CN104230416B - A kind of method manufacturing SOLID ORGANIC carbon fertilizer - Google Patents
A kind of method manufacturing SOLID ORGANIC carbon fertilizer Download PDFInfo
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- CN104230416B CN104230416B CN201410414422.3A CN201410414422A CN104230416B CN 104230416 B CN104230416 B CN 104230416B CN 201410414422 A CN201410414422 A CN 201410414422A CN 104230416 B CN104230416 B CN 104230416B
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- 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
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Abstract
A kind of method manufacturing SOLID ORGANIC carbon fertilizer of the present invention, it relates to manufacture the method for fertilizer with fermentation technique. it comprises: the biological organic waste water concentrated solution adding its weight 15% in the major ingredient of the water content 45-55% of biological particle preparation, and it is mixed into the zymophyte pulvis of this material gross weight 0.5%, fully after mixing, directly heap builds up the material fermentation heap of high 1.0-1.2 rice, not turning in 6-8 days, after its cooling, it is spread out and the biological organic waste water concentrated solution of the major ingredient weight 18-25% that splashes, and add zymophyte pulvis again by the consumption of last time, mix, again heap builds material fermentation heap, not turning in 6-8 days, after its cooling, transfer heap builds the stewing dry heap of high 2.5-3.0 rice, not turning in 20-30 days, treat that the water content of fermentation materials in its slow cooling and heap is down to 30%, namely reactor startup is carried out, fermentation material is broken and packs. thing humic acids bacteria powder made a living by zymophyte pulvis or stalk becomes thoroughly decomposed pulvis.
Description
Technical field
The present invention relates to a kind of method utilizing fermentation technique to manufacture fertilizer.
Background technology
Carbon is first of the necessary macroelement of plant and the metabolic energy. " chemistry Plant Nutrition " that before more than 170 years, western scholar is founded is as according to the classical Plant Nutrition set up and soil fertilizer science, only admitting that the carbon needed for plant derives from CO2Gas is absorbed and chlorophyll photosynthetic conversion carbon " passage " by blade. Thus cause the mistake to organic fertilizer location: do not give the function that organic fertilizer provides organic matter nutrient to farm crop, thus organic fertilizer is manufactured " the mineralising soil ulmin " that can only improve soil. These embody a concentrated expression of in the existing organic commercial fertilizer material technological standard of China, it does not have the index of the organic carbon that statement can be absorbed by root system of plant.
What condition should plant organic matter nutrient possess? first is take carbon as main component; 2nd be can water molten; 3rd is that molecular particle size should be enough little, directly can be absorbed by root system of plant. This kind of plant organic matter nutrient is exactly the molten organic carbon of micromolecular water, is called for short effective carbon. Test is widely applied to prove: the factor of the mineral substance nutrient contained by eliminating, the active substance that farm crop directly rise in organic fertilizer growth promoting effect is exactly mainly effective carbon. Effective carbon is also suitable for directly being absorbed by soil microorganisms, accelerates it and breeds in a large number, and this is the important factor that improvement soil promotes root system. Organic fertility of organic fertilizer carbon rate effective with it is proportionate relation. Therefore correct fertilizer theory and fertilizer functional localization, should to produce and to preserve effective carbon as important goal. If the organic fertilizer of the effective carbon rate of superelevation can be obtained, just obtain efficient organic fertilizer!
Traditional compost method utilizing fermentation technique to manufacture fertilizer alternately is stacked by layer biological material and the earth of agricultural crop straw, leaf and the processing of farm products waste composition such as rice husk, pomace, vinasse, mushroom bacteria rod slag, tea grounds, grouts, adds the thin soil of lid layer after the diluent of aerobic high-heat zymophyte that the biological material of every layer thickness 15-20 centimetre is evenly splashed;Wherein the usage quantity of aerobic high-heat fermenting agent is about the 0.2% of biological material weight; Heap is high or to be wrapped up with plastics film to about 1.2 meters at the outer batter layer of muds soil piled. In order to ensure the abundant microbe conversion of biological material, it is necessary to repeated multiple times turning (is spread out and re-establish fermentation heap). Finally use the hyperthermia drying of cylinder more than 80 DEG C, make the commercially produced product being convenient to transport. Only pay close attention to the mistake of the location of nitrogen, phosphorus, potassium content due to tradition fertilizer, the production technique of this kind of organic fertilizer is not considered manufacture and preserve effective carbon, and biological organism material is through aerobic high-heat fermentation and repeatedly turning, and wherein a large amount of biological organic matters is decomposed into H2O and CO2Gas is drained, and again through cylinder hyperthermia drying, not only drain CO more2, the molten organic carbon of remaining micromolecular water is also condensed into macromole because of the high temperature of more than 80 DEG C, and the organic fertilizer produced has become a pile to lack the ghost of marrow, is " when addle, child has also been sprinkled away! "
Summary of the invention
Manufacture the method for SOLID ORGANIC carbon fertilizer it is desirable to provide a kind of, it is fertile that the method can manufacture the SOLID ORGANIC carbon being rich in the molten organic carbon of micromolecular water (effective carbon).
