CN113321542A - Preparation process of chicken manure stacking fermentation bio-organic fertilizer - Google Patents
Preparation process of chicken manure stacking fermentation bio-organic fertilizer Download PDFInfo
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- CN113321542A CN113321542A CN202110649916.XA CN202110649916A CN113321542A CN 113321542 A CN113321542 A CN 113321542A CN 202110649916 A CN202110649916 A CN 202110649916A CN 113321542 A CN113321542 A CN 113321542A
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- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
- C05F17/20—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation using specific microorganisms or substances, e.g. enzymes, for activating or stimulating the treatment
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- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05B—PHOSPHATIC FERTILISERS
- C05B1/00—Superphosphates, i.e. fertilisers produced by reacting rock or bone phosphates with sulfuric or phosphoric acid in such amounts and concentrations as to yield solid products directly
- C05B1/02—Superphosphates
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- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
- C05F17/70—Controlling the treatment in response to process parameters
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- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
- C05F17/80—Separation, elimination or disposal of harmful substances during the treatment
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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
- 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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Abstract
The invention discloses a preparation process of a chicken manure stacking fermentation bio-organic fertilizer, which comprises the steps of shoveling chicken manure into a stirrer, adding mushroom residues, plant ash, bovine bone meal, organic bean residues and calcium superphosphate, crushing and mixing, then uniformly spraying a decomposition agent, stacking fertilizer piles on a cement stacking platform, sequentially fermenting and decomposing, promoting secondary fermentation and decomposition and tertiary fermentation and decomposition by using a percolate generated in the fermentation process, meanwhile, the temperature in the fermentation and decomposition process is effectively controlled to be kept between 50 and 70 ℃ by arranging the heat dissipation holes in the fermentation and decomposition process, so that ventilation and heat dissipation are facilitated, the compost can be decomposed uniformly, meanwhile, the harmless treatment of sterilization and disinsection is achieved, so that the quality of the biological organic fertilizer is improved on the basis of shortening the formation period of the chicken manure stacking fermentation organic fertilizer, the fermentation percolate is effectively recycled, and the method is environment-friendly.
Description
Technical Field
The invention particularly relates to a preparation process of a chicken manure stacking fermentation bio-organic fertilizer.
Background
With the application of the livestock and poultry manure organic fertilizer, the ecological environment balance of a farmland can be gradually destroyed, and potential harm is caused to the quality safety of agricultural products. Therefore, in order to make the livestock and poultry manure be efficiently and safely utilized, before the livestock and poultry manure is used in agriculture, the livestock and poultry manure is subjected to composting treatment, complex organic matters in the livestock and poultry manure are decomposed into humus by utilizing microbial fermentation, and high temperature of 50-65 ℃ is generated in the decomposition process, so that pathogenic microorganisms are killed, and part of antibiotic residues are eliminated.
At present, the production of the livestock and poultry manure organic fertilizer can meet the requirement through multiple fermentation and decomposition treatments, in the preparation process, after each fine stacking and turning, the fermentation and decomposition can be carried out only by adding a decomposition agent, and the leachate generated by fermentation and hydrolysis is wasted and is discharged at will to influence the environment.
Disclosure of Invention
In view of the above, the invention aims to provide the preparation process of the chicken manure stacking fermentation organic fertilizer, which is environment-friendly and can improve the quality of the biological organic fertilizer on the basis of shortening the period of forming the biological organic fertilizer by chicken manure stacking fermentation, and effectively and repeatedly utilize fermentation percolate.
