CN103980010B - Livestock and poultry manure decomposing inoculant, use method thereof and biological organic fertilizer prepared by using livestock and poultry manure decomposing inoculant - Google Patents

Livestock and poultry manure decomposing inoculant, use method thereof and biological organic fertilizer prepared by using livestock and poultry manure decomposing inoculant Download PDF

Info

Publication number
CN103980010B
CN103980010B CN201410242443.1A CN201410242443A CN103980010B CN 103980010 B CN103980010 B CN 103980010B CN 201410242443 A CN201410242443 A CN 201410242443A CN 103980010 B CN103980010 B CN 103980010B
Authority
CN
China
Prior art keywords
livestock
poultry
manure
parts
fermentation
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.)
Active
Application number
CN201410242443.1A
Other languages
Chinese (zh)
Other versions
CN103980010A (en
Inventor
何宗均
梁海恬
赵琳娜
田阳
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.)
Tianlan Diwo (Tianjin) Agricultural Technology Co.,Ltd.
Original Assignee
TIANJIN AGRICULTURAL RESOURCE AND ENVIRONMENT INST
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 TIANJIN AGRICULTURAL RESOURCE AND ENVIRONMENT INST filed Critical TIANJIN AGRICULTURAL RESOURCE AND ENVIRONMENT INST
Priority to CN201410242443.1A priority Critical patent/CN103980010B/en
Publication of CN103980010A publication Critical patent/CN103980010A/en
Application granted granted Critical
Publication of CN103980010B publication Critical patent/CN103980010B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

Landscapes

  • Fertilizers (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)

Abstract

The invention discloses a livestock and poultry manure decomposing inoculant, a use method thereof and a biological organic fertilizer prepared by using the livestock and poultry manure decomposing inoculant and fermenting through a special process. The livestock and poultry manure decomposing inoculant is prepared by compounding the following materials in parts by weight: 0.5-2 parts of bacillus subtilis, 0.5-2 parts of streptomyces microflavus, 0.5-2 parts of trichoderma longibrachiatum and 0.5-2 parts of bacillus mucilagimosus krassilm, wherein the effective viable count is 6*10<8> per gram. The livestock and poultry manure decomposing inoculant disclosed by the invention has multiple functions, can be used for decomposing the livestock and poultry manure and removing the odor and can resist the fusarium oxysporum and increase the yield after being applied to crops. When the livestock and poultry manure decomposing inoculant is applied to treating the livestock and poultry manure, the bacterial count, C/N ratio and fermentation period condition are all better than those of the comparison of an unknown inoculant. The biological organic fertilizer is prepared by adding 1 kilogram of the livestock and poultry manure decomposing inoculant to every 5 squares of the livestock and poultry manure and then fermenting through the special process. The livestock and poultry manure is formed by mixing the following materials in parts by weight: 40-60 parts of chicken manure, 20-40 parts of cattle manure, 5-15 parts of pig manure and 5-15 parts of lignite. The biological organic fertilizer disclosed by the invention is applied to scallion planting, achieves the disease control efficiency up to 56% and increases the yield per mu by 20.5%.

