CN102775201B - Carbon-sequestering high-activity microbial organic fertilizer and preparation method thereof - Google Patents
Carbon-sequestering high-activity microbial organic fertilizer and preparation method thereof Download PDFInfo
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- CN102775201B CN102775201B CN201210252826.8A CN201210252826A CN102775201B CN 102775201 B CN102775201 B CN 102775201B CN 201210252826 A CN201210252826 A CN 201210252826A CN 102775201 B CN102775201 B CN 102775201B
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- 230000000694 effects Effects 0.000 title claims abstract description 41
- 238000002360 preparation method Methods 0.000 title claims description 17
- 230000000813 microbial effect Effects 0.000 title abstract description 14
- 239000003895 organic fertilizer Substances 0.000 title abstract description 13
- 238000002156 mixing Methods 0.000 claims abstract description 57
- 239000000463 material Substances 0.000 claims abstract description 46
- 230000004151 fermentation Effects 0.000 claims abstract description 36
- 241000193388 Bacillus thuringiensis Species 0.000 claims abstract description 34
- 229940097012 bacillus thuringiensis Drugs 0.000 claims abstract description 34
- 238000000855 fermentation Methods 0.000 claims abstract description 34
- 235000021419 vinegar Nutrition 0.000 claims abstract description 27
- 239000000052 vinegar Substances 0.000 claims abstract description 27
- 239000002054 inoculum Substances 0.000 claims abstract description 23
- 239000002023 wood Substances 0.000 claims abstract description 21
- 239000010815 organic waste Substances 0.000 claims abstract description 19
- 238000010564 aerobic fermentation Methods 0.000 claims abstract description 14
- 239000002028 Biomass Substances 0.000 claims abstract description 7
- 239000003337 fertilizer Substances 0.000 claims description 56
- 244000005700 microbiome Species 0.000 claims description 51
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 43
- 229910052799 carbon Inorganic materials 0.000 claims description 43
- 150000001875 compounds Chemical class 0.000 claims description 30
- 239000002994 raw material Substances 0.000 claims description 21
- 239000007787 solid Substances 0.000 claims description 20
- 239000003795 chemical substances by application Substances 0.000 claims description 17
- 239000000428 dust Substances 0.000 claims description 17
- 239000000843 powder Substances 0.000 claims description 17
- 239000010902 straw Substances 0.000 claims description 17
- 241000187654 Nocardia Species 0.000 claims description 15
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 11
- 229910052760 oxygen Inorganic materials 0.000 claims description 11
- 239000001301 oxygen Substances 0.000 claims description 11
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 11
- 230000001580 bacterial effect Effects 0.000 claims description 9
- 241000194108 Bacillus licheniformis Species 0.000 claims description 7
- 241000233866 Fungi Species 0.000 claims description 7
- 241000222393 Phanerochaete chrysosporium Species 0.000 claims description 7
- 238000005273 aeration Methods 0.000 claims description 4
- 235000013305 food Nutrition 0.000 claims description 3
- 239000010802 sludge Substances 0.000 claims description 3
- 239000002699 waste material Substances 0.000 claims description 3
- 241001503642 Nocardia seriolae Species 0.000 abstract 2
- 230000035558 fertility Effects 0.000 abstract 1
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 14
- 239000002689 soil Substances 0.000 description 13
- 239000002361 compost Substances 0.000 description 11
- 238000000034 method Methods 0.000 description 11
- 238000009264 composting Methods 0.000 description 7
- 229910052757 nitrogen Inorganic materials 0.000 description 7
- 239000000047 product Substances 0.000 description 7
- 239000000126 substance Substances 0.000 description 7
- 235000017166 Bambusa arundinacea Nutrition 0.000 description 6
- 235000017491 Bambusa tulda Nutrition 0.000 description 6
- 241001330002 Bambuseae Species 0.000 description 6
- 235000015334 Phyllostachys viridis Nutrition 0.000 description 6
- 239000011425 bamboo Substances 0.000 description 6
- 230000008569 process Effects 0.000 description 6
- 230000008901 benefit Effects 0.000 description 5
- 238000004519 manufacturing process Methods 0.000 description 4
- 239000002068 microbial inoculum Substances 0.000 description 4
- 239000000203 mixture Substances 0.000 description 3
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- 238000011081 inoculation Methods 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 244000144972 livestock Species 0.000 description 2
- 239000002910 solid waste Substances 0.000 description 2
- 238000005507 spraying Methods 0.000 description 2
- 238000009423 ventilation Methods 0.000 description 2
- RZVAJINKPMORJF-UHFFFAOYSA-N Acetaminophen Chemical compound CC(=O)NC1=CC=C(O)C=C1 RZVAJINKPMORJF-UHFFFAOYSA-N 0.000 description 1
- 241000196324 Embryophyta Species 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 1
- 208000027418 Wounds and injury Diseases 0.000 description 1
