mixed, regulate water content to 20%, add the bacterium of aerobic fermentationKind, ventilate, be stirred aerobe fermentation 1 day, make aerobic fermentation head product;
Three, aerobic fermentation second step: be that 2:1 will make in the anaerobic fermentation product making in step 1 and step 2 according to mass ratioThe aerobic fermentation head product obtaining mixes, and regulates water content to 55%; Then put into stirring-type aerobic fermentation equipment, every 8hStir once, stir 25min at every turn, the oxygenation that simultaneously ventilates, treats that water content is down to 25%, makes stalk speed and separates agent;
The raw material of anaerobic fermentation is: bacterial classification, molasses and the water of dregs of beans, wheat bran, ground rice, anaerobic fermentation;
The bacterial classification of anaerobic fermentation is: sarcina methanica, Lactobacillus Jensenii, core Fusobacterium, propionibacterium freudenreichii and beef-steak fungus;
The bacterial classification of aerobic fermentation is: white yellow intend becoming pore fungi, aspergillus niger, product yellowish fiber monad, bacillus stearothermophilus, moltenFiber butyric acid vibrios, thermophilic actinomycete and yellow product look streptomycete;
The amount of each raw material is in sequence number in table 1, table 22,4 above.
The amount (kg) of table 1 anaerobic fermentation Raw
The amount (kg) of table 2 aerobic fermentation first step Raw
Embodiment 3
The step that the present embodiment uses the stalk speed making in embodiment 1 to separate agent degrading straw is: according to 40-50kg/t in stalkAdd a kind of stalk speed making of embodiment to separate agent, after mixing, process/place how long 2 months, to stalk cellulase,Lignoenzyme, hemicellulase detect, and concrete outcome is as shown in table 3, wherein 1,3,5 are respectively use embodiment 1In the stalk speed that the makes data of separating agent degrading straw, CK does not add stalk speed to separate the data of agent.
Table 3 stalk speed is separated the degradation capability of agent to stalk
From result in table 3, do not add stalk speed to separate stalk cellulase, hemicellulase, the lignin of agent (CK)Enzyme content is respectively 6IU/mL, 7IU/mL, 4IU/mL, adds the speed of stalk in embodiment 1 to separate in the stalk of agent above three kindsThe content of enzyme all higher than contrast 10-19 doubly, because the content of digestive enzyme improves, illustrates that straw degradative rate also significantly improves thereupon,Show stalk speed solution agent of the present invention degrading straw fast and effectively, produce plant and be easy to the glucose, fructose, the sugarcane that absorbThe simple materials such as sugar, protein, amino acid, and improve the content of ammonium salt and nitrate in soil, increase soil fertility.
Embodiment 4
The step that the present embodiment uses the stalk speed making in embodiment 2 to separate agent degrading straw is: add in stalk according to 50kg/tEnter a kind of stalk speed making of embodiment and separate agent, after mixing, mixture is imbedded to 5-20cm under large Tanaka's soil, earthing, aboveThe vegetables such as plantation Chinese cabbage, tomato, cucumber. Adopt the method planting vegetable of the present embodiment with directly compared with large Tanaka's planting vegetableCan significantly suppress harmful microbe existence and breeding, alleviate and the insect pest of successive elimination soil-borne disease and continuous cropping obstacle, and can press downGrowing of weeds processed improves vegetable yields and quality etc.
Although more than described the specific embodiment of the present invention, it will be understood by those of skill in the art that these are only to liftExample explanation, protection scope of the present invention is limited by appended claims. Those skilled in the art is not deviating from the present inventionPrinciple and the prerequisite of essence under, can make various changes or modifications to these embodiments, but these changes and amendment all fallEnter protection scope of the present invention.