The technical scheme of the present invention is: a kind of method manufacturing SOLID ORGANIC carbon fertilizer, and the step comprised has:
Step 1, first time builds heap fermentation; The major ingredient of the water content 45-55% of biological particle preparation adds the biological organic waste water concentrated solution of this major ingredient weight 15%, and in above-mentioned material, is mixed into the zymophyte pulvis of this material gross weight 0.5%; Fully after mixing, directly heap builds the material fermentation heap of high 1.0-1.2 rice; Described biological organic waste water concentrated solution refers to the mixed solution of any one in alcohol slops within the scope of 4-6 of water content 45-55% and pH value, monosodium glutamate waste liquid, yeast waste liquor and black liquid or at least two kinds; Described zymophyte pulvis refers to that biological humic bacteria powder or stalk become thoroughly decomposed pulvis; Material fermentation heap builds not turning in 6-8 days after heap, qualified for fermenting more than 60 DEG C taking at least continuous 72 hours of the material temperature in piling;
Step 2, second time builds heap fermentation; After above-mentioned material fermentation heap starts cooling, it is spread out, splash the above-mentioned biological organic waste water concentrated solution of above-mentioned major ingredient weight 18-25%, add above-mentioned zymophyte pulvis again by the consumption of last time simultaneously, mix, again heap builds material fermentation heap pile high 1.0-1.2 rice, and this material fermentation heap builds not turning in 6-8 days after heap, qualified as fermenting more than 60 DEG C taking at least continuous 72 hours of the material temperature in piling;
Step 3, builds stewing dry heap stewing dry; After step 2 material fermentation heap starts cooling, the stewing dry heap that Gao Dui district heap builds high 2.5-3.0 rice transferred to by the fermentation material this material fermentation piled, not turning in 20-30 days, slow cooling after its intensification;
Step 4, arranges; The water content of the interior fermentation material of stewing dry heap is down to 30%, namely carries out reactor startup, fermentation material fragmentation and packaging.
Present method utilizes content to exceed biological humic (BFA) bacteria powder of traditional technology 1.5 times or the stalk pulvis that becomes thoroughly decomposed does biological particle organic fertilizer fermentation agent, directly pile the material fermentation heap building high 1.0-1.2 rice for twice, make in two organic fertilizer fermentation cycles being as short as 6-8 days need not turning, its CO2The aerobic high-heat that quantity discharged is only traditional ferments 1/3rd of repeatedly turning technique, so effectively carbon reserve capacity improves greatly. Biological organic waste water concentrated solution (general requirement water ratio about 50%) is rich in the molten organic carbon of water.But this kind of molten organic carbon of water is because of the long-time high temperature of concentration process process, mainly exist with macromole form, as direct application can cause plant root anoxic and dead seedling. Facts have proved that being added to by this kind of concentrated solution in biological particle in right amount participates in fermentation, the organic macromolecule of carbon in biological particle and concentrated solution can be resolved into small molecules and effective carbon by biological humic bacteria powder or the stalk microorganism in pulvis of becoming thoroughly decomposed. This just makes effective carbon content in the organic fertilizer after fermentation higher. The present invention adopts " high heap is stewing dry " method to substitute traditional " cylinder hyperthermia drying " method. " high heap is stewing dry " utilizes the material that just fermentation has been finished to carry out high heap, and heap is up to more than 2.5 meters. Bringing from fermentation zone due to material and build Gao Dui, the short period of time can be heated up again and be reached 60 DEG C, but to pile pressure big due to height, and oxygen is not enough, presents cooling soon. In the slow cooling reaching more than 20 day time, due to the heat exchange that the thermograde of fermentation materials in stockpile and environment is formed, and the effect of air flow, the steam in stockpile can constantly outwards distribute, and makes fermentation materials water content naturally drop to about 30%. What this kind utilized bioenergy and natural wind subtracts water process, avoids the hyperthermia drying using more than 80 DEG C, makes effective carbon can not be condensed into macromole, and this is a kind of not only energy-conservation but also preserves the technology of effective carbon. Through above 4 steps 32-46 days altogether, just the obtained high-performance solid fertilizer containing effective carbon rate more than 6%, reached goal of the invention.
In described step 1 and step 2, if ambient air temperature tackles material fermentation heap covering and heat insulating things lower than 20 DEG C. Like this, in the season of cold, still can carry out building heap in open air and produce.
Described biological particle is that animal excrement add crushed aggregate of plant. The plant material of the agricultural crop straw of crushed aggregate of plant and broken littleization, leaf and the processing of farm products waste such as rice husk, pomace, vinasse, mushroom bacteria rod slag, tea grounds, grouts and so on, main as the confession of organic carbon with this kind of material, wide material sources, the effect of animal excrement is the nutrition that the zymophyte becoming thoroughly decomposed in pulvis for biological humic bacteria powder or stalk in fermentation heap provides breeding rapidly. Adopt these biological particles both can the high quality carbon of production agricultural demand fertile, it is also possible to eliminate biological waste to the pollution of environment.