- 230000009471 action Effects 0.000 description 1
- 239000003905 agrochemical Substances 0.000 description 1
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical group N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 1
- 244000052616 bacterial pathogen Species 0.000 description 1
- 230000033228 biological regulation Effects 0.000 description 1
- 238000009395 breeding Methods 0.000 description 1
- 230000001488 breeding effect Effects 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 238000005056 compaction Methods 0.000 description 1
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- 230000001877 deodorizing effect Effects 0.000 description 1
- 210000003608 fece Anatomy 0.000 description 1
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- 150000007524 organic acids Chemical class 0.000 description 1
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- 150000002989 phenols Chemical class 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
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- 239000011591 potassium Substances 0.000 description 1
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Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
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- Fertilizers (AREA)
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
Abstract
The invention provides a carbon-sequestering high-activity microbial organic fertilizer. The carbon-sequestering high-activity microbial organic fertilizer comprises, by weight, 50-60 parts of organic waste residues, 15-35 parts of biomass auxiliary materials, 0.1-0.2 part of wood vinegar, 20-30 parts of back-mixing materials and 0.1-0.2 part of microbial inoculants, and is characterized in that the microbial inoculants at least include bacillus thuringiensis and nocardia seriolae. Growth of aerobic fermentation microbes can be accelerated by adding the bacillus thuringiensis and/or the nocardia seriolae, so that fermentation time is shortened, fermentation is accelerated, the content of active microbes in the organic fertilizer is increased, and fertility is improved.
Description
Technical field
The present invention relates to microbial organic fertilizer field, be specifically related to a kind of fowl and animal excrement or industrial organic waste residues solid carbon high-activity microorganism fertilizer obtaining and preparation method thereof that ferments that utilizes.
Background technology
The consumption of China's agrochemical constantly increases in recent years, and the consumption in average every mu of farmland has reached kg rank, is 2 times of developed country's chemical fertilizer safely use upper limit.The excessive use of chemical fertilizer has brought the problems such as soil compaction, organic content decline, space plug closes, make productivity and the structure of soil be subject to great destruction, and the change of Soil structure further makes, the utilising efficiency of chemical fertilizer is low, turnover rate increases, the loss of a large amount of chemical fertilizer has caused serious pollution of area source, and the ecotope enclosing to complete cycle has brought great injury.
In order to reduce the use of chemical fertilizer, recover structure and the composition composition of soil, finally recover the productivity in soil, China starts to promote the use of fertilizer the beginning of this century and replaces chemical fertilizer.The kind of fertilizer is more at present, and wherein microorganism organism has obtained development faster in recent years under the guidance of national fertilizer standard.The microbial organic fertilizer organic fertilizer that to be organic solid waste (comprising the solid waste that organic waste, stalk, feces of livestock and poultry, grouts, agricultural byproducts and food-processing produce) form through microorganism fermentation, deodorizing and the post-treatment that becomes thoroughly decomposed completely.As Chinese patent literature CN101016216A discloses a kind of method of bamboo vinegar to livestock culture waste effectively compost of utilizing, concrete steps are: first control the initial aqueous rate of composting material between 62-68%, carbon/nitrogen ratio is controlled at 25%, mix bamboo vinegar the forced ventilation of rear sprinkling after dilution and carry out aerobic compost, in composting process, control top temperature below 65 DEG C, after compost 5-7 days, after spraying the bamboo vinegar after dilution again, wait compost to finish completely, raw material surface is applied to farmland through can be used as fertilizer after one month become thoroughly decomposed again.Above-mentioned compost method is by spraying bamboo vinegar, and owing to containing organic acid, phenols etc. in bamboo vinegar, the foul smell that fowl and animal excrement is given out has played the effect that absorbs and cover, and has improved the air ambient of composting plant.Except using bamboo vinegar liquid, Chinese patent CN102180744A also discloses a kind of method that uses pyroligneous liquor organic fertilizer to be carried out to sterilization, taste removal.