Claims (6)

1. stalk speed is separated a preparation method for agent, it is characterized in that comprising the following steps:
One, anaerobic fermentation: the raw material of anaerobic fermentation is stirred, pack closed container into, fermentation 3-5 days, makes anaerobism and send outFerment product;
Two, the aerobic fermentation first step: after maize pulp and wheat bran are mixed, regulate water content to 20-35%, according to maize pulp and branThe 5-15% of skin total amount adds the bacterial classification of aerobic fermentation, ventilates, is stirred aerobe fermentation 1-3 days, makes aerobic fermentation head product;
Three, aerobic fermentation second step: be that 2:1 will make in the anaerobic fermentation product making in step 1 and step 2 according to mass ratioThe aerobic fermentation head product obtaining mixes, and regulates water content to 30-55%; Then put into stirring-type aerobic fermentation equipment, every5-8h stirs once, stirs 20-25min at every turn, and the oxygenation that simultaneously ventilates treats that water content is down to 10-25%, makes stalk speedSeparate agent;
The raw material of described anaerobic fermentation comprises according to mass fraction: 200-300 part dregs of beans, 200-300 part wheat bran, 100-200 partBacterial classification, 5-10 part molasses and 200-300 part water of ground rice, 5-10 part anaerobic fermentation;
The bacterial classification of described anaerobic fermentation is: sarcina methanica, Lactobacillus Jensenii, core Fusobacterium, propionibacterium freudenreichii and cow tongueBacterium;
In described aerobic fermentation, the mass ratio of maize pulp and wheat bran is 1:3-2:1;
The bacterial classification of described aerobic fermentation is: white yellow intend becoming pore fungi, aspergillus niger, product yellowish fiber monad, bacillus stearothermophilus,Butyrivibrio fibrisolvens, thermophilic actinomycete and yellow product look streptomycete.
2. stalk speed according to claim 1 is separated the preparation method of agent, it is characterized in that: the raw material of described anaerobic fermentation is pressedComprise according to mass fraction: the bacterial classification of 220-280 part dregs of beans, 220-280 part wheat bran, 120-180 part ground rice, 7-9 part anaerobic fermentation,6-8 part molasses and 230-270 part water.
3. stalk speed according to claim 2 is separated the preparation method of agent, it is characterized in that: the raw material of described anaerobic fermentation is pressedComprise according to mass fraction: the bacterial classification of 250 parts of dregs of beans, 250 parts of wheat brans, 150 parts of ground rice, 8 parts of anaerobic fermentations, 7 parts of molasses and250 parts of water.
4. stalk speed is separated an agent, it is characterized in that: it is that in claim 1-3, either method makes that described stalk speed is separated agent.
5. stalk speed is separated an application for agent, it is characterized in that: for fast degradation stalk.
6. stalk speed according to claim 5 is separated the application of agent, it is characterized in that comprising the following steps: in stalk, addStalk speed is separated agent, mixes; The addition that stalk speed is separated agent is 40-50kg/t.
CN201510989732.2A 2015-12-24 2015-12-24 Fast straw degradation agent as well as preparation method and application thereof Pending CN105581021A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201510989732.2A CN105581021A (en) 2015-12-24 2015-12-24 Fast straw degradation agent as well as preparation method and application thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201510989732.2A CN105581021A (en) 2015-12-24 2015-12-24 Fast straw degradation agent as well as preparation method and application thereof

Publications (1)

Publication Number Publication Date
CN105581021A true CN105581021A (en) 2016-05-18

Family

ID=55921233

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201510989732.2A Pending CN105581021A (en) 2015-12-24 2015-12-24 Fast straw degradation agent as well as preparation method and application thereof

Country Status (1)

Country Link
CN (1) CN105581021A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107176891A (en) * 2017-06-28 2017-09-19 山东博华高效生态农业科技有限公司 It is a kind of to promote the biological agent and its production technology of stalk fast degradation
CN109503276A (en) * 2018-12-19 2019-03-22 安徽尊贵现代农业科技有限公司 A kind of preparation method of the biological organic fertilizer with insect prevention function
AT520801A1 (en) * 2017-11-17 2019-07-15 Georg Stimpfl Process for the utilization of biomass

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101775359A (en) * 2009-01-13 2010-07-14 刘相梅 Special microorganism composite bacterial agent for directly decomposing and fermenting crops straws to generate marsh gas and application method thereof
CN102173507A (en) * 2011-01-12 2011-09-07 南京加德绿色能源研发有限公司 Method for comprehensively recycling fecal sewage of large-scale livestock and poultry farms and farmland crop straws
CN102676492A (en) * 2012-05-30 2012-09-19 上海交通大学 Efficient straw degrading composite fungicide and organic fertilizer preparing method thereof
CN102690755A (en) * 2012-06-01 2012-09-26 德州市元和农业科技开发有限责任公司 Compound microbial bacterial preparation for degrading crop straw and preparation method and application of compound microbial bacterial preparation
CN103898008A (en) * 2013-06-08 2014-07-02 东莞市保得生物工程有限公司 Preparation method of organic material decomposition agent
CN104099282A (en) * 2014-07-19 2014-10-15 尹梦珍 Environment-friendly straw degradation agent