Description

A kind of feces of livestock and poultry decomposing microbial inoculum and its using method and made biological organic fertilizer
Technical field
The invention belongs to application of the agriculture microorganism on feces of livestock and poultry is processed, it is related to a kind of feces of livestock and poultry and becomes thoroughly decomposed bacterium Agent and its using method and made biological organic fertilizer.
Background technology
At present, China's Amount of poultry excrements is modern equivalent to 3.4 times of trade waste discharge capacity up to 18.84 hundred million t 10 years afterwards, also by with 8% speed increase, feces of livestock and poultry not processed and applied livestock and poultry breeding industry due to most of, to water The direct or indirect negative effect that body, air, soil, health and ecosystem are caused, processes and solves feces of livestock and poultry The environmental problem for causing, is current problem anxious to be resolved.Feces of livestock and poultry production is quickly processed using feces of livestock and poultry decomposing microbial inoculum Organic fertilizer, is the Main for solving problem above both at home and abroad, and this technology at home and abroad has been obtained for being widely applied.
At present, domestic feces of livestock and poultry decomposing microbial inoculum has often related only to the decomposition of cellulose and protein in feces of livestock and poultry Ability, function is often more single, and microbial inoculum itself and extension product organic fertilizer performance are single, and added value is not high, agriculturally Income cannot be improved naturally, so as to affect the smooth solution of problem above.
Based on this, spy proposes the present invention.The invention considers the particularity and extension product of feces of livestock and poultry itself to be had The disease-resistant performance of the deodoriging properties of the functional characteristic of machine fertilizer, such as decomposing microbial inoculum, decomposing microbial inoculum and its extension product organic fertilizer With bacterial manure performance etc..
The content of the invention
It is an object of the invention to provide a kind of decomposing microbial inoculum and its using method dedicated for processing feces of livestock and poultry, and With the microbial inoculum and the bio-organic fertilizer of special process fermenting and producing.
The present invention provide a kind of feces of livestock and poultry decomposing microbial inoculum, it is characterised in that it by decomposable asymmetric choice net cellulose, protein, remove Smelly, disease-resistant and bacterial manure several functions various bacterial strains are composited, and its active component includes bacillus subtilises(Bacillus subtilis), streptomyces microflavus(Streptomyces microflavus), long handle Trichoderma spp.(Trichoderma longbrachiatum)And Bacillus mucilaginosus(Bacillus mucilaginosus), it is by following portions by weight Each single strain fermented product composition:0.5~2 part of bacillus subtilises, 0.5~2 part of streptomyces microflavus, 0.5~2 part of long handle Trichoderma spp. and 0.5~2 part of Bacillus mucilaginosus;Poultry manure decomposing agent living bacteria count is 6 × 108Individual/g.
Concretely Chinese agriculture Microbiological Culture Collection administrative center deposit number is ACCC to the bacillus subtilises 11089 bacterial strain.Concretely Chinese agriculture Microbiological Culture Collection administrative center deposit number is the streptomyces microflavus The bacterial strain of ACCC 40027.Concretely Chinese agriculture Microbiological Culture Collection administrative center deposit number is the long handle Trichoderma spp. The bacterial strain of ACCC 30150.The Bacillus mucilaginosus concretely Chinese agriculture Microbiological Culture Collection administrative center preservation Numbering is the bacterial strain of ACCC 10013.
The feces of livestock and poultry decomposing microbial inoculum has several functions, including fermentation maturity and deodorization can be carried out to feces of livestock and poultry, Anti- cucumber fusarium axysporum and crops can be applied to can increase production.Described decomposing microbial inoculum can be used for cattle, pig, chicken, sheep, horse, duck etc. The quick composting of feces of livestock and poultry, and can in right amount add other organic materials, such as brown coal.
The present invention further discloses the using method of feces of livestock and poultry decomposing microbial inoculum, it is characterised in that enter by the steps OK:
1st, the carbon-nitrogen ratio of feces of livestock and poultry is adjusted(25~30:1)And moisture(55~60%, with handss one hold handss seam drip for Preferably), 1 kilogram of composite bacteria agent capable is added per 5 side's feces of livestock and poultry, turn over and smash uniform.
2nd, by feces of livestock and poultry heap trapezoidal, 1 meter of the heap top width of growth that pretreatment is good, 2 meters of heap bottom width, heap high summer and autumn 0.8~1 Rice, 1.2~1.4 meters of winter-spring season, depending on heap length is according to place, per heap volume 5 sides are no less than.
3rd, after fermentation starts, temperature of charge is worked as(20~30 centimetres of depths)Kept for three days when rising to 55 DEG C, then turn over and smash one It is secondary.If fermentation initial stage temperature does not rise, moisture is adjusted to recommendation ratio and turned over daily and smash once until heap temperature rises.
4th, after heap temperature rises to again 55 DEG C, kept for three days, then turn over and smash once;
5th, according to heap tender feeling condition carry out turning over smashing afterwards, temperature upward period is not turned over to be smash, temperature stops rising then to turn over smashing, and lays equal stress on Multiple the step for, when heap temperature is identical with outdoor temperature, moisture is down to below 30%, that is, sweat is completed, whole fermentation Cycle is usually 15~25 days.
The present invention further discloses poultry manure decomposing microbial inoculum becomes thoroughly decomposed and the application in deodorization in livestock manure fermented, and Application in arviculture volume increase, wherein being applied to mu volume increase 17.4% in Caulis et Folium Brassicae capitatae plantation.
The invention also discloses a kind of bio-organic fertilizer, it is characterised in that it is sent out by the feces of livestock and poultry decomposing microbial inoculum Ferment feces of livestock and poultry becomes thoroughly decomposed and forms, wherein adding 1 kilogram of feces of livestock and poultry decomposing microbial inoculum, described feces of livestock and poultry per 5 side's feces of livestock and poultry Parts by weight it is as follows:40~60 parts of chicken manure;20~40 parts of cattle manure;5~15 parts of pig manure;5~15 parts of brown coal.
The described chicken manure content of organic matter >=45%, total nitrogen content >=2.5%;The cattle manure content of organic matter >=50%;Pig manure is organic Matter content >=45%;Lignite humic acid content >=50%.
The present invention further discloses the production method of bio-organic fertilizer, it is characterised in that carry out by the steps:
1st, the mixing of raw material:Fully mixed with batch mixer chicken manure, cattle manure, pig manure and brown coal are weighed by weight;
2nd, add water:By water and mixed material 1:1 weight ratio adds water, and control water content is 50~60%;
3rd, feces of livestock and poultry decomposing agent is added:1 kilogram of composite bacteria agent capable is added per 5 side's feces of livestock and poultry;
4th, bank up specification:By regulate water and add composite bacteria agent capable feces of livestock and poultry heap grow up trapezoidal, 1 meter of heap top width, 2 meters of heap bottom width, 0.8~1 meter of heap high summer and autumn, 1.2~1.4 meters of winter-spring season depending on heap length is according to place, are no less than per heap volume 5 sides;
5th, the control of turning time:Kept for three days when 20~30 centimetres of depths temperature of charge rise to 55 DEG C, then turn over and smash Once, after heap temperature rises to again 55 DEG C, kept for three days, then turn over and smash once, when temperature is more than 70 DEG C, need to be turned over immediately Smash, suppression of the high temperature to growth of microorganism is eliminated by cooling, so as to promote the activity of a large amount of mesophilic bacterias, accelerate entering for compost Journey;
6th, turning is required:Turn over and to accomplish during pile tune, even, broken, it is exactly that original top section in pile is transferred to earth's surface to adjust Become underclad portion, and underclad portion is transferred to top layer and is changed into top section, to reach the purpose of abundant fermentation;Even is exactly in pile Raw material mixes also uneven part, and mixing work is carried out again;Broken is exactly the massive zymolysis thing to being formed during the fermentation Carry out broken work;
7th, the addition of object bacteria:After fermentation the phase, i.e., when fermentation starts cooling, add Bacillus mucilaginosus single strain Microbial inoculum, is 1kg per square object material addition;