In order to solve the technical problems, the technical scheme of the invention is as follows:
a preparation process of a chicken manure stacking fermentation bio-organic fertilizer comprises the following steps:
step 1: conveying raw material chicken manure blocks into an aerobic fermentation workshop by using a conveying belt, stirring and loosening by using a forklift, shoveling the loosened chicken manure into a stirrer by using the forklift, adding mushroom residues, plant ash, bovine bone meal, organic bean dregs and calcium superphosphate into the stirrer, crushing and mixing by using the stirrer, spraying a thoroughly-decomposed agent by using an automatic strain spraying machine in the stirring process, fully and uniformly stirring, and then screening stones and branches by using a screening machine to prepare a composting raw material for later use;
step 2, stacking and fermenting the compost raw materials prepared in the step 1 in an aerobic fermentation workshop by using a forklift, and specifically comprising the following steps:
a. pouring a cement stacking platform with the length of 16 meters and the width of 10 meters in an aerobic fermentation workshop, pouring a liquid drainage groove at the edge of the cement stacking platform, and pouring a liquid storage tank at the end of the liquid drainage groove for later use;
b. stacking the compost raw materials prepared in the step 1 on a cement stacking table in the specific step a to form a compost fermentation pile with the width of 8 meters, the height of 4.5 meters and the pile length of 15 meters, and then uniformly distributing ventilation and heat dissipation holes above the compost fermentation pile by utilizing an iron rod with the radius of 3cm in a mode of inserting from top to bottom, so that the temperature of the compost fermentation pile in the fermentation process is controlled to be 50-70 ℃ for later use;
c. b, performing first fermentation according to the compost fermentation pile finished in the specific step b, wherein the fermentation time is 8 days, and as the water content of compost raw materials is low, spraying purified water to the compost fermentation pile to ensure that the humidity of the compost fermentation pile reaches 40%, in the fermentation process, during the first fermentation day, the temperature of the compost fermentation pile is increased to 50 ℃, then slowly increased to 70 ℃, and kept for 7-8 days, at the moment, most parasitic ova and harmful bacteria in the compost fermentation pile are killed at high temperature to finish harmless treatment, and meanwhile, as hydrolysis is generated in the fermentation process, the compost fermentation pile generates percolate rich in thoroughly decomposed agents and is collected into a liquid storage tank through a liquid drainage groove for later use;
d. c, performing first fermentation treatment on the compost fermentation pile for 8 days by a specific step c, turning the compost fermentation pile by using a groove type pile turning machine, stacking on a cement stacking table again, tightly pressing the secondary compost fermentation pile by using a forklift into a secondary compost fermentation pile with the width of 8 meters, the height of 4.5 meters and the pile length of 15 meters, and meanwhile, arranging air-permeable heat dissipation holes by using an iron rod with the radius of 3cm above the secondary compost fermentation pile in a manner of inserting from top to bottom so that the temperature of the compost fermentation pile is still controlled to be 50-70 ℃ in the fermentation process, extracting and spraying percolate generated by first fermentation to the secondary compost fermentation pile through a pump body for 16 days, and collecting the percolate generated by secondary compost fermentation into a liquid storage tank through a liquid drainage groove for later use;
e. in the concrete step d, conveying the raw materials to a fermentation tank of an aerobic fermentation workshop by using a forklift to perform third fermentation, spraying the percolate in a liquid storage tank to the stacked compost in the fermentation tank again, controlling the fermentation temperature to be 50-70 ℃ at the same time, finely turning the compost by using an automatic pile turning machine during the fermentation period to evaporate the percolate, shoveling the compost fermentation pile to a cement stacking platform by using the forklift after the humidity of the compost fermentation pile is reduced to 20%, finely loosening the compost fermentation pile, stacking again to perform fourth pile turning fermentation for 25-27 days, drying the compost fermentation pile due to water evaporation, and beginning to reduce the fermentation temperature, wherein the color of the compost fermentation pile becomes deep brown black, namely the fermentation rotten process of the compost fermentation pile is completed for later use;
and step 3: in the step 2, the compost fermentation pile is conveyed to an automatic blanking machine in batches after four times of fermentation is finished, then conveyed to a crusher by a conveyer belt to be crushed twice, and conveyed to a mesh screen machine to be screened into primary powder after being crushed, and then is subjected to deodorization treatment by a dust removal deodorizer after being screened, and the powder fertilizer enters the next procedure after meeting the requirement, and returns to an aerobic fermentation workshop to mix chicken manure blocks to be stirred for rework treatment because the powder fertilizer does not meet the requirement due to uneven mixing of a decomposing agent;
step five: and (4) feeding the qualified powdery fertilizer in the step (4) into a stirrer, controlling stirring to turn at a speed of 55r/pm, spraying bacillus subtilis and bacillus licheniformis into the stirrer by using an automatic strain spraying machine, uniformly stirring the bacillus subtilis and the bacillus licheniformis with the powdery fertilizer, sampling and inspecting, conveying the qualified powdery fertilizer into an automatic weighing and packaging machine to measure and package the qualified powdery fertilizer into a finished product, and conveying the unqualified powdery fertilizer after inspection into the step (1) according to process requirements to process the unqualified powdery fertilizer.