But, the defect that above-mentioned prior art still exists is, the fermentation time that mentioned microorganism fertilizer needs in preparation process is all long, especially during taking fowl and animal excrement as main raw material, conventionally the fermentation time that needs 20 ~ 25 days, this just makes the whole production cycle of fertilizer longer, has affected the production efficiency of fertilizer, has increased production cost.In addition, although the content of living microorganism can reach the standard of 0.2 hundred million/g of national regulation in the microbial organic fertilizer preparing in prior art, but from microbiological angle, the content of living microorganism is old larger room for promotion still, how can effectively improve the content of living microorganism in fertilizer, be a still unsolved difficult problem of prior art.
Summary of the invention
All long in order to solve the fermentation time that microbial organic fertilizer of the prior art needs in composting process, and in prior art, lack the problem that can effectively improve living microorganism content in fertilizer, the invention provides solid carbon high-activity microorganism fertilizer that a kind of fermentation time is short, production efficiency is high and the content of living microorganism is higher and preparation method thereof.
The technical scheme of solid carbon high-activity microorganism fertilizer of the present invention and preparation method thereof is:
One is carbon high-activity microorganism fertilizer admittedly, comprises the raw material of following weight part:
Organic waste residues, 50-60 part;
Biomass auxiliary material, 15-35 part;
Back-mixing material, 20-30 part;
Wood vinegar, 0.1-1.0 part;
Microbiobacterial agent, 0.1-1.0 part;
It is characterized in that, described microbiobacterial agent comprises bacillus thuringiensis and Nocardia bacteria, and the ratio of described bacillus thuringiensis and nocardial inoculum size is 3:1-8:1.
Described organic waste residues is one or more in fowl and animal excrement, food service industry waste residue, biological sludge, and the water ratio of described organic waste residues is lower than 80%.
Described wood vinegar is 0.1 ~ 0.2 weight part, and described microbiobacterial agent is 0.1-0.2 weight part.
Described biomass auxiliary material is straw powder and stalk carbon dust, and wherein said straw powder is 10-20 weight part, and described stalk carbon dust is 5-15 weight part.
The ratio of described bacillus thuringiensis and nocardial inoculum size is 6:1.
Described microbiobacterial agent also comprises subtilis, Bacillus licheniformis, white-rot fungi and Phanerochaete chrysosporium;
In described microbiobacterial agent, bacillus thuringiensis and nocardial inoculum size account for 80% of total bacterial classification inoculum size.
The preparation method of described solid carbon high-activity microorganism fertilizer, comprising:
(1) organic waste residues is mixed with biomass auxiliary material, then add push after wood vinegar and microbiobacterial agent mixing;
(2) send pushing the mixing compound obtaining through step (1) into fermenter, in described fermenter, add back-mixing material, controlled fermentation temperature is carried out aerobic fermentation lower than 60 DEG C, until temperature completes fermentation while no longer increasing, completes the grog that fermentation obtains and is finished product.
In fermenter in described step (2), the piling height of compound and back-mixing material is no more than 2m.
Described step is put into compound after fermenter in (2), the back-mixing material that is 10-50cm at the surface coverage thickness of described compound.
In the aerobic fermentation process of described step (2), when the dark 1m of the mixing stockpile place oxygen content in fermenter is lower than 1% time, described compound is carried out to aeration, until oxygen concn is increased to 10%.