8th, fermentation termination control:When heap temperature is identical with outdoor temperature, moisture is down to less than 30%, that is, complete biological organic The whole fermentation production process of fertilizer, whole cycle is usually 15~20 days, 25~30 days time in winter;
9th, fermented quality control:Crushed after the completion of fermentation, sieved, detected, weighed and packed, bio-organic fertilizer is produced Product production is completed, and bio-organic fertilizer organic matter requires to reach 45%~55%, N, P, K total nutrient 5%, and living bacteria count > 0.2 × 108Individual/g, excrement colibacillus group number is negative, induced worm egg death rate 100%.
The present invention further discloses application of the biological organic fertilizer in terms of vegetable disease-resistant effect of increasing production.The biological organic Fertilizer is applied to have obvious disease-resistant yield-increasing effect in Herba Alii fistulosi plantation, and preventive effect is increased production up to 20.5% up to 56%.
The decomposing microbial inoculum energy quick composting feces of livestock and poultry that the present invention is provided, with good deodoriging properties, and then output is high Quality can be disease-resistant bio-organic fertilizer, can avoid because feces of livestock and poultry becomes thoroughly decomposed that the pest and disease damage that thoroughly do not brought is high, emergence rate The disadvantage such as low, burn seedlings, dead seedling, weeds are more.Can significantly be increased by the become thoroughly decomposed bio-organic fertilizer product of production of described decomposing microbial inoculum Plus the content of the nutrient such as the soil organism and phosphorus, potassium, quantity of useful microbe in nutrient conversion efficiency and product is improved, promote Soil remediation, culture fertility can reduce fertilizer application amount, while strengthening the disease resistance of crop, improve crop quality, reduce and throw Enter, improve yield, promote to increase income.
Description of the drawings:
Fig. 1 is the preparation technology flow chart of bio-organic fertilizer.
Specific embodiment
Below example facilitates a better understanding of the present invention, but does not limit the present invention.Experiment in following embodiments Method, if no special instructions, is conventional method.Test material used in following embodiments, if no special instructions, is certainly What routine biochemistry reagent shop was commercially available.Quantitative test in following examples, is respectively provided with three repetitions and tests, and as a result makes even Average.
Following bacterial strain is all obtained from Chinese agriculture Microbiological Culture Collection administrative center (Agricultural Culture Collection of China, abbreviation ACCC):
Bacillus subtilises(Bacillus subtilis):ACCC deposit numbers are 11089, abbreviation ACCC11089;
Streptomyces microflavus(Streptomyces microflavus):ACCC deposit numbers are 40027, abbreviation ACCC 40027;
Long handle Trichoderma spp.(Trichoderma longbrachiatum):ACCC deposit numbers are 30150, referred to as ACCC30150;
Bacillus mucilaginosus(Bacillus mucilaginosus):ACCC deposit numbers are 10013, referred to as ACCC10013。
Embodiment 1:
The preparation of culture medium and strain
First, the preparation of culture medium
1st, Rhizoma Solani tuber osi, glucose agar medium(PDA)
200 grams of the Rhizoma Solani tuber osi of skin is removed, is cut into small pieces, the 1000ml that adds water boils 30 minutes, potato ball is filtered off, by filtrate 1000ml, plus 20 grams of glucose are complemented to, 15 grams of agar dissolves rear subpackage, and 15 pounds sterilize 30 minutes, and pH natures prepare liquid Agar is not added with during culture medium.
2nd, nutrient agar
It is made up of peptone 5g, Sodium Chloride 5g, Carnis Bovis seu Bubali cream 3g and distilled water 1000ml.pH7.0(Solid medium adds fine jade Fat 15-20g).
3rd, Gao Shi synthesizes No. 1 culture medium
KNO3 1g, K2HPO4 0.5g, NaCl 0.5g, FeSO47H2O 0.01g, MgSO47H2O 0.5g soluble starches 20g, pH7.2~7.4, distilled water 1000ml.
4th, B. mucilaginocus culture medium
Yeast extract 0.4g, Mannitol 10.0g, K2HPO4 0.5g、MgSO47H2O 0.2g、FeCl3 0.005g、CaCO3 1.0g, distilled water 1000.0ml, PH7.0-7.2, when preparing solid medium 15 grams of agar are added.
5th, solid fermentation culture medium
Testa Tritici 80g, bean cake 10g, (NH4)2SO41.0g, KH2PO40.2g, MgSO4·7H200.05g, 80mL distilled water.
2nd, the activation of strain
Bacillus subtilises bacterium is seeded in nutrient agar culture medium;Long handle Trichoderma spp. is seeded in PDA culture medium;Carefully Yellow streptomycete is seeded in Gao Shi and synthesizes in No. 1 culture medium;Bacillus mucilaginosus are seeded in B. mucilaginocus culture medium
Bacillus subtilises, streptomyces microflavus, long handle Trichoderma spp. and Bacillus mucilaginosus are carried out into respectively inclined-plane switching, is connect Enter respective ramp culture medium, activation culture 3-7 days.
3rd, prepared by single strain
1st, the culture and fermentation of bacillus subtilises
Slant medium and Shake flask medium are all nutrient agar, and when preparing solid medium 15 grams of agar are added, and are planted Sub- tank and fermentation tank culture medium are 1000kg water, the bean milk of 8.75kg Semen sojae atricolor, the starch of 6.5kg, 1kg glucoses, CaCO3100g, FeCl310g, pH7.0, Jing after 121 DEG C of real tanks sterilize 30 minutes, cultivate 24~36 hours at 28 DEG C~30 DEG C, when Bacterium number reaches 10 × 10 in per ml fermentation liquids8Individual/g.Then the fermentation liquid by weight respectively than 3 parts is adsorbed on 1 part of Vermiculitum Room temperature dries and obtain bacillus subtilises single strain microbial inoculum.
2nd, the culture and fermentation of Bacillus mucilaginosus
Slant medium and Shake flask medium are all B. mucilaginocus culture medium, and seed tank and fermentation tank culture medium are 1000kg Water, the bean milk of 8.75kg Semen sojae atricolor, the starch of 6.5kg, 1kg glucoses, CaCO3100g, FeCl3The real tanks of 121 DEG C of 10g, pH7.0, Jing After sterilizing 30 minutes, cultivate 48 hours at 28 DEG C~30 DEG C, when bacterium number reaches 5 × 10 in every ml fermentation liquids8Individual/g.Then press and divide Fermentation liquid of the other weight than 3 parts is adsorbed in room temperature on 1 part of Vermiculitum and dries and obtain Bacillus mucilaginosus single strain microbial inoculum.
3rd, the culture and fermentation of long handle Trichoderma spp.
Inclined-plane and Shake flask medium are Rhizoma Solani tuber osi, glucose agar medium, and slant medium adds agar.Liquid culture During 500ml triangular flasks are sub-packed in after base is sterilized, each funguses slant strains of access, shaking table speed 180r/min, 28 DEG C~30 DEG C Culture 48 hours, big when occurring density in shaking flask, mycelium pellet is not substantially muddy.Seed tank and fermentation cylinder for fermentation culture medium For the cooking liquor of 1000kg water, the bean milk of 8.75kg Semen sojae atricolor, the starch of 6.5kg, 1kg glucoses and 2kg Rhizoma Solani tuber osis, pH7.0, Jing After 121 DEG C of real tanks sterilize 30 minutes, cultivate 48 hours at 28 DEG C~30 DEG C, after density big mycelium pellet occurs in fermentation liquid, connect Plant in solid fermentation culture medium, inoculum concentration 10%, 121 DEG C, 0.1MPa autoclaving 30min, 25 DEG C of solid fermentation culture 48h, Spore count is up to 6 × 108Individual/g.
4th, the culture and fermentation of streptomyces microflavus
Inclined-plane and Shake flask medium are that Gao Shi synthesizes No. 1 culture medium, and slant medium adds agar.Fluid medium Jing is gone out During 500ml triangular flasks are sub-packed in after bacterium, each funguses slant strains are accessed, shaking table speed 180r/min, 28 DEG C~30 DEG C cultures 5~ 7 days, big when occurring density in shaking flask, mycelium pellet was not substantially muddy.Seed tank and fermentation cylinder for fermentation culture medium are The cooking liquor of 1000kg water, the bean milk of 8.75kg Semen sojae atricolor, the starch of 6.5kg, 1kg glucoses and 2kg Rhizoma Solani tuber osis, pH7.0, Jing 121 After DEG C real tank sterilizes 30 minutes, cultivate 48 hours at 28 DEG C~30 DEG C, after density big mycelium pellet occurs in fermentation liquid, be inoculated into In solid fermentation culture medium, inoculum concentration 10%, 121 DEG C, 0.1MPa autoclaving 30min, 25 DEG C of solid fermentation cultures 5~7 days, Spore count is up to 6 × 108Individual/g.
4th, decomposing microbial inoculum(Represented with composite bacteria agent capable below)Preparation
Bacillus subtilises, streptomyces microflavus, long handle Trichoderma spp. and the Bacillus mucilaginosus list bacterium produced as stated above It is 0.5~2 to plant weight ratio:0.5~2:0.5~2:0.5~2.Mixing is obtained composite bacteria agent capable after mixing thoroughly, and composite bacteria agent capable is effectively lived Bacterium number reaches 6 × 108Individual/g.
Embodiment 2:
Composite bacteria agent capable is constituted
A kind of feces of livestock and poultry decomposing microbial inoculum, is formulated as follows(By weight):