Furthermore, each ton of the powdery fertilizer contains 60 percent of chicken manure, 15 percent of mushroom residue, 9 percent of plant ash, 5 percent of bovine bone meal, 5 percent of organic bean dregs, 4.5 percent of calcium superphosphate, 0.6 percent of bacillus subtilis, 0.4 percent of bacillus licheniformis and 0.5 percent of decomposing agent.
Further, the organic bean dregs are peanut bran.
Furthermore, the decomposing inoculant is an organic material decomposing inoculant with the effective viable count of more than or equal to 0.50 hundred million/g.
The technical effects of the invention are mainly reflected in the following aspects: the chicken manure is shoveled into a stirrer, mushroom residue, plant ash, bovine bone meal, organic bean dregs and calcium superphosphate are added for crushing and mixing, then a decomposition agent is uniformly sprayed, a fertilizer pile is stacked on a cement stacking table and is sequentially fermented and decomposed, percolate generated in the fermentation process is used for promoting secondary fermentation decomposition and tertiary fermentation decomposition, meanwhile, through arrangement of radiating holes in the fermentation decomposition process, the temperature in the fermentation decomposition process is effectively controlled to be kept at 50-70 ℃, ventilation and heat dissipation are facilitated, the compost can be uniformly decomposed, and meanwhile, harmless treatment of sterilization and insect killing is achieved, so that the quality of the biological organic fertilizer is improved on the basis of shortening the period of forming the chicken manure stacking fermentation organic fertilizer, the fermentation percolate is effectively recycled, and the environment is friendly.
Detailed Description
The embodiments of the present invention are described in further detail to make the technical solutions of the present invention easier to understand and master.
Examples
A preparation process of a chicken manure stacking fermentation bio-organic fertilizer comprises the following steps:
step 1: conveying raw material chicken manure blocks into an aerobic fermentation workshop by using a conveying belt, stirring and loosening by using a forklift, shoveling the loosened chicken manure into a stirrer by using the forklift, adding mushroom residues, plant ash, bovine bone meal, organic bean dregs and calcium superphosphate into the stirrer, crushing and mixing by using the stirrer, spraying a thoroughly-decomposed agent by using an automatic strain spraying machine in the stirring process, fully and uniformly stirring, and then screening stones and branches by using a screening machine to prepare a composting raw material for later use;
step 2, stacking and fermenting the compost raw materials prepared in the step 1 in an aerobic fermentation workshop by using a forklift, and specifically comprising the following steps:
a. pouring a cement stacking platform with the length of 16 meters and the width of 10 meters in an aerobic fermentation workshop, pouring a liquid drainage groove at the edge of the cement stacking platform 1, and pouring a liquid storage tank at the end of the liquid drainage groove for later use;
b. stacking the compost raw materials prepared in the step 1 on a cement stacking table in the specific step a to form a compost fermentation pile with the width of 8 meters, the height of 4.5 meters and the pile length of 15 meters, and then uniformly distributing ventilation and heat dissipation holes above the compost fermentation pile by utilizing an iron rod with the radius of 3cm in a mode of inserting from top to bottom, so that the temperature of the compost fermentation pile in the fermentation process is controlled to be 50-70 ℃ for later use;
c. b, performing first fermentation according to the compost fermentation pile finished in the specific step b, wherein the fermentation time is 8 days, and as the water content of compost raw materials is low, spraying purified water to the compost fermentation pile to ensure that the humidity of the compost fermentation pile reaches 40%, in the fermentation process, during the first fermentation day, the temperature of the compost fermentation pile is increased to 50 ℃, then slowly increased to 70 ℃, and kept for 7-8 days, at the moment, most parasitic ova and harmful bacteria in the compost fermentation pile are killed at high temperature to finish harmless treatment, and meanwhile, as hydrolysis is generated in the fermentation process, the compost fermentation pile generates percolate rich in thoroughly decomposed agents and is collected into a liquid storage tank through a liquid drainage groove for later use;