Described biological particle also has the peat composed of rotten mosses.
The peat composed of rotten mosses is rich in organic carbon, adds the peat composed of rotten mosses in fermentation heap, its effect except as organic carbon for while main, it is also possible to eliminate the foul smell that animal excrement produce, eliminate in production process and the finished product to the pollution of environment smell.
The present invention manufactures the method for SOLID ORGANIC carbon fertilizer, adopting heavy dose of biological humic (BFA) bacteria powder or the stalk pulvis that becomes thoroughly decomposed biological particle to divide the biological organic waste water concentrated solution of twice interpolation participate in directly building heap exempt from turning fermentation and the stewing measure such as dry of high heap, the obtained SOLID ORGANIC carbon being rich in the molten organic carbon of micromolecular water (effective carbon) is fertile. Applying biological humic acids (BFA) bacteria powder or stalk become thoroughly decomposed pulvis and add biological organic waste water concentrated solution and carry out solid biologic particle building heap fermentation for twice, exempt from turning, reduce CO to greatest extent in each fermentation period2Quantity discharged, preserve the effective carbon in fertilizer more. Also innovate the green technology that a biological organic waste water is recycled. By building the stewing dry fermentation materials of high heap, do not rely on cylinder hyperthermia drying, while avoiding making small molecules organic carbon be condensed into macromole because of high temperature, energy consumption can be saved.The high-performance solid fertilizer containing effective carbon rate more than 6% is obtained through 32-46 days. Through widely applying test to prove: organic fertility (the mineral substance nutrient factor contained by eliminating) the carbon rate effective with it of organic fertilizer is proportionate relation. Effective carbon rate of general merchandise fertilizer on average about 1.2%, the effective carbon rate of organic fertilizer produced according to the present invention is more than 5 times of general merchandise fertilizer, visible this is a kind of efficient organic fertilizer, its land area of one unit consumption is only the 20-25% of general merchandise fertilizer, this just creates qualitative change compared with tradition organic fertilizer, thus " ultra-high efficiency fertilizer " organic carbon creating a kind of organic fertility and quick-acting ultra-traditional organic commercial fertilizer all far away is fertile. The present invention is simple is applicable to again suitability for industrialized production, is easy to promote, it is achieved that the great innovation of organic fertilizer industry and change. The biological organic waste water introducing fertilizer production that the present invention is also difficult to again harmless treatment for a large amount of serious environment pollution has opened up wide prospect. During organic fertilizer constructed in accordance, often utilize the biological organic waste of 1 ton of solid biologic, so that it may digest more than 300 kilogram of concentrated biological organic waste water, be equivalent to digest the biological organic waste water 1.5 tons containing solid substance 10%. National 1,800,000,000 mu of common fertilizers 1,800,000,000 tons of can dissolving every year of ploughing, fertilizer of the present invention about 400,000,000 tons of also can dissolving, equals the biological organic waste water 7.2 hundred million tons indirectly dissolved containing solid substance 10%. This is that huge storage carbon is in the environmental practice of soil.
Embodiment
One, embodiment one
In outdoor taking pig excrement, edible mushrooms waste mushroom stick (50 order sieves can be crossed through being crushed to) and peat composed of rotten mosses powder mixture 10 tons (water ratio about 55%) as major ingredient, with 1.5 tons of alcohol waste water concentrated solutions (water ratio 55% and pH value are 4.2) and 57.5kg biological humic (BFA) bacteria powder, wheeled mixer is used fully to mix even, then with forklift transfer to fermentation zone directly pile build material fermentation heap, piling high 1.0 meters, prevailing circumstances temperature is 23 DEG C. Material temperature in observing this material fermentation and piling increase gradually (change normal) and continuous more than 72 hours material temperatures more than 60 DEG C after, judge the fermentation of this batch materials normally. Not turning in 8 days, after 8 days, there is cooling in the fermentation materials in this material fermentation heap, with forklift, this fermentation materials heap is spread out, see its humidity partially wet (water ratio about 50%), the alcohol waste water concentrated solution splashing identical again 1.8 tons, and add BFA bacteria powder 57.5kg, it may also be useful to wheeled mixer fully mixes even, again directly pile the material fermentation heap building high 1.0 meters of heap with forklift, prevailing circumstances temperature is 22 DEG C. This material fermentation heap is surveyed temperature, the material temperature observed in heap increase gradually with continuous more than 72 hours material temperatures more than 60 DEG C after, normal by aforementioned judgements fermentation, in build pile latter 7 days in not turning. Occurring cooling after 7 days in this fermented product stockpile, with forklift by the fermentation materials Chan Daogaodui district of this heap, directly heap builds the stewing dry heap of high 2.5 meters of heap, carries out stewing dry, and the fermentation materials short period of time rises above 60 DEG C again, then presents cooling soon. The fermentation materials got for 25th day in stewing dry heap judges that water ratio is close to 30%, namely with forklift, the fermentation materials of this heap is transferred to transfer district to spread out (reactor startup), material temperature is made to drop to room temperature, with another chaptrel formula mixer by again broken for the fermentation materials after cooling, enter conveying and packaging operation, 8.8 tons, the SOLID ORGANIC fertilizer of obtained high effectively carbon rate.