The composition of the feces of livestock and poultry decomposing microbial inoculum of table 1
Title Bacillus subtilises Streptomyces microflavus Long handle Trichoderma spp. Bacillus mucilaginosus
(1) 0.5 2.0 1.0 2.0
(2) 1.0 1.5 2.0 1.5
(3) 1.5 1.0 1.5 1.0
(4) 2.0 0.5 0.5 0.5
Wherein living bacteria count is 6 × 108Individual/g;
The proportioning of the bio-organic fertilizer raw materials for production of table 2(Weight percent)
Title Chicken manure(%) Cattle manure(%) Pig manure(%) Brown coal(%)
(1) 40 40 10 10
(2) 45 30 15 10
(3) 50 30 5 15
(4) 60 20 15 5
Embodiment 3:
Mutual antagonistic experiment between bacterial strain
Bacillus subtilises after activation, streptomyces microflavus, long handle Trichoderma spp. and Bacillus mucilaginosus are carried out between bacterial strain Mutual antagonistic experiment, combination of two is divided into into 12 kinds of compound modes, each three repetition of combination.
Bacteriostatic test is carried out using steel ring method, bacterial strain is cultivated 3-7 days in corresponding culture medium(190r/min, 28 DEG C)System Into fermentation liquid.Take one of which bacterium(A)Fermentation liquid 0.1mL be applied on PDA plate, then in the solid medium of each flat board On put the steel rings of two in advance sterilizings, then any bacterium outside the A bacterium of 0.25mL is added in each steel ring(B)Fermentation Liquid, each is processed in triplicate, only to connect the plate of A bacterium as control.28 DEG C of cultures and routine observation antibacterial situation.The results are shown in Table 3。
Antagonistic effect between the strain of table 3
Bacillus subtilises Streptomyces microflavus Long handle Trichoderma spp. Bacillus mucilaginosus
Bacillus subtilises - - -
Streptomyces microflavus - - -
Long handle Trichoderma spp. - - -
Bacillus mucilaginosus - - -
Note:"-" represents that Antagonistic reaction is negative, and "+" represents that Antagonistic reaction is positive.
Result of the test shows between bacillus subtilises, streptomyces microflavus, 4 kinds of bacterium of long handle Trichoderma spp. and Bacillus mucilaginosus Unrestraint is acted on, and Antagonistic reaction is feminine gender.
Embodiment 4:
The cellulose and the measure of breaks down proteins ability of single bacterial strain and composite bacteria agent capable
First, cellulase activity assay method
1st, reagent and solution
Substrate solution:0.625 g sanloses are accurately weighed, 100.0 mL sodium phosphate buffers (0.2 are dissolved in M, pH 6.0), heated and stirred is allowed to dissolve.
DNS developers:10.0 g 3 are weighed, 5- dinitrosalicylic acids are dissolved in distilled water, add 20.0 g hydroxides Sodium, 200.0 g sodium potassium tartrate tetrahydrates and 500.0 ml water, add the g of re-distilled phenol 2.0, anhydrous sodium sulfite 0.5 after heating for dissolving G is cooled down after all dissolvings, is dissolved to 1000.0 mL.
2nd, instrument and equipment
Spectrophotometer, electronic balance, agitator incubator.
3rd, Specification Curve of Increasing
Standard glucose solution:25.0mL is settled to distillation water dissolution 25.0mg glucoses.
5 test tubes with 20.0 ml scales are taken, by upper table reagent is measured.Often respectively add the M hydrogen-oxygens of 1.0 ml 2.0 in pipe Change sodium solution and 2.0 ml DNS nitrite ions, after accurately 5.0 min of heating are placed in boiling water bath after shaking up, flowing water cooling, distillation Water is settled to 20.0 ml, shakes up the OD values that each pipe is determined at 490 nm, and as abscissa, OD values are the μ g numbers with glucose Vertical coordinate, draws standard curve.
The Specification Curve of Increasing table of table 4
Test tube number Standard glucose solution(ml) Sodium phosphate buffer (0.2M pH 6.0)(ml) Glucose amount in test tube(μg)
1 0 5 0
2 0.4 4.6 400
3 0.7 4.2 800
4 1.6 3.4 1600
5 3.2 1.8 3200
4th, former state enzyme liquid
10 times of 5.0g samples distilled water diluting is weighed, fully vibration, static 30min is filtered, and its filtrate is former state enzyme Liquid.
5th, determination step
Take 3 test tubes with 20.0ml scales, 1 as blank, remaining 2 used as parallel sample pipe.Sample Guan Zhongjia 1.0ml former state enzyme liquids, are then separately added into the substrate solution that 4.0ml is pre-heated to 60 DEG C, at 60 DEG C in 3 test tubes 20min is reacted in water-bath to take out, the 2.0M sodium hydroxide solutions and 2.0ml DNS nitrite ions for adding 1.0ml immediately is often managed, and is shaken 1.0ml former state enzyme liquids are added in control tube after even.3 test tubes are put in boiling water bath, are taken out immediately after colour developing 5min, flowed Water cooling, is dissolved to 20.0ml, and its OD value is surveyed at 490nm with spectrophotometer.
6th, cellulase activity is calculated:
Glucose μ g numbers, U=are converted into according to standard curve(M1-M0)/20
In formula:U:The enzyme activity of sample(μg/min); M0:Control glucose amount(μg)
M1:Example weight after decomposition(μg); 20:The enzyme-to-substrate response time(min)
1ml former state enzyme liquids, the μ g glucoses of generation per minute 1 are defined as 1 enzyme activity unit(u).
2nd, proteinase activity assay method
1st, reagent:According to the regulation in QB/T 1803.
2nd, the preparation of former state enzyme liquid
Weigh sample 10.0g(Or 10.0ml), add the triangular flask equipped with bead(150ml)In, add certain body Long-pending phosphate buffer(pH7.5)Dissolving, 200 r/min shaking tables vibration 30min, then four layers of filtered through gauze, filtrate then at 3000r/min is centrifuged 20min.Supernatant after centrifugation is according to enzyme activity buffer(pH7.5)Debita spissitudo is diluted to, for surveying It is on probation.
3rd, determination step:Other simply have in concrete measure according to the regulation of QB/T1803 and change at two:One is reaction Time(After adding casein)30min is changed to by 10min;Two is that former static filtration is changed to that 5min filtrations are centrifuged.
3rd, enzyme assay result
Bacillus subtilises, streptomyces microflavus, long handle Trichoderma spp., Bacillus mucilaginosus and composite bacteria agent capable will be prepared by upper The method of stating carries out cellulase and protease activity determination, and measurement result see the table below.
The enzyme activity implementations of table 5
Process Cellulase activity (u/ml) Proteinase activity (u/ml)
Bacillus subtilises 68.00 47.20
Streptomyces microflavus 12.51 -
Long handle Trichoderma spp. 95.08 15.74
Bacillus mucilaginosus 15.64 8.94
Composite bacteria agent capable 60.08 21.37
Testing result shows, by bacillus subtilises, streptomyces microflavus, long handle Trichoderma spp., 4 kinds of bacterial strains of Bacillus mucilaginosus The composite bacteria agent capable of composition has very strong cellulose and breaks down proteins ability, higher than organic matter decomposing inoculant national Specification Cellulase activity 30 (u/ml) and proteinase activity 15 (u/ml) requirement, composite bacteria agent capable can be used as organic material composting Agent is used.
Embodiment 5:
Single bacterial strain is determined with the fermentative deodorizing ability of composite bacteria agent capable
First, agents useful for same and fermentation substrate
1st, sulfuric acid solution:Sulphuric acid 0.005mol, with distilled water 1L is settled to.
2nd, starch indicator solution:1g starch adds distilled water 10ml, in injecting the distilled water that 200ml boils, micro-boiling 2min.
3rd, bromocresol green ethanol solution:0.10g bromocresol greens, with ethanol 100ml is settled to.
4th, C.I. 13020 .-bromocresol green indicator:The 0.1% bromocresol green ethanol solution and 0.2% methyl of 1 volume of 3 volumes Red ethanol solution mixing.
5th, acetic acid zinc solution:Weigh 50g zinc acetates to be dissolved in a small amount of distilled water, add 2 to drip glacial acetic acid, stir to solution and become It is limpid, add 2 to drip ethanol, it is settled to 1L with distilled water.
6th, C.I. 13020. ethanol solution is prepared:0.20g C.I. 13020 .s, with ethanol 100ml is settled to.
7th, boric acid solution:20.41g boric acid and 1000ml distilled water.
8th, iodine standard solution:13g iodine is dissolved in 100mL distilled water with 35g potassium iodide, and with distilled water 1000mL is settled to, Shake up and be stored in brown bottle.
9th, hypo solution:The water sodium thiosulfate of 13g five and 0.5g sodium carbonate, are settled to 1L, slowly with distilled water 10min is boiled, in being contained in brown bottle.
10th, hydrochloric acid(1+1)Solution:By 1 volume of water and the hydrochloric acid of 1 volume 37%.
11st, fermentative deodorizing substrate:It is made up of dried poultrymanure 60g, powder of straw 10g and water, water content is 50%.
2nd, assay method
The main component of the foul smell that compost is produced is ammonia and hydrogen sulfide, and the harm to people and animals is very big, main in embodiment The deodorizing capability of microbial bacterial agent is evaluated using ammonia detection, sulfurated hydrogen detection and organoleptic detection.
1st, ammonia detection method