d. c, performing first fermentation treatment on the compost fermentation pile for 8 days by a specific step c, turning the compost fermentation pile by using a groove type pile turning machine, stacking on a cement stacking table again, tightly pressing the secondary compost fermentation pile by using a forklift into a secondary compost fermentation pile with the width of 8 meters, the height of 4.5 meters and the pile length of 15 meters, and meanwhile, arranging air-permeable heat dissipation holes by using an iron rod with the radius of 3cm above the secondary compost fermentation pile in a manner of inserting from top to bottom so that the temperature of the compost fermentation pile is still controlled to be 50-70 ℃ in the fermentation process, extracting and spraying percolate generated by first fermentation to the secondary compost fermentation pile through a pump body for 16 days, and collecting the percolate generated by secondary compost fermentation into a liquid storage tank through a liquid drainage groove for later use;
e. in the concrete step d, conveying the raw materials to a fermentation tank of an aerobic fermentation workshop by using a forklift to perform third fermentation, spraying the percolate in a liquid storage tank to the stacked compost in the fermentation tank again, controlling the fermentation temperature to be 50-70 ℃ at the same time, finely turning the compost by using an automatic pile turning machine during the fermentation period to evaporate the percolate, shoveling the compost fermentation pile to a cement stacking platform by using the forklift after the humidity of the compost fermentation pile is reduced to 20%, finely loosening the compost fermentation pile, stacking again to perform fourth pile turning fermentation for 25-27 days, drying the compost fermentation pile due to water evaporation, and beginning to reduce the fermentation temperature, wherein the color of the compost fermentation pile becomes deep brown black, namely the fermentation rotten process of the compost fermentation pile is completed for later use;
and step 3: in the step 2, the compost fermentation pile is conveyed to an automatic blanking machine in batches after four times of fermentation is finished, then conveyed to a crusher by a conveyer belt to be crushed twice, and conveyed to a mesh screen machine to be screened into primary powder after being crushed, and then is subjected to deodorization treatment by a dust removal deodorizer after being screened, and the powder fertilizer enters the next procedure after meeting the requirement, and returns to an aerobic fermentation workshop to mix chicken manure blocks to be stirred for rework treatment because the powder fertilizer does not meet the requirement due to uneven mixing of a decomposing agent;
step five: and (4) feeding the qualified powdery fertilizer in the step (4) into a stirrer, controlling stirring to turn at a speed of 55r/pm, spraying bacillus subtilis and bacillus licheniformis into the stirrer by using an automatic strain spraying machine, uniformly stirring the bacillus subtilis and the bacillus licheniformis with the powdery fertilizer, sampling and inspecting, conveying the qualified powdery fertilizer into an automatic weighing and packaging machine to measure and package the qualified powdery fertilizer into a finished product, and conveying the unqualified powdery fertilizer after inspection into the step (1) according to process requirements to process the unqualified powdery fertilizer.
In this example, each ton of the powdered fertilizer contains 60% of chicken manure, 15% of mushroom dregs, 9% of plant ash, 5% of bovine bone meal, 5% of organic bean dregs, 4.5% of calcium superphosphate, 0.6% of bacillus subtilis, 0.4% of bacillus licheniformis and 0.5% of a decomposition agent.
In this embodiment, the organic bean dregs are peanut bran.
In this embodiment, the decomposing inoculant is an organic material decomposing inoculant with an effective viable count of more than or equal to 0.50 hundred million/g.
The technical effects of the invention are mainly reflected in the following aspects: the chicken manure is shoveled into a stirrer, mushroom residue, plant ash, bovine bone meal, organic bean dregs and calcium superphosphate are added for crushing and mixing, then a decomposition agent is uniformly sprayed, a fertilizer pile is stacked on a cement stacking table and is sequentially fermented and decomposed, percolate generated in the fermentation process is used for promoting secondary fermentation decomposition and tertiary fermentation decomposition, meanwhile, through arrangement of radiating holes in the fermentation decomposition process, the temperature in the fermentation decomposition process is effectively controlled to be kept at 50-70 ℃, ventilation and heat dissipation are facilitated, the compost can be uniformly decomposed, and meanwhile, harmless treatment of sterilization and insect killing is achieved, so that the quality of the biological organic fertilizer is improved on the basis of shortening the period of forming the chicken manure stacking fermentation organic fertilizer, the fermentation percolate is effectively recycled, and the environment is friendly.