According to about the standard NY/T1976-2010 measuring water-soluble fertilizer organic content 6.21 articles of the 6.2nd of the Ministry of Agriculture, the suspension of obtained this fertilizer sample of 100mL.Filter out solution in clean beaker with quantitative paper at a slow speed, then operate by the method for this standard 6.3,6.4,6.5, record. Finally going out organic content by the 7th article of formulae discovery is w3 (%), but should according to the exchange coefficient of carbon content and organic content, and by gained organic content divided by 1.724, obtaining effective carbon rate is w2 (%). Recording the effective carbon rate of the present embodiment fertilizer sample is 6.3%.
Two, embodiment two
In outdoor taking cow dung, maize straw (through being crushed to long less than 3 centimetres) and peat composed of rotten mosses powder mixture 10 tons (water ratio about 50%) as major ingredient, with 1.5 tons of alcohol waste water concentrated solutions (water ratio 50% and pH value are 4.3) and 57.5kgBFA bacteria powder, wheeled mixer is used fully to mix even, then with forklift transfer to fermentation zone directly pile build material fermentation heap, pile high 1.05 meters, ambient air temperature is 26 DEG C, it is not necessary to adopt the measure of extra insulation. This material fermentation heap is carried out material temperature monitoring. Observe material temperature increase gradually with continuous more than 72 hours material temperatures more than 60 DEG C after, judge that the fermentation of this batch materials is normal. Not turning in 6 days, after 6 days, cooling occurs in this fermented product stockpile, with forklift, this fermentation materials heap is spread out, see its humidity partially dry (water ratio about 47%), then the alcohol waste water concentrated solution 2.03 tons splashing identical, and add BFA bacteria powder 57.5kg, using wheeled mixer fully to mix even, again directly pile the material fermentation heap building high 1.05 meters of heap with forklift, ambient air temperature is 26 DEG C. This material fermentation heap is surveyed temperature, observe heap in material temperature increase gradually with continuous more than 72 hours material temperatures more than 60 DEG C after, normal by aforementioned judgement fermentation, in building heap not turning in latter 6 days, when cooling occurred in fermented product stockpile after 6 days, the fermentation materials Chan Daogaodui district this material fermentation piled with forklift, the stewing dry heap building high 3 meters of heap is directly piled with forklift, carrying out stewing dry, in stewing dry heap, the fermentation materials short period of time rises above 60 DEG C again, presents cooling soon later. Within 20th day, get fermentation materials in stewing dry heap and judge that water ratio is close to 30%, namely with forklift, the fermentation materials in stewing dry heap is transferred to transfer district to spread out, material temperature is made to drop to room temperature, with another chaptrel formula mixer by again broken for the fermentation materials after cooling, enter conveying and packaging operation, 9.7 tons, the SOLID ORGANIC fertilizer of obtained high effectively carbon rate.
Recording the effective carbon rate of the present embodiment fertilizer sample according to the detection method of embodiment one is 6.5%.
Three, embodiment three
In outdoor taking chicken excrement, rice husk and peat composed of rotten mosses powder mixture 10 tons (water ratio about 46%) as major ingredient, with 1.5 tons of alcohol waste water concentrated solutions (water ratio 45% and pH value are 4.0) and 57.5kgBFA bacteria powder, wheeled mixer is used fully to mix even, then with forklift transfer to fermentation zone directly pile build material fermentation heap, pile high 1.1 meters, ambient air temperature is 15 DEG C, and material fermentation heap is upper covers woven straw insulation. This material fermentation heap is carried out material temperature monitoring. Observe material temperature increase gradually with continuous more than 72 hours material temperatures more than 60 DEG C after, judge that the fermentation of this batch materials is normal. Not turning in 7 days, cooling occurred in this fermented product stockpile after 7 days, with forklift, this fermentation materials heap is spread out, see its humidity partially dry (water ratio about 46%), then the alcohol waste water concentrated solution 2.3 tons splashing identical, and add BFA bacteria powder 57.5kg, wheeled mixer is used fully to mix even, again directly pile the material fermentation heap building high 1.1 meters of heap with forklift, ambient air temperature is 16 DEG C, and this material fermentation heap is upper covers woven straw insulation.This material fermentation heap is surveyed temperature, the material temperature observed in heap increase gradually with continuous more than 72 hours material temperatures more than 60 DEG C after, by aforementioned judgements fermentation normally, keep this material fermentation to pile not turning. When this material fermentation heap builds its fermentation materials appearance cooling in the 8th day after heap, the fermentation materials Chan Daogaodui district this material fermentation piled with forklift, directly heap builds the stewing dry heap of high 3 meters of heap, carry out stewing dry, in this stewing dry heap, the fermentation materials short period of time rises above 60 DEG C again, presents cooling soon later. Within 30th day, get fermentation materials in this stewing dry heap and judge that water ratio is close to 30%, namely with forklift, fermentation materials in this stewing dry heap is transferred to transfer district to spread out, material temperature is made to drop to room temperature, with another chaptrel formula mixer by again broken for the fermentation materials after cooling, enter conveying and packaging operation, 10.4 tons, the organic fertilizer of obtained high effectively carbon rate.