The advantage of solid carbon high-activity microorganism fertilizer of the present invention is:
(1) solid carbon high-activity microorganism fertilizer of the present invention, comprises that 50 ~ 60 weight part water ratio are lower than 80% organic waste residues; The straw powder of 15-35 weight part and/or stalk carbon dust; The wood vinegar of 0.1 ~ 0.2 weight part; The back-mixing material of 20 ~ 30 weight parts.The material of back-mixing described in the present invention completes the fertilizer finished product after fermentation, and a part for the grog cleaning out from fermenter can be used as back-mixing material and sends into next preparation section.When fertilizer in first preparation the present invention, do not add described back-mixing material, in the time of operation for the second time, add the fertilizer finished product preparing for the first time, after circulation several times at first, can obtain stable finished product.The present invention is by adding appropriate back-mixing material, and the suitable raw material of other ratio prepares fertilizer jointly, and advantage is: 1, above-mentioned raw materials has suitable water ratio and porosity, has ensured the conveying of oxygen in material, is conducive to the aerobic fermentation of microorganism; Although 2, in above-mentioned raw materials, the temperature-rise period of various raw materials is different, adjust the ratio of each raw material by adding back-mixing material simultaneously, ensure that the intensification route of aerobic composting process meets the thermodynamic (al) principle that heats up, be conducive to the fermentation of microorganism; 3, the present invention is by adding back-mixing material and adjusting the ratio of each raw material, make to pile in body is rapidly heated and can also maintain the long period in the pliotherm period in promotion, and hot stage can be killed parasite and pathogenic bacteria in compost, also be the period that soil ulmin forms simultaneously, therefore the raw material of the definite suitable proportion of this patent had both ensured compost quality, had improved again the total amount of compost finished product.4, in conventional composting process, nitrogen loss rate reaches 30% ~ 50% of total nitrogen, and the present invention is by limiting kind and the proportionlity thereof of raw material, can control preferably nitrogen in compost to accumulate with ammonium nitrogen form, and reduces nitrogen loss.
On the basis of above-mentioned raw materials, the present invention has also added bacillus thuringiensis and/or Nocardia bacteria in raw material, these two kinds of bacterial classifications have purification to aerobic fermentation microorganism, can accelerate aerobic fermentation microbial growth by adding described bacillus thuringiensis and/or Nocardia bacteria, thereby shorten fermentation time, improve fermentation efficiency, and promote the content of microorganism in fertilizer, microbial organic fertilizer fermentation in the present invention is fast, do not need to carry out Secondary Fermentation, do not need digest process of the prior art.Meanwhile, the interpolation of wood vinegar has also been played promoter action to microbial growth, and the living microorganism content of the microbial organic fertilizer in the present invention can reach 100,000,000 (10 × 10
7)/g, be the 3-5 of fertilizer in prior art doubly.Described in control of the present invention, the ratio of bacillus thuringiensis and nocardial inoculum size is 3:1-8:1, advantage is that this ratio can ensure to give full play to the advantage function of inoculation microbial inoculum, can reduce again the competition between the indigenous microorganism in inoculation microbial inoculum and composting process simultaneously, prevent that certain quasi-microorganism from utilizing emulative occupy-place and the ability of squeezing to stop and repel other microorganisms, be conducive to the biocenological diversity of compost, as preferably, the ratio that the present invention also limits described bacillus thuringiensis and nocardial inoculum size is 6:1.
(2) solid carbon high-activity microorganism fertilizer of the present invention, also comprise stalk carbon dust, described stalk carbon dust is being applied to after soil, and the simple substance carbon in described carbon dust can be substantially irreversibly fixed in soil, and the carbon that has increased soil converges, in addition, utilize the fluffy characteristic of stalk carbon dust, the porosity structure of the soil that can also increase sharply, improves the ventilation effect of soil, be conducive to crop root fixed nitrogen and breathing, rapid-action to the improvement of soil.Solid carbon high-activity microorganism fertilizer described in the present invention, in the situation that every mu using 3 tons, carbon remittance increasing amount is no less than 100kg/ ton, and the voidage increase of soil is no less than 30%.
(3) solid carbon high-activity microorganism fertilizer of the present invention, has also added the straw powder of some amount, and described straw powder can increase the content of the nutritions such as nitrogen, phosphorus, potassium, can also effectively reduce the water ratio of compost simultaneously.
(4) solid carbon high-activity microorganism fertilizer of the present invention, also comprises subtilis, Bacillus licheniformis, white-rot fungi and Phanerochaete chrysosporium; Described subtilis, Bacillus licheniformis, white-rot fungi and Phanerochaete chrysosporium are added simultaneously and have combination advantage, can promote the breeding of bacterial classification, and the combination of above-mentioned bacterial classification can high-efficiency lignin degrading and many persistence and toxic organic pollutant.
In order to make technical solutions according to the invention more be convenient to understand, below in conjunction with embodiment, technical solutions according to the invention are described further.
Embodiment
In the following embodiments, 1 weight part is 100 grams;
embodiment 1
High-activity microorganism fertilizer described in the present embodiment, comprises the raw material of following weight part:
Water ratio is organic fermentation residue of 90%, 50 parts;
Sawdust, 15 parts;
Back-mixing material, 20 parts;
Wood vinegar, 0.1 part;
Bacillus thuringiensis and Nocardia bacteria, 0.1 part;
The ratio of described bacillus thuringiensis and nocardial inoculum size is 3:1;
Organic fermentation residue described in the present embodiment is from pharmaceutical industry.