The ammonia in gas is absorbed with 2% boric acid solution, is then titrated with 0.005mol/L sulfuric acid solutions, first dripped during titration Methylate is red-and bromocresol green mixed indicator 5-6 drops are in the boric acid solution for absorbing ammonia then molten with 0.005mol/L sulphuric acid Drop is fixed to arrive terminal up to pink, according to the consumption of sulfuric acid solution(Volume)Calculate ammonia level.
Reaction equation is:(1)NH3+H3BO3→NH4H2BO3;(2)NH4H2BO3+H2SO4→(NH4)2SO4+2H3BO3
The computing formula of the amount of the material of ammonia:n1=0.005*(V1-V01)*10-3;n1The amount of the material of-ammonia (mol), the substance withdrawl syndrome of 0.005-sulphuric acid(mol/L), V1The consumption of sulfuric acid solution when-test solution is titrated(ml), V01— The consumption of sulfuric acid solution during blank titration(ml).
2nd, sulfurated hydrogen detection method
Iodimetric titration is, with the hydrogen sulfide in acetic acid zinc-iron alloy solution unstripped gas, to add excess iodine standardized titration molten in slightly acidic solution Liquid is S2-Simple substance S is oxidized to, remaining iodine is titrated with hypo solution, according to hypo solution consumption, is calculated Hydrogen sulfide content;By 5mL iodine standard solutions, 5mL hydrochloric acid(1+1)Solution adds the 50g/L zinc acetate solutions for absorbing hydrogen sulfide In, confined reaction 5 minutes is titrated, the starch indicator of Deca 0.5% during nearly terminal, extremely with 0.05mol/L hypo solutions Become colorless, the volume of record hypo solution used, you can calculate the content of hydrogen sulfide.
The reaction equation of iodometric titrationiodimetry titration:(1)H2S+Zn2+→ZnS↓+2H+;(2)ZnS+I2→Zn2++2I-+S↓;(3)I2+ 2S2O3 2-→2I-+S4O6 2-
The computing formula of the amount of the material of hydrogen sulfide:n2=[0.5-0.05*(V02-V2)/2]*10-3;n2The thing of-hydrogen sulfide The amount of matter(mol), the amount of the material of 0.5-standard iodine solution(mol), the substance withdrawl syndrome of 0.05-hypo solution (mol/L), V02The consumption of hypo solution during-blank titration(ml), V2Hypo solution when-test solution is titrated Consumption(ml).
3rd, experimental technique
Bacillus subtilises after activation, Bacillus licheniformis, sporotrichum thermophile, aspergillus oryzae and Trichoderma viride are used respectively Fluid medium culture 2 days, obtains the bacterium solution of each bacterial strain.
The bacterium solution and composite bacteria agent capable of each bacterial strain are tested as follows respectively:Bacterium solution is connected on into fermentative deodorizing Medium Culture, Mix in 500mL beakers(Every part of fermentative deodorizing substrate is inoculated with 10mL bacterium solutions), as experiment sample, fermentative deodorizing substrate is set Used as check sample, each sample kraft paper and one layer of plastic paper are sealed.Each sample(Six kinds of experiment samples and a kind of control sample This)Three parallel processing are set, and each parallel processing arranges three repetitions, as a result takes the meansigma methodss of three repetitions.At first Contain in parallel middle placement 20mL 2% boric acid solution small beaker to absorb sweat in the ammonia that produces, the 7th day with acid Titration measuring;Produce during the 50g/L acetic acid zinc solutions of 20mL are contained in second parallel middle placement to absorb sweat Hydrogen sulfide, use iodometric determination within the 7th day;3rd parallel, carries out sense organ measure within the 7th day.
4th, experimental result
The results are shown in Table 6.
The fermentative deodorizing ability of table 6
Process Foul smell grade Ammonia level(10-3mol) Hydrogen sulfide content(10-3mol)
Bacillus subtilises + 0.00260 0.32321
Streptomyces microflavus + 0.00250 0.32509
Long handle Trichoderma spp. +++ 0.00325 0.43461
Bacillus mucilaginosus ++ 0.00310 0.40098
Composite bacteria agent capable + 0.00220 0.30765
Control ++++ 0.00713 0.65432
Note:How much expression sense organs of "+" determine foul smell grade, and "+" represents that sense organ measure is more smelly.
Show with reference to the testing result of organoleptic detection and ammonia and hydrogen sulfide content, by bacillus subtilises, thin Huang strepto- The composite bacteria agent capable deodorizing effect of bacterium, long handle Trichoderma spp. and Bacillus mucilaginosus composition is significantly better than single bacterial strain and control.
Embodiment 6:
Single bacterial strain is determined with the resistances against diseases of composite bacteria agent capable
Bacteriostatic test is carried out using steel ring method, by the bacillus subtilises after activation, streptomyces microflavus, long handle Trichoderma spp., glue Peptone sample bacillus cereuss and composite bacteria agent capable carry out bacteriostatic test with cucumber fusarium axysporum respectively, each three repetition of combination.
Each bacterial strain is cultivated 2-3 days in corresponding culture medium(190r/min, 28 DEG C)Fermentation liquid is made, by cultured Huang Cucurbit wilt bacterium makes spore concentration for 106The bacteria suspension of individual/mL.Take cucumber fusarium axysporum bacteria suspension 0.1mL and be applied to PDA plate On, the steel ring of two sterilizings in advance is then put on the solid medium of each flat board, then add in each steel ring Above-mentioned each fermented liquid of 0.25mL and composite bacteria liquid, each is processed in triplicate, only to connect cucumber fusarium axysporum bacteria suspension Plate is control.28 DEG C of cultures and routine observation antibacterial situation.
The each bacterial strain of table 7 and bacteriostasis of the composite bacteria agent capable to cucumber fusarium axysporum
Note:"+" represents that Antagonistic reaction is positive, and "+" represents that inhibition is bigger.
Result of the test shows, bacillus subtilises, streptomyces microflavus, long handle Trichoderma spp., Bacillus mucilaginosus and compound bacteria Agent has fungistatic effect to cucumber fusarium axysporum, and wherein composite bacteria agent capable is most strong.
Embodiment 7:
The effect of increasing production of single bacterial strain and composite bacteria agent capable
1st, test site and varieties of plant
Test vegetable is Caulis et Folium Brassicae capitatae.
2nd, field design
Totally 6 process, each processes 3 repetitions, conventional fertilizer application, plot area 96m2
Process 1:Bacillus subtilises;Process 2:Streptomyces microflavus;Process 3:Long handle Trichoderma spp.;Process 4:Glue peptone sample spore Bacillus;Process 5:Composite bacteria agent capable;Process 6:Control.
3rd, result of the test
The each bacterial strain of table 8 and composite bacteria agent capable field effect of increasing production
Process Cell average product (kg) Per mu yield(kg) Volume increase(%)
Process 1 480 3335 14.3
Process 2 482 3349 14.8
Process 3 478 3321 13.8
Process 4 490 3404 16.7
Process 5 495 3425 17.4
Process 6 420 2918 -
Result of the test shows, bacillus subtilises, streptomyces microflavus, long handle Trichoderma spp., Bacillus mucilaginosus and compound bacteria Agent has effect of increasing production on Caulis et Folium Brassicae capitatae is planted than control, and wherein composite bacteria agent capable is optimal, better than single bacterial strain, can exist as bacterial manure Used in farmland.
Embodiment 8:
The using method and effect of composite bacteria agent capable
By above example, illustrate by bacillus subtilises, streptomyces microflavus, long handle Trichoderma spp., Bacillus mucilaginosus 4 The composite bacteria agent capable of bacterium composition is planted, the effect with several functions can carry out the quick of feces of livestock and poultry as organic matter decomposing inoculant Become thoroughly decomposed, the deodorization of feces of livestock and poultry can be carried out as deodorizer, the preventing and treating of crop pest can be carried out as disease-resistant microbial inoculum, can also make For the cultivation that agricultural microbial agent is applied to crops, play a part of volume increase.
First, the using method of composite bacteria agent capable
1st, the carbon-nitrogen ratio of feces of livestock and poultry is adjusted(25~30:1)And moisture(55~60%, with handss one hold handss seam drip for Preferably), 1 kilogram of composite bacteria agent capable is added per 5 side's feces of livestock and poultry, turn over and smash uniform.
2nd, by feces of livestock and poultry heap trapezoidal, 1 meter of the heap top width of growth that pretreatment is good, 2 meters of heap bottom width, heap high summer and autumn 0.8~1 Rice, 1.2~1.4 meters of winter-spring season, depending on heap length is according to place, per heap volume 5 sides are no less than.
3rd, after fermentation starts, temperature of charge is worked as(20~30 centimetres of depths)Kept for three days when rising to 55 DEG C, then turn over and smash one It is secondary.If fermentation initial stage temperature does not rise, moisture is adjusted to recommendation ratio and turned over daily and smash once until heap temperature rises.
4th, after heap temperature rises to again 55 DEG C, kept for three days, then turn over and smash once;
5th, according to heap tender feeling condition carry out turning over smashing afterwards, temperature upward period is not turned over to be smash, temperature stops rising then to turn over smashing, and lays equal stress on Multiple the step for, when heap temperature is identical with outdoor temperature, moisture is down to below 30%, that is, sweat is completed, whole fermentation Cycle is usually 15~25 days.