Recording the effective carbon rate of the present embodiment fertilizer sample solid according to the detection method of embodiment one is 6.4%.
Four, embodiment four
In outdoor taking sheep excrement, wood sawdust and peat composed of rotten mosses powder mixture 10 tons (water ratio about 45%) as major ingredient, become thoroughly decomposed pulvis with 1.5 tons of monosodium glutamate waste liquid concentrated solutions (water ratio 53% and pH value are 4.6) and 57.5kg stalk, wheeled mixer is used fully to mix even, then with forklift transfer to fermentation zone directly pile build material fermentation heap, pile high 1.2 meters, ambient air temperature is 30 DEG C, it is not necessary to adopt the measure of extra insulation. This material fermentation heap is carried out material temperature monitoring. Observe material temperature increase gradually with continuous more than 72 hours material temperatures more than 60 DEG C after, judge that the fermentation of this batch materials is normal. Not turning in 6 days, afterwards, there is cooling in fermentation materials, with forklift, this fermentation materials heap is spread out, see its humidity partially dry (water ratio about 45%), then the monosodium glutamate waste liquid concentrated solution 2.4 tons splashing identical, and add stalk and become thoroughly decomposed pulvis 57.5kg, using wheeled mixer fully to mix even, again directly pile the material fermentation heap building high 1.2 meters of heap with forklift, ambient air temperature is 29 DEG C. This material fermentation heap is surveyed temperature, observe heap in material temperature increase gradually with continuous more than 72 hours material temperatures more than 60 DEG C after, normal by aforementioned judgement fermentation, not turning in 6 days, builds the fermentation materials appearance cooling piling latter 6th day wherein, the fermentation materials Chan Daogaodui district this material fermentation piled with forklift in this material fermentation heap, directly heap builds the stewing dry heap of high 2.8 meters of heap, carrying out stewing dry, in this stewing dry heap, the fermentation materials short period of time rises above 60 DEG C again, presents cooling soon later. Within 22nd day, get fermentation materials in this stewing dry heap and judge that water ratio is close to 30%, namely with forklift, the fermentation materials that this material fermentation is piled is transferred to transfer district to spread out, material temperature is made to drop to room temperature, with another chaptrel formula mixer by again broken for the fermentation materials after cooling, enter conveying and packaging operation, 10.5 tons, the organic fertilizer of obtained high effectively carbon rate.
Recording the effective carbon rate of the present embodiment fertilizer sample according to the detection method of embodiment one is 6.7%.
Five, embodiment five
In outdoor taking sheep excrement, wheat stalk (through being crushed to long less than 3 centimetres) and peat composed of rotten mosses powder mixture 10 tons (water ratio about 46%) as major ingredient, become thoroughly decomposed pulvis with 1.5 tons of yeast waste liquor concentrated solutions (water ratio 49% and pH value are 4.8) and 57.5kg stalk, wheeled mixer is used fully to mix even, then with forklift transfer to fermentation zone directly pile build material fermentation heap, pile high 1.15 meters, ambient air temperature is 21 DEG C, it is not necessary to adopt the measure of extra insulation.This material fermentation heap is carried out material temperature monitoring. Observe material temperature increase gradually with continuous more than 72 hours material temperatures more than 60 DEG C after, judge that the fermentation of this batch materials is normal. Not turning in 7 days, afterwards, cooling occurs in this fermented product stockpile, with forklift, this fermentation materials heap is spread out, see its humidity partially dry (water ratio about 45%), then the yeast waste liquor concentrated solution 2.5 tons splashing identical, and add stalk and become thoroughly decomposed pulvis 57.5kg, using wheeled mixer fully to mix even, again directly pile the material fermentation heap building high 1.15 meters of heap with forklift, ambient air temperature is 21 DEG C. This material fermentation heap is surveyed temperature, observe heap in material temperature increase gradually with continuous more than 72 hours material temperatures more than 60 DEG C after, normal by aforementioned judgement fermentation, not turning in 8 days, builds the fermentation materials appearance cooling piling latter 8th day wherein, with forklift by fermentation materials Chan Daogaodui district in this heap in this material fermentation heap, directly heap builds the stewing dry heap of high 2.7 meters of heap, carrying out stewing dry, in stewing dry heap, the fermentation materials short period of time rises above 60 DEG C again, presents cooling soon later. Within 20th day, get fermentation materials in stewing dry heap and judge that water ratio is close to 30%, namely with forklift, fermentation materials in this stewing dry heap is transferred to transfer district to spread out, material temperature is made to drop to room temperature, with another chaptrel formula mixer by again broken for the fermentation materials after cooling, enter conveying and packaging operation, 10.6 tons, the organic fertilizer of obtained high effectively carbon rate.