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101775359A (en) * 2009-01-13 2010-07-14 刘相梅 Special microorganism composite bacterial agent for directly decomposing and fermenting crops straws to generate marsh gas and application method thereof
CN102173507A (en) * 2011-01-12 2011-09-07 南京加德绿色能源研发有限公司 Method for comprehensively recycling fecal sewage of large-scale livestock and poultry farms and farmland crop straws
CN102676492A (en) * 2012-05-30 2012-09-19 上海交通大学 Efficient straw degrading composite fungicide and organic fertilizer preparing method thereof
CN102690755A (en) * 2012-06-01 2012-09-26 德州市元和农业科技开发有限责任公司 Compound microbial bacterial preparation for degrading crop straw and preparation method and application of compound microbial bacterial preparation
CN103898008A (en) * 2013-06-08 2014-07-02 东莞市保得生物工程有限公司 Preparation method of organic material decomposition agent
CN104099282A (en) * 2014-07-19 2014-10-15 尹梦珍 Environment-friendly straw degradation agent

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107176891A (en) * 2017-06-28 2017-09-19 山东博华高效生态农业科技有限公司 It is a kind of to promote the biological agent and its production technology of stalk fast degradation
AT520801A1 (en) * 2017-11-17 2019-07-15 Georg Stimpfl Process for the utilization of biomass
AT520801B1 (en) * 2017-11-17 2021-01-15 Georg Stimpfl Process for the utilization of biomass
CN109503276A (en) * 2018-12-19 2019-03-22 安徽尊贵现代农业科技有限公司 A kind of preparation method of the biological organic fertilizer with insect prevention function

Similar Documents

Publication Publication Date Title
CN101786911B (en) Microorganism and enzyme powder composite biological agent for microbial organic fertilizer
CN102212494B (en) Organic matter decomposing inoculant, and preparation method and application thereof
CN105296394A (en) Microbial decomposition agent for animal wastes and straws and preparation method thereof
CN104529573A (en) Multi-effect ferment fertilizer prepared from agricultural wastes
CN104193431B (en) A kind of feces of livestock and poultry harmless treatment specific complex microbial bacterial agent and preparation method
CN104671860A (en) Bioorganic fertilizer using agricultural waste as raw materials and preparation method of bioorganic fertilizer
CN101712566B (en) Preparation method of soil moisturizing bio-fertilizer
CN106386163A (en) Method for cultivating edible fungi by using crop straw
CN106497853B (en) Filter mud of sugarcane fermenting agent and filter mud of sugarcane fermentation process
CN101357857B (en) Bio organic fertilizer for aquaculture and paddy field and producing method thereof
CN108314585A (en) Agriculture probiotics conversion stalk and the method for cultivating excrement production biological organic fertilizer
CN105199962A (en) Microbial straw-decomposing agent as well as preparation method and application thereof
CN104788144A (en) Preparation method of active probiotic organic fertilizer
CN104761309A (en) Active probiotic organic fertilizer and application thereof
CN106631546A (en) Bio-organic fertilizer and preparation method thereof
CN104447095A (en) Bioactive organic pesticide-added fertilizer as well as preparation method and application of bioactive organic pesticide-added fertilizer
CN105948841B (en) Organic fertilizer tank type fermentation method taking mushroom dregs as substrate
CN110256145A (en) A kind of tobacco organic fertilizer and preparation method thereof
CN112047785A (en) Chitin-containing environment-friendly enzyme biological fertilizer and preparation method thereof
CN105110944A (en) Agaricus bisporus culture substrate and preparation method thereof
CN106673725A (en) Preparation method of organic fertilizer
CN107285925A (en) A kind of method of utilization microorganism formulation stalk stack retting returning to the field
CN111875422A (en) Method for preparing organic fertilizer from vegetable tails, straws and mushroom dregs
CN108409381A (en) A kind of medicinal plant growth special fertilizer and preparation method thereof
CN108485995A (en) A kind of complex micro organism fungicide and biological organic fertilizer promoting hickory chick growth

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20160518

RJ01 Rejection of invention patent application after publication