2nd, the using effect of composite bacteria agent capable
1st, materials and methods
Composting material:Chicken manure, cattle manure, pig manure and brown coal.Weight ratio accounts for 40~60% for chicken manure;Cattle manure accounts for 20~40%;Pig Excrement 5~15%;Brown coal 5~15%.C/N ratios are 37.
If two process, are processed:Plus the invention feces of livestock and poultry decomposing microbial inoculum;Control:Not with the blank of microbial inoculum, often Individual process 2T raw materials, three repetitions are averaged, pile type fermentation reactor system.Fermentation period room temperature is down to by fermentation temperature in terms of Gained is calculated, fermentation is processed two and is sampled analysis, including available N, P, K total amount on the 16th day(%), C/N ratios, bacterium number and large intestine bar Bacterium, averages, and observes the physical state of fermentation, as a result as shown in the table:
2nd, result and analysis
The composite bacteria agent capable of table 9 becomes thoroughly decomposed and deodorizing effect
As shown in Table 9, from the point of view of indices, process ferment effect and be better than control, wherein process fermentation temperature is in 2 days 55 DEG C can be reached, control needs 5 days;The result of fermentation shows as processing micro organism quantity growth and breeding to be enlivened, bacterium number and speed Effect N, P, K content is above as shown in table 5 control, and fermentation period is also greatly shortened, wherein being processed as 16 days, compares 28 days, place Haircut ferment color pitchy, odorless, and it is light color to compare, and has stink.Fermentation post processing in 16 days and control C/N ratios are respectively 18.6th, than lower, microorganism acts on better to 23.0, C/N to feces of livestock and poultry cellulose degradation.Therefore, from bacterium number, available nutrient, From the point of view of C/N ratios, abnormal smells from the patient and fermentation period effect, illustrate to add the composite bacteria agent capable to feces of livestock and poultry become thoroughly decomposed and deodorization is all played Facilitation effect.
Embodiment 9:
Made biological organic fertilizer and Field information effect are produced using composite bacteria agent capable
Under the conditions of certain site facility, there is biodegradation, chemical degradation by adding decomposing microbial inoculum, feces of livestock and poultry And physical change, produce CO2、H2O and NH3Deng gas and discharge heat, generating can absorb small molecule by crop conversion in a large number Inorganic and organic nutrient substance, form stable physical arrangement and state, obtain bio-organic fertilizer of the present invention and produce Product.
First, the production of biological organic fertilizer and technique
1st, raw material and formula:Biological organic fertilizer raw materials for production include chicken manure, cattle manure, four kinds of organic materials of pig manure and brown coal. By weight, chicken manure accounts for 40~60%;Cattle manure accounts for 20~40%;Pig manure 5~15%;Brown coal 5~15%.
2nd, material choice:The chicken manure content of organic matter >=45%, total nitrogen content >=2.5%;The cattle manure content of organic matter >=50%;Pig The excrement content of organic matter >=45%;Lignite humic acid content >=50%.
3rd, proportioning raw materials:Weigh by weight 40~60% chicken manure, 20~40% cattle manure, 5~15% pig manure and 5~ 15% brown coal.
4th, the mixing of raw material:The dried poultrymanure, dry cow dung, dry pig manure and brown coal that weigh by weight are filled with batch mixer Divide and mix.
5th, add water:By water:Mixed material 1:1 weight ratio adds water, and control water content is 50~60% or so.
6th, composite bacteria agent capable of the present invention is added:1 kilogram of composite bacteria agent capable is added per 5 side's feces of livestock and poultry
7th, bank up specification:By regulate water and add composite bacteria agent capable feces of livestock and poultry heap grow up trapezoidal, 1 meter of heap top width, 2 meters of heap bottom width, 0.8~1 meter of heap high summer and autumn, 1.2~1.4 meters of winter-spring season depending on heap length is according to place, are no less than per heap volume 5 sides.
8th, the control of turning time:After fermentation of banking up starts, if fermentation initial stage temperature does not rise, such as moisture content not enough, is then adjusted Whole moisture such as moisture content excess, then must daily be turned over and smash once to recommendation ratio 50~60%, increase oxygen content in pile, promote micro- Biological fast-growth, until heap temperature rises.Work as temperature of charge(20~30 centimetres of depths)Kept for three days when rising to 55 DEG C, then turned over Smash once, harmful pathogenic microorganism such as excrement enterobacteria and roundworm egg and worm's ovum are killed with profit.After heap temperature rises to again 55 DEG C, protect Hold three days, then turn over and smash once.Carry out turning over smashing according to heap tender feeling condition afterwards, temperature upward period is not turned over to be smash, temperature stops rising Then turn over and smash, when temperature is more than 70 DEG C, need to carry out turning over immediately smashing, suppression of the high temperature to growth of microorganism is eliminated by cooling, from And promote the activity of a large amount of mesophilic bacterias, accelerate the process of compost.
9th, turning is required:Turn over and to accomplish during pile tune, even, broken.Adjust is exactly that original top section in pile is transferred to earth's surface Become underclad portion, and underclad portion is transferred to top layer and is changed into top section, to reach the purpose of abundant fermentation;Even is exactly in pile Raw material mixes also uneven part, and mixing work is carried out again;Broken is exactly the massive zymolysis thing to being formed during the fermentation Carry out broken work.
10th, the addition of object bacteria:After fermentation the phase, i.e., when fermentation starts cooling, add Bacillus mucilaginosus list bacterium Strain microbial inoculum, is 1kg per square object material addition.
11st, fermentation termination control:When heap temperature is identical with outdoor temperature, moisture is down to less than 30%, outward appearance pitchy, odorless, The whole fermentation production process of biological organic fertilizer is completed, whole cycle is usually 15~20 days, 25~30 days time in winter.
12nd, fermented quality control:Crushed after the completion of fermentation, sieved, detected, weighed and packed, bio-organic fertilizer Production is completed.Bio-organic fertilizer organic matter requires to reach 45%~55%, N, P, K total nutrient 5%, living bacteria count > 0.2 ×108Individual/g, excrement colibacillus group number is negative, induced worm egg death rate 100%.
Because the composite bacteria agent capable collects cellulose decomposition, breaks down proteins, deodorization, disease-resistant and bacterial manure several functions in one Body, after adding feces of livestock and poultry material, on the one hand probioticss decompose the feces of livestock and poultry that becomes thoroughly decomposed and form stable biological organic fertilizer, on the one hand Itself expanding propagation is carried out using feces of livestock and poultry, own disease-resistant and bacterial manure function is transplanted in the biological organic fertilizer for generating, The biological organic fertilizer for making generation is equally provided with the multiple performances such as disease-resistant and bacterial manure, sees technological process Fig. 1.
2nd, using method
200~500 kilograms are applied with per mu as base manure, is spread fertilizer over the fields before ploughing and earth's surface, then uniformly apply with being ploughed Use as base manure in soil;Trench digging is sprinkled into fertilizer in field of vegetables during ditch spread, then moves seedling or dibbling, 200 kilograms of left sides of mu consumption It is right;Dibbling or when transplanting, can take the method spreaded manuer in holes, and can be put in every cave after the mixing of fertilizer and fine earth, then transplant again or Dibbling, 10 kilograms or so of mu consumption.
3rd, Field information effect
Trial crops are Herba Alii fistulosi, and soil situation is available nitrogen 73PPm, rapid available phosphorus 33PPm, available potassium 165PPm, organic matter 1.85%, total salt 0.117%, pH7.89, plot area 40m2, test area is 0.36 mu, 10 mu of area of demonstrating.
EXPERIMENTAL DESIGN:If two process:1st, conventional fertilizer application+biological organic fertilizer, 2, conventional fertilizer application(Control);Three repetitions, Order is arranged.Result of the test is as shown in table 10:
The biological organic fertilizer Field information effect of table 10
Result of the test shows that biological organic fertilizer of the present invention has obvious disease-resistant yield-increasing effect, and preventive effect increases up to 56% Produce up to 20.5%.