Recording the effective carbon rate of the present embodiment fertilizer sample solid according to the detection method of embodiment one is 6.3%.
Six, embodiment six
In outdoor taking pig excrement, rice straw (through being crushed to long less than 3 centimetres) and peat composed of rotten mosses powder mixture 10 tons (water ratio about 49%) as major ingredient, with 1.5 tons of black liquid concentrated solutions (water ratio 50% and pH value are 6.0) and 57.5kgBFA bacteria powder, wheeled mixer is used fully to mix even, then with forklift transfer to fermentation zone directly pile build material fermentation heap, pile high 1.08 meters, ambient air temperature is 27 DEG C, it is not necessary to adopt the measure of extra insulation. This material fermentation heap is carried out material temperature monitoring. Observe material temperature increase gradually with continuous more than 72 hours material temperatures more than 60 DEG C after, judge that the fermentation of this batch materials is normal. Not turning in 6 days, afterwards, cooling occurs in this fermented product stockpile, with forklift, fermentation materials in this heap is spread out, see its humidity partially dry (water ratio about 48%), then the black liquid concentrated solution 2.1 tons splashing identical, and add BFA bacteria powder 57.5kg, using wheeled mixer fully to mix even, directly heap builds the material fermentation heap of high 1.08 meters of heap again, and ambient air temperature is 25 DEG C. This material fermentation heap is surveyed temperature, observe heap in material temperature increase gradually with continuous more than 72 hours material temperatures more than 60 DEG C after, normal by aforementioned judgement fermentation, not turning in 7 days, builds fermentation materials appearance cooling in the 7th day this heap after heap in this material fermentation heap, with forklift by fermentation materials Chan Daogaodui district in this heap, directly heap builds the stewing dry heap of high 2.6 meters of heap, carrying out stewing dry, in this stewing dry heap, the fermentation materials short period of time rises above 60 DEG C again, presents cooling soon later. Within 23rd day, get fermentation materials in this stewing dry heap and judge that water ratio is close to 30%, namely with forklift, fermentation materials in this stewing dry heap is transferred to transfer district to spread out, material temperature is made to drop to room temperature, with another chaptrel formula mixer by again broken for the fermentation materials after cooling, enter conveying and packaging operation, 10.0 tons, the SOLID ORGANIC fertilizer of obtained high effectively carbon rate.
Recording the effective carbon rate of the present embodiment fertilizer sample according to the detection method of embodiment one is 6.2%.
Seven, embodiment seven
In outdoor taking chicken excrement, corn cob (through being crushed to largest particle length below 1.5 centimetres) and peat composed of rotten mosses powder mixture 10 tons (water ratio about 49%) as major ingredient, the concentrated solution (water ratio 51% and pH value are 4.7) mixed with yeast waste liquor with 1.5 tons of monosodium glutamate waste liquids and 57.5kgBFA bacteria powder, wheeled mixer is used fully to mix even, then with forklift transfer to fermentation zone directly pile build material fermentation heap, pile high 1.06 meters, ambient air temperature is 31 DEG C, it is not necessary to adopt the measure of extra insulation. This material fermentation heap is carried out material temperature monitoring. Observe material temperature increase gradually with continuous more than 72 hours material temperatures more than 60 DEG C after, judge that the fermentation of this batch materials is normal. Not turning in 68 days, afterwards, in this heap, there is cooling in fermentation materials, with forklift, this fermentation materials heap is spread out, see its humidity partially dry (water ratio about 47%), then the concentrated solution 2.15 tons that identical monosodium glutamate waste liquid of splashing mixes with yeast waste liquor, and add BFA bacteria powder 57.5kg, using wheeled mixer fully to mix even, again directly pile the material fermentation heap building high 1.06 meters of heap with forklift, ambient air temperature is 32 DEG C. This material fermentation heap is surveyed temperature, observe heap in material temperature increase gradually with continuous more than 72 hours material temperatures more than 60 DEG C after, judge that fermentation is normal, not turning in 6 days, builds fermentation materials appearance cooling in the 6th day this heap after heap in this material fermentation heap, with forklift by fermentation materials Chan Daogaodui district in this heap, directly heap builds the stewing dry heap of high 2.9 meters of heap, carrying out stewing dry, in this stewing dry heap, the fermentation materials short period of time rises above 60 DEG C again, presents cooling soon later. Within 28th day, get fermentation materials in this stewing dry heap and judge that water ratio is close to 30%, namely with forklift, fermentation materials in this stewing dry heap is transferred to transfer district to spread out, material temperature is made to drop to room temperature, with another chaptrel formula mixer by again broken for the fermentation materials after cooling, enter conveying and packaging operation, 10.1 tons, the SOLID ORGANIC fertilizer of obtained high effectively carbon rate.