The preparation method of the high-activity microorganism fertilizer described in the present embodiment, comprising:
1) organic waste residues is mixed with straw powder, then add push after wood vinegar and bacillus thuringiensis, Nocardia bacteria mixing;
2) sending into fermenter through the mixing compound obtaining of step 1) extruding, in described fermenter, add back-mixing material, described compound and back-mixing material are stirred, in fermenter, the piling height of compound and back-mixing material is 3m, controlled fermentation temperature is carried out aerobic fermentation lower than 60 DEG C, when leavening temperature is during higher than 60 DEG C, carry out turning operation once, until temperature completes fermentation while no longer increasing;
3) in fermenter, clear up grog, send into stockyard.
embodiment 2
High-activity microorganism fertilizer described in the present embodiment, comprises the raw material of following weight part:
Water ratio is 85% biological sludge, 60 parts;
Stalk carbon dust, 35 parts;
Back-mixing material, 30 parts;
Wood vinegar, 1 part;
Bacillus thuringiensis and Nocardia bacteria, 1 part;
The ratio of described bacillus thuringiensis and nocardial inoculum size is 8:1;
The preparation method of the high-activity microorganism fertilizer described in the present embodiment, comprising:
1) organic waste residues is mixed with straw powder, then add push after wood vinegar and bacillus thuringiensis, Nocardia bacteria mixing;
2) sending into fermenter through the mixing compound obtaining of step 1) extruding, in described fermenter, add back-mixing material, described compound and back-mixing material are stirred, in fermenter, the piling height of compound and back-mixing material is 2.5m, controlled fermentation temperature is carried out aerobic fermentation lower than 60 DEG C, when leavening temperature is during higher than 60 DEG C, carry out turning operation once, until completing fermentation while no longer increasing, temperature obtains finished product;
3) in fermenter, clear up grog, send into stockyard.
embodiment 3
High-activity microorganism fertilizer described in the present embodiment, comprises the raw material of following weight part:
Water content is 78% fowl and animal excrement, 55 parts;
Straw powder, 10 parts;
Stalk carbon dust, 5 parts;
Back-mixing material, 20 parts;
Wood vinegar, 0.1 part;
Bacillus thuringiensis and Nocardia bacteria, 0.1 part;
The ratio of described bacillus thuringiensis and nocardial inoculum size is 8:1;
The preparation method of the high-activity microorganism fertilizer described in the present embodiment, comprising:
1) organic waste residues is mixed with straw powder, then add push after wood vinegar and bacillus thuringiensis, Nocardia bacteria mixing;
2) sending into fermenter through the mixing compound obtaining of step 1) extruding, in described fermenter, add back-mixing material, described compound and back-mixing material are stirred, in fermenter, the piling height of compound and back-mixing material is 2.5m, controlled fermentation temperature is carried out aerobic fermentation lower than 60 DEG C, when leavening temperature is during higher than 60 DEG C, carry out turning operation once, until completing fermentation while no longer increasing, temperature obtains finished product;
3) in fermenter, clear up grog, send into stockyard.
embodiment 4
A kind of high-activity microorganism fertilizer, comprises the raw material of following weight part:
Water ratio is 80% food service industry organic waste residues, 55 parts;
Straw powder, 20 parts;
Stalk carbon dust, 15 parts;
Back-mixing material, 20 parts;
Wood vinegar, 0.15 part;
Bacillus thuringiensis and Nocardia bacteria, 0.2 part;
The ratio of described bacillus thuringiensis and nocardial inoculum size is 8:1;
The preparation method of the high-activity microorganism fertilizer described in the present embodiment, comprising:
1) organic waste residues is mixed with straw powder and stalk carbon dust, then add push after wood vinegar and bacillus thuringiensis, Nocardia bacteria mixing;
2) sending into fermenter through the mixing compound obtaining of step 1) extruding, the back-mixing material that is 10cm at the surface coverage thickness of described compound, in fermenter, the piling height of compound and back-mixing material is 2m, controlled fermentation temperature is carried out aerobic fermentation lower than 60 DEG C, when leavening temperature is during higher than 60 DEG C, carry out turning operation once, until temperature completes fermentation while no longer increasing;
3) in fermenter, clear up grog, send into stockyard.