Claims (2)

1. a kind of preparation method of bio-organic fertilizer, its feature is carried out by the steps:
(1)The mixing of raw material:Fully mixed with batch mixer dried poultrymanure, dry cow dung, dry pig manure and brown coal are weighed by weight, The parts by weight of described feces of livestock and poultry are as follows:40~60 parts of chicken manure;20~40 parts of cattle manure;5~15 parts of pig manure;Brown coal 5~15 Part;The wherein chicken manure content of organic matter >=45%, total nitrogen content >=2.5%;The cattle manure content of organic matter >=50%;The pig manure content of organic matter ≥45%;Lignite humic acid content >=50%.
(2)Add water:By water and mixed material 1:1 weight ratio adds water, and control water content is 50~60%;
(3)Add feces of livestock and poultry decomposing agent:1 kilogram of composite bacteria agent capable, described feces of livestock and poultry is added to become thoroughly decomposed bacterium per 5 side's feces of livestock and poultry Agent is composited by decomposable asymmetric choice net cellulose, protein, deodorization, disease-resistant and bacterial manure several functions various bacterial strains, its activity into Dividing includes bacillus subtilises(Bacillus subtilis), streptomyces microflavus(Streptomyces microflavus), it is long Handle Trichoderma spp.(Trichoderma longbrachiatum)And Bacillus mucilaginosus(Bacillus mucilaginosus), it It is made up of each single strain fermented product of following portions by weight:0.5~2 part of bacillus subtilises, 0.5~2 part of streptomyces microflavus, 0.5~2 part of 0.5~2 part of long handle Trichoderma spp. and Bacillus mucilaginosus;Poultry manure decomposing agent living bacteria count is 6 × 108Individual/g;
(4)Bank up specification:By regulate water and add composite bacteria agent capable feces of livestock and poultry heap grow up trapezoidal, 1 meter of heap top width, heap bottom Wide 2 meters, 0.8~1 meter of heap high summer and autumn, 1.2~1.4 meters of winter-spring season depending on heap length is according to place, per heap volume 5 sides are no less than;
(5)The control of turning time:Kept for three days when 20~30 centimetres of depths temperature of charge rise to 55 DEG C, then turn over and smash one It is secondary, after heap temperature rises to again 55 DEG C, kept for three days, then turn over and smash once, carry out turning over smashing according to heap tender feeling condition afterwards, in temperature The period of liter does not turn over and smashes, and temperature stops rising then to turn over smashing, and the step for repetition, when temperature is increased beyond 70 DEG C, need to enter immediately Row is turned over to be smash, and by cooling suppression of the high temperature to growth of microorganism is eliminated, and so as to promote the activity of a large amount of mesophilic bacterias, accelerates compost Process;
(6)Turning is required:Turn over and to accomplish during pile tune, even, broken, it is exactly that original top section in pile is transferred to earth's surface to become to adjust Underclad portion, and underclad portion is transferred to top layer and is changed into top section, to reach the purpose of abundant fermentation;Even is exactly to raw material in pile The also uneven part of mixing, carries out again mixing work;Broken is exactly that the massive zymolysis thing to being formed during the fermentation is carried out Broken work;
(7)The addition of object bacteria:After fermentation the phase, i.e., when fermentation starts cooling, add Bacillus mucilaginosus single strain bacterium Agent, is 1 kilogram per square object material addition;
(8)Fermentation termination is controlled:When heap temperature is identical with outdoor temperature, moisture is down to less than 30%, that is, complete biological organic fertilizer Whole fermentation production process, whole cycle is usually 15~20 days, 25~30 days time in winter;
(9)Fermented quality is controlled:Crushed after the completion of fermentation, sieved, detected, weighed and packed, bio-organic fertilizer product Production is completed, and bio-organic fertilizer organic matter requires to reach 45%~55%, N, P, K total nutrient 5%, and living bacteria count > 0.2 × 108Individual/g, excrement colibacillus group number is negative, induced worm egg death rate 100%.
2. application of the biological organic fertilizer described in claim 1 in terms of vegetable disease-resistant effect of increasing production is improved.
CN201410242443.1A 2014-06-03 2014-06-03 Livestock and poultry manure decomposing inoculant, use method thereof and biological organic fertilizer prepared by using livestock and poultry manure decomposing inoculant Active CN103980010B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201410242443.1A CN103980010B (en) 2014-06-03 2014-06-03 Livestock and poultry manure decomposing inoculant, use method thereof and biological organic fertilizer prepared by using livestock and poultry manure decomposing inoculant