Recording the effective carbon rate of the present embodiment fertilizer sample according to the detection method of embodiment one is 6.6%.
Eight, embodiment eight
In outdoor taking cow dung, edible mushrooms waste mushroom stick (through being crushed to 50 order sieves) and peat composed of rotten mosses powder mixture 10 tons (water ratio about 53%) as major ingredient, the concentrated solution (water ratio 55% and pH value are 4.7) mixed with monosodium glutamate waste liquid with 1.5 tons of alcohol slopss and 57.5kg stalk become thoroughly decomposed pulvis, wheeled mixer is used fully to mix even, then with forklift transfer to fermentation zone directly pile build material fermentation heap, pile high 1.12 meters, ambient air temperature is 25 DEG C, it is not necessary to adopt the measure of extra insulation. Material fermentation heap is carried out material temperature monitoring. Observe material temperature increase gradually with continuous more than 72 hours material temperatures more than 60 DEG C after, judge that the fermentation of this batch materials is normal. Not turning in 8 days, afterwards, in this heap, there is cooling in fermentation materials, with forklift, this fermentation materials heap is spread out, see its humidity moderate (water ratio about 50%), then the concentrated solution 1.82 tons that identical alcohol slops of splashing mixes with monosodium glutamate waste liquid, and add stalk and become thoroughly decomposed pulvis 57.5kg, using wheeled mixer fully to mix even, again directly pile the material fermentation heap building high 1.12 meters of heap with forklift, ambient air temperature is 24 DEG C. This material fermentation heap is surveyed temperature, observe heap in material temperature increase gradually with continuous more than 72 hours material temperatures more than 60 DEG C after, judge that fermentation is normal, not turning in 6 days, builds fermentation materials appearance cooling in the 6th day this heap after heap in this material fermentation heap, with forklift by fermentation materials Chan Daogaodui district in this heap, directly heap builds the stewing dry heap of high 3 meters of heap, carrying out stewing dry, in this stewing dry heap, the fermentation materials short period of time rises above 60 DEG C again, presents cooling soon later.Within 20th day, get fermentation materials in this stewing dry heap and judge that water ratio is close to 30%, transfer to transfer district by fermentation materials in this stewing dry heap to spread out, material temperature is made to drop to room temperature, with another chaptrel formula mixer by again broken for the fermentation materials after cooling, enter conveying and packaging operation, 8.9 tons, the SOLID ORGANIC fertilizer of obtained high effectively carbon rate.
Recording the effective carbon rate of the present embodiment fertilizer sample according to the detection method of embodiment one is 6.8%.
Nine, embodiment nine
In outdoor taking chicken excrement, Kidney bean stalk (through being crushed to long less than 3 centimetres) and peat composed of rotten mosses powder mixture 10 tons (water ratio about 46%) as major ingredient, the concentrated solution (water ratio 51% and pH value are 5.2) mixed with yeast waste liquor with 1.5 tons of alcohol slopss, monosodium glutamate waste liquid and 57.5kgBFA bacteria powder, wheeled mixer is used fully to mix even, then with forklift transfer to fermentation zone directly pile build material fermentation heap, pile high 1.20 meters, ambient air temperature is 28 DEG C, it is not necessary to adopt the measure of extra insulation. This material fermentation heap is carried out material temperature monitoring. Observe material temperature increase gradually with continuous more than 72 hours material temperatures more than 60 DEG C after, judge that the fermentation of this batch materials is normal. Not turning in 6 days, afterwards, in this heap, there is cooling in fermentation materials, with forklift, this fermentation materials heap is spread out, see its humidity partially dry (water ratio about 49%), then the concentrated solution 2.00 tons that identical alcohol slops of splashing, monosodium glutamate waste liquid mix with yeast waste liquor, and add BFA bacteria powder 57.5kg, using wheeled mixer fully to mix even, again directly pile the material fermentation heap building high 1.20 meters of heap with forklift, ambient air temperature is 28 DEG C. This material fermentation heap is surveyed temperature, observe heap in material temperature increase gradually with continuous more than 72 hours material temperatures more than 60 DEG C after, judge that fermentation is normal, not turning in 6 days, builds fermentation materials appearance cooling in the 6th day this heap after heap in this material fermentation heap, with forklift by fermentation materials Chan Daogaodui district in this heap, directly heap builds the stewing dry heap of high 3 meters of heap, carrying out stewing dry, in this stewing dry heap, the fermentation materials short period of time rises above 60 DEG C again, presents cooling soon later. Within 20th day, get fermentation materials in this stewing dry heap and judge that water ratio is close to 30%, namely with forklift, fermentation materials in this stewing dry heap is transferred to transfer district to spread out, material temperature is made to drop to room temperature, with another chaptrel formula mixer by again broken for the fermentation materials after cooling, enter conveying and packaging operation, 10.2 tons, the SOLID ORGANIC fertilizer of obtained high effectively carbon rate.