embodiment 5
High-activity microorganism fertilizer described in the present embodiment, comprises the raw material of following weight part:
Water ratio is 80% fowl and animal excrement, 60 parts;
Straw powder, 20 parts;
Stalk carbon dust, 15 parts;
Wood vinegar, 0.15 part;
Back-mixing material, 20 parts;
Bacillus thuringiensis, Nocardia bacteria, subtilis, Bacillus licheniformis, white-rot fungi and Phanerochaete chrysosporium, 0.2 part;
The ratio of described bacillus thuringiensis and nocardial inoculum size is 6:1, and described bacillus thuringiensis and nocardial inoculum size account for 80% of total bacterial classification inoculum size;
The preparation method of the high-activity microorganism fertilizer described in the present embodiment, comprising:
1) organic waste residues is mixed with straw powder and stalk carbon dust, then add push after wood vinegar and described microbiobacterial agent mixing;
2) sending into fermenter through the mixing compound obtaining of step 1) extruding, the back-mixing material that is 10cm at the surface coverage thickness of described compound, in fermenter, the piling height of compound and back-mixing material is 1.8m, controlled fermentation temperature is carried out aerobic fermentation lower than 60 DEG C, when leavening temperature is during higher than 60 DEG C, carry out turning operation once, until temperature completes fermentation while no longer increasing; The present embodiment also detects the dark 1m of the mixing stockpile place oxygen content in fermenter, when oxygen content is lower than 1% time, described compound is carried out to aeration, until oxygen concn is increased to 10%;
3) in fermenter, clear up grog, send into stockyard.
embodiment 6
High-activity microorganism fertilizer described in the present embodiment, comprises the raw material of following weight part:
Water ratio is 70% fowl and animal excrement, 60 parts;
Straw powder, 20 parts;
Stalk carbon dust, 15 parts;
Wood vinegar, 0.15 part;
Back-mixing material, 30 parts;
Bacillus thuringiensis, Nocardia bacteria, subtilis, Bacillus licheniformis, white-rot fungi and Phanerochaete chrysosporium, 0.1 part;
The ratio of described bacillus thuringiensis and nocardial inoculum size is 6:1, and described bacillus thuringiensis and nocardial inoculum size account for 80% of total bacterial classification inoculum size;
The preparation method of the high-activity microorganism fertilizer described in the present embodiment, comprising:
1) organic waste residues is mixed with straw powder and stalk carbon dust, then add push after wood vinegar and microbiobacterial agent mixing;
2) sending into fermenter through the mixing compound obtaining of step 1) extruding, the back-mixing material that is 50cm at the surface coverage thickness of described compound, in fermenter, the piling height of compound and back-mixing material is 1.8m, controlled fermentation temperature is carried out aerobic fermentation lower than 60 DEG C, when leavening temperature is during higher than 60 DEG C, carry out turning operation once, until temperature completes fermentation while no longer increasing; The present embodiment also detects the dark 1m of the mixing stockpile place oxygen content in fermenter, when oxygen content is lower than 1% time, described compound is carried out to aeration, until oxygen concn is increased to 10%;
3) in fermenter, clear up grog, send into stockyard.
Microbiobacterial agent bacillus thuringiensis, Nocardia bacteria, subtilis, Bacillus licheniformis, white-rot fungi and Phanerochaete chrysosporium in the present invention are the microbial inoculum from row filter, domestication, cultivation, and in nutrient solution, the colony number of microorganism is 10
6-10
7cfumL
-1, above-mentioned bacterial classification is known bacterial classification, and its training method is known technology.As selectable embodiment, microbiobacterial agent described in the present invention can be also arbitrarily commercially available liquid or the microbial inoculum of powdery, it is 0.1-1.0 weight part that the present invention limits microbiobacterial agent, and object is to regulate the raw material of described microbial organic fertilizer in suitable ratio.
experimental example
In order to confirm technique effect of the present invention, the present invention is provided with experimental example, and in the indices to the high-activity microorganism fertilizer described in the present invention and preparation process, required fermentation time is measured, and result is as follows:
Obviously, above-described embodiment is only for example is clearly described, and the not restriction to embodiment.For those of ordinary skill in the field, can also make other changes in different forms on the basis of the above description.Here exhaustive without also giving all embodiments, and the apparent variation of being extended out thus or variation are still among the protection domain in the invention.