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410242443.1A CN103980010B (en) 2014-06-03 2014-06-03 Livestock and poultry manure decomposing inoculant, use method thereof and biological organic fertilizer prepared by using livestock and poultry manure decomposing inoculant

Publications (2)

Publication Number Publication Date
CN103980010A CN103980010A (en) 2014-08-13
CN103980010B true CN103980010B (en) 2017-05-17

Family

ID=51272215

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410242443.1A Active CN103980010B (en) 2014-06-03 2014-06-03 Livestock and poultry manure decomposing inoculant, use method thereof and biological organic fertilizer prepared by using livestock and poultry manure decomposing inoculant

Country Status (1)

Country Link
CN (1) CN103980010B (en)

Families Citing this family (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104193434A (en) * 2014-09-01 2014-12-10 中山市巴斯德农业科技有限公司 Method for preparing biological organic fertilizer by using cow dung
CN105175051A (en) * 2015-08-14 2015-12-23 广西壮族自治区农业科学院农业资源与环境研究所 Bio-organic fertilizer employing pig dung as raw material and preparation method therefor
CN105154373A (en) * 2015-10-08 2015-12-16 山东大学 High-temperature cow dung decomposition agent and preparation method thereof
CN106083460A (en) * 2016-06-13 2016-11-09 镇江贝思特有机活性肥料有限公司 A kind of bio-feritlizer preventing and treating watermelon blight
CN105948946A (en) * 2016-06-29 2016-09-21 固镇县华丰蔬菜专业合作社 Microbial fertilizer for preventing green Chinese onions from rust disease
CN108485995A (en) * 2018-03-19 2018-09-04 辽宁省农业科学院 A kind of complex micro organism fungicide and biological organic fertilizer promoting hickory chick growth
CN108299033A (en) * 2018-04-17 2018-07-20 福建圣德生物科技有限公司 A kind of biological organic fertilizer and its preparation method
CN109824393A (en) * 2019-04-09 2019-05-31 河北省农林科学院农业资源环境研究所 A kind of compost method reducing ammonia emission in animal waste fermentation process
CN110105152A (en) * 2019-05-16 2019-08-09 宿迁润沃生物科技有限公司 A method of organic fertilizer is made using feces of livestock and poultry
CN112852666A (en) * 2021-01-19 2021-05-28 新疆河润水业有限责任公司 Preparation method of microbial agent and microbial fertilizer prepared by adopting microbial agent
CN114561329B (en) * 2022-04-21 2023-03-21 中国农业科学院农业资源与农业区划研究所 Compound microbial inoculum for fermenting livestock and poultry manure and fermentation method thereof
CN117567214B (en) * 2023-12-04 2024-08-20 内蒙古生态环境科学研究院有限公司 Composite organic fertilizer for soil improvement and restoration and preparation method thereof

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102199562A (en) * 2011-03-22 2011-09-28 四川农业大学 Composite bacterial preparation as well as preparation method and application thereof
CN102690769A (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 efficiently degrading feces and preparation method and application of compound microbial bacterial preparation
CN102898189A (en) * 2012-09-29 2013-01-30 洋县益民绿色农业科技有限责任公司 Method for producing functional biological organic base fertilizer by using poultry excrement
CN103232944A (en) * 2013-04-25 2013-08-07 南京林业大学 Microorganism bacterium agent for straw and excrement mixed composting
CN103289930A (en) * 2013-06-05 2013-09-11 中国海洋大学生物工程开发有限公司 Microbial rotten bacterium agent as well as preparation method and application thereof
CN103497899A (en) * 2013-09-29 2014-01-08 北京农学院 Biologically-fermented organic fertilizer and preparation method thereof
CN103508760A (en) * 2013-10-10 2014-01-15 宣城市南阳生物科技有限公司 Method for utilizing chicken manure to produce organic fertilizer
CN103787729A (en) * 2013-09-13 2014-05-14 保康丰源肥业有限责任公司 Organic fertilizer and preparation method thereof

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102199562A (en) * 2011-03-22 2011-09-28 四川农业大学 Composite bacterial preparation as well as preparation method and application thereof
CN102690769A (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 efficiently degrading feces and preparation method and application of compound microbial bacterial preparation
CN102898189A (en) * 2012-09-29 2013-01-30 洋县益民绿色农业科技有限责任公司 Method for producing functional biological organic base fertilizer by using poultry excrement
CN103232944A (en) * 2013-04-25 2013-08-07 南京林业大学 Microorganism bacterium agent for straw and excrement mixed composting
CN103289930A (en) * 2013-06-05 2013-09-11 中国海洋大学生物工程开发有限公司 Microbial rotten bacterium agent as well as preparation method and application thereof
CN103787729A (en) * 2013-09-13 2014-05-14 保康丰源肥业有限责任公司 Organic fertilizer and preparation method thereof
CN103497899A (en) * 2013-09-29 2014-01-08 北京农学院 Biologically-fermented organic fertilizer and preparation method thereof
CN103508760A (en) * 2013-10-10 2014-01-15 宣城市南阳生物科技有限公司 Method for utilizing chicken manure to produce organic fertilizer

Also Published As

Publication number Publication date
CN103980010A (en) 2014-08-13

Similar Documents

Publication Publication Date Title
CN103980010B (en) Livestock and poultry manure decomposing inoculant, use method thereof and biological organic fertilizer prepared by using livestock and poultry manure decomposing inoculant
CN103981107B (en) A kind of multifunctional agricultural microbiobacterial agent and using method thereof and effect
CN103980019B (en) A kind of cultural solid organic waste mesopilous organisms zymotechnique and application
CN103966149B (en) A kind of house refuse and sludge decomposing microbial inoculum and its application and made decomposed matrix
CN103524253B (en) A kind of seedling medium and preparation method thereof and purposes
CN103641522B (en) Crop straw decomposing inoculant and using method
CN106434430A (en) Compound microbial agent for degrading antibiotic and pesticide residues as well as preparation and application thereof
CN105462878B (en) A kind of efficient decomposing agent of feces of livestock and poultry and its fermentation process
CN110305671A (en) One kind is for facilities vegetable continuous cropping soil biological modification agent and its preparation and application method
CN104263677A (en) Composite microbial seed dressing agent and preparation method and application of composite microbial seed dressing agent
CN107365725A (en) A kind of organic matter decomposing inoculant and preparation method thereof
CN101781153A (en) Organic fertilizer for killing underground injurious insect and preparation method thereof
CN102826875B (en) Microbial organic fertilizer and purpose of microbial organic fertilizer
CN106045677A (en) Method for preparing organic compound biological fertilizer special for fruit trees
CN106699423A (en) Lycium barbarum root rot biocontrol preparation and preparation method thereof
CN103980020B (en) The biological organic fertilizer that a kind of decomposing microbial inoculum and natural organic matter material produce
CN102972192B (en) Method for improving pathogen-inhibiting and disease-controlling pesticide effect of rapeseed meal by applying myrosinase preparation in field
CN106146076A (en) A kind of method that liquid manure of livestock and poultry that ferments manufactures biological organic fertilizer
CN110200017A (en) A kind of complex micro organism fungicide and preparation method thereof for preventing and treating root-knot nematode
CN105777452A (en) Straw compound organic fertilizer and preparation method thereof
CN108676760A (en) A kind of organic fertilizer decomposing agent and preparation method thereof
CN108640751A (en) A kind of microbial manure, preparation method and application for preventing Radix Angelicae Sinensis root rot
CN106399167A (en) Biocontrol agent for lily continuous cropping obstacles and preparation method
CN110511892A (en) A kind of organic fertilizer fermentation microbial inoculum and its application
CN110257277A (en) A kind of composite bacteria agent ZLM-11 and its application

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20210113

Address after: Room 217-10, 123 Yuhua street, Baodi District, Tianjin 301800

Patentee after: Tianlan Diwo (Tianjin) Agricultural Technology Co.,Ltd.

Address before: 300380 Biological Center building, 17 km away from Jinjing Road, Xiqing District, Tianjin

Patentee before: TIANJIN INSTITUTE OF AGRICULTURAL RESOURCES AND ENVIRONMENT SCIENCE