Recording the effective carbon rate of the present embodiment fertilizer sample according to the detection method of embodiment one is 6.6%.
The above, it is only the better embodiment of the present invention, scope of the invention process is not limited with this, the equivalence change done according to the technical scheme of the present invention and description with modify, such as by alcohol slops, monosodium glutamate waste liquid, yeast waste liquor and black liquid other two or three or four kind have the biological organic waste water concentrated solution making water content 45-55% and pH value within the scope of 4-6; Use other known biomaterial being rich in organic carbon to substitute crushed aggregate of plant in above embodiment etc., all should belong to the scope that the present invention is contained.
Claims (3)
1. manufacturing a method for SOLID ORGANIC carbon fertilizer, the step comprised has:
Step 1, first time builds heap fermentation; The major ingredient of the water content 45-55% of biological particle preparation adds the biological organic waste water concentrated solution of this major ingredient weight 15%, and in above-mentioned material, is mixed into the zymophyte pulvis of this material gross weight 0.5%;Fully after mixing, directly heap builds the material fermentation heap of high 1.0-1.2 rice; Described biological particle is that animal excrement add crushed aggregate of plant; Described biological organic waste water concentrated solution refers to the mixed solution of any one in alcohol slops within the scope of 4-6 of water content 45-55% and pH value, monosodium glutamate waste liquid, yeast waste liquor and black liquid or at least two kinds; Described zymophyte pulvis refers to that biological humic bacteria powder or stalk become thoroughly decomposed pulvis; Material fermentation heap builds not turning in 6-8 days after heap, qualified for fermenting more than 60 DEG C taking at least continuous 72 hours of the material temperature in piling;
Step 2, second time builds heap fermentation; After above-mentioned material fermentation heap starts cooling, it is spread out, splash the above-mentioned biological organic waste water concentrated solution of above-mentioned major ingredient weight 18-25%, add above-mentioned zymophyte pulvis again by the consumption of last time simultaneously, mix, again heap builds material fermentation heap pile high 1.0-1.2 rice, and this material fermentation heap builds not turning in 6-8 days after heap, qualified as fermenting more than 60 DEG C taking at least continuous 72 hours of the material temperature in piling;
Step 3, builds stewing dry heap stewing dry; After step 2 material fermentation heap starts cooling, the stewing dry heap that Gao Dui district heap builds high 2.5-3.0 rice transferred to by the fermentation material this material fermentation piled, not turning in 20-30 days, slow cooling after its intensification;
Step 4, arranges; The water content of the interior fermentation material of stewing dry heap is down to 30%, namely carries out reactor startup, fermentation material fragmentation and packaging.
2. a kind of method manufacturing SOLID ORGANIC carbon fertilizer according to claim 1, it is characterised in that: in described step 1 and step 2, if ambient air temperature tackles material fermentation heap covering and heat insulating things lower than 20 DEG C.
3. a kind of method manufacturing SOLID ORGANIC carbon fertilizer according to claim 1, it is characterised in that: described biological particle also has the peat composed of rotten mosses.
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| CN104649764A (en) * | 2015-03-03 | 2015-05-27 | 黑龙江省庆东阳光农业生物科技股份有限公司 | Preparation and using methods of refined multifunctional organic fertilizer |
| CN105061109B (en) * | 2015-08-03 | 2018-03-16 | 郑州大学 | A kind of sub-micron organic carbon fertilizer and its production method |
| CN105884449A (en) * | 2015-11-04 | 2016-08-24 | 北京嘉博文生物科技有限公司 | Method for producing organic fertilizer by means of monosodium glutamate wastewater and straw fermentation |
| CN105503335A (en) * | 2015-12-17 | 2016-04-20 | 东莞市环境科学研究所 | Method and device for producing high organic carbon fertilizer through kitchen waste |
| CN107434751A (en) * | 2017-08-04 | 2017-12-05 | 山东森博生物科技有限公司 | A kind of method that biological organic carbon fertilizer is produced using black liquor of pulp making |
| CN109988042A (en) * | 2019-04-08 | 2019-07-09 | 齐鲁工业大学 | A method of organic fertilizer is manufactured using monosodium glutamate waste liquid |
| CN111072431A (en) * | 2019-12-12 | 2020-04-28 | 新疆农垦科学院 | Organic functional carrier loaded with water-soluble microbial agent, preparation method of organic functional carrier, functional biological organic liquid fertilizer and biological organic fertilizer |
| CN110922272A (en) * | 2019-12-23 | 2020-03-27 | 四川战友兴农科技有限公司 | Biological carbon fertilizer capable of replacing chemical fertilizer and preparation method and use method thereof |
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| CN101486597A (en) * | 2008-01-18 | 2009-07-22 | 天津市农业资源与环境研究所 | Microbial composite microorganism inoculant for producing biological organic fertilizer from decomposed organic wastes |
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