Claims (9)
1. consolidate a carbon high-activity microorganism fertilizer, comprise the raw material of following weight part:
Organic waste residues, 50-60 part;
Biomass auxiliary material, 15-35 part, described biomass auxiliary material is straw powder and stalk carbon dust, and wherein said straw powder is 10-20 weight part, and described stalk carbon dust is 5-15 weight part;
Back-mixing material, 20-30 part;
Wood vinegar, 0.1-1.0 part;
Microbiobacterial agent, 0.1-1.0 part;
It is characterized in that, described microbiobacterial agent comprises bacillus thuringiensis and Nocardia bacteria, and the ratio of described bacillus thuringiensis and nocardial inoculum size is 3:1-8:1;
The preparation method of described solid carbon high-activity microorganism fertilizer, comprising:
(1) organic waste residues is mixed with biomass auxiliary material, then add push after wood vinegar and microbiobacterial agent mixing;
(2) send pushing the mixing compound obtaining through step (1) into fermenter, in described fermenter, add back-mixing material, controlled fermentation temperature is carried out aerobic fermentation lower than 60 DEG C, until temperature completes fermentation while no longer increasing, completes the grog that fermentation obtains and is finished product.
2. solid carbon high-activity microorganism fertilizer according to claim 1, is characterized in that, described organic waste residues is one or more in fowl and animal excrement, food service industry waste residue, biological sludge, and the water ratio of described organic waste residues is lower than 80%.
3. solid carbon high-activity microorganism fertilizer according to claim 1 and 2, is characterized in that, described wood vinegar is 0.1 ~ 0.2 weight part, and described microbiobacterial agent is 0.1-0.2 weight part.
4. want the solid carbon high-activity microorganism fertilizer described in 1 or 2 according to right, it is characterized in that, the ratio of described bacillus thuringiensis and nocardial inoculum size is 6:1.
5. want the solid carbon high-activity microorganism fertilizer described in 3 according to right, it is characterized in that, the ratio of described bacillus thuringiensis and nocardial inoculum size is 6:1.
6. want the solid carbon high-activity microorganism fertilizer described in 1 or 2 or 5 according to right, it is characterized in that, described microbiobacterial agent also comprises subtilis, Bacillus licheniformis, white-rot fungi and Phanerochaete chrysosporium;
In described microbiobacterial agent, bacillus thuringiensis and nocardial inoculum size account for 80% of total bacterial classification inoculum size.
7. solid carbon high-activity microorganism fertilizer according to claim 1, is characterized in that, in the fermenter in step (2), the piling height of compound and back-mixing material is no more than 2m.
8. according to the solid carbon high-activity microorganism fertilizer described in claim 1 or 7, it is characterized in that, step is put into compound after fermenter in (2), the back-mixing material that is 10-50cm at the surface coverage thickness of described compound.
9. solid carbon high-activity microorganism fertilizer according to claim 8, it is characterized in that, in the aerobic fermentation process of described step (2), when the dark 1m of the mixing stockpile place oxygen content in fermenter is lower than 1% time, described compound is carried out to aeration, until oxygen concn is increased to 10%.
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| CN107056542A (en) * | 2017-04-12 | 2017-08-18 | 中南林业科技大学 | The Chemical Mixed Fertilizer of camellia oleifera lam tea seed yield and carbon sink is improved simultaneously |
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Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1376651A (en) * | 2002-04-26 | 2002-10-30 | 袁登辉 | Process for preparing fermented organic amino acid fertilizer |
| CN102101796A (en) * | 2010-10-20 | 2011-06-22 | 姜虎 | High-quality composting pretreatment method and device for urban kitchen waste |
| CN102180744A (en) * | 2011-01-07 | 2011-09-14 | 唐山汇力科技有限公司 | Preparation method of soil conditioner |
-
2012
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Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1376651A (en) * | 2002-04-26 | 2002-10-30 | 袁登辉 | Process for preparing fermented organic amino acid fertilizer |
| CN102101796A (en) * | 2010-10-20 | 2011-06-22 | 姜虎 | High-quality composting pretreatment method and device for urban kitchen waste |
| CN102180744A (en) * | 2011-01-07 | 2011-09-14 | 唐山汇力科技有限公司 | Preparation method of soil conditioner |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107056542A (en) * | 2017-04-12 | 2017-08-18 | 中南林业科技大学 | The Chemical Mixed Fertilizer of camellia oleifera lam tea seed yield and carbon sink is improved simultaneously |
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