The above are only typical examples of the present invention, and besides, the present invention may have other embodiments, and all the technical solutions formed by equivalent substitutions or equivalent changes are within the scope of the present invention as claimed.
Claims (4)
1. A preparation process of a chicken manure stacking fermentation bio-organic fertilizer is characterized by comprising the following steps:
step 1: conveying raw material chicken manure blocks into an aerobic fermentation workshop by using a conveying belt, stirring and loosening by using a forklift, shoveling the loosened chicken manure into a stirrer by using the forklift, adding mushroom residues, plant ash, bovine bone meal, organic bean dregs and calcium superphosphate into the stirrer, crushing and mixing by using the stirrer, spraying a thoroughly-decomposed agent by using an automatic strain spraying machine in the stirring process, fully and uniformly stirring, and then screening stones and branches by using a screening machine to prepare a composting raw material for later use;
step 2, stacking and fermenting the compost raw materials prepared in the step 1 in an aerobic fermentation workshop by using a forklift, and specifically comprising the following steps:
a. pouring a cement stacking platform with the length of 16 meters and the width of 10 meters in an aerobic fermentation workshop, pouring a liquid drainage groove at the edge of the cement stacking platform, and pouring a liquid storage tank at the end of the liquid drainage groove for later use;
b. stacking the compost raw materials prepared in the step 1 on a cement stacking table in the specific step a to form a compost fermentation pile with the width of 8 meters, the height of 4.5 meters and the pile length of 15 meters, and then uniformly distributing ventilation and heat dissipation holes above the compost fermentation pile by utilizing an iron rod with the radius of 3cm in a mode of inserting from top to bottom, so that the temperature of the compost fermentation pile in the fermentation process is controlled to be 50-70 ℃ for later use;
c. b, performing first fermentation according to the compost fermentation pile finished in the specific step b, wherein the fermentation time is 8 days, and as the water content of compost raw materials is low, spraying purified water to the compost fermentation pile to ensure that the humidity of the compost fermentation pile reaches 40%, in the fermentation process, during the first fermentation day, the temperature of the compost fermentation pile is increased to 50 ℃, then slowly increased to 70 ℃, and kept for 7-8 days, at the moment, most parasitic ova and harmful bacteria in the compost fermentation pile are killed at high temperature to finish harmless treatment, and meanwhile, as hydrolysis is generated in the fermentation process, the compost fermentation pile generates percolate rich in thoroughly decomposed agents and is collected into a liquid storage tank through a liquid drainage groove for later use;
d. c, performing first fermentation treatment on the compost fermentation pile for 8 days by a specific step c, turning the compost fermentation pile by using a groove type pile turning machine, stacking on a cement stacking table again, tightly pressing the secondary compost fermentation pile by using a forklift into a secondary compost fermentation pile with the width of 8 meters, the height of 4.5 meters and the pile length of 15 meters, and meanwhile, arranging air-permeable heat dissipation holes by using an iron rod with the radius of 3cm above the secondary compost fermentation pile in a manner of inserting from top to bottom so that the temperature of the compost fermentation pile is still controlled to be 50-70 ℃ in the fermentation process, extracting and spraying percolate generated by first fermentation to the secondary compost fermentation pile through a pump body for 16 days, and collecting the percolate generated by secondary compost fermentation into a liquid storage tank through a liquid drainage groove for later use;
e. in the concrete step d, conveying the raw materials to a fermentation tank of an aerobic fermentation workshop by using a forklift to perform third fermentation, spraying the percolate in a liquid storage tank to the stacked compost in the fermentation tank again, controlling the fermentation temperature to be 50-70 ℃ at the same time, finely turning the compost by using an automatic pile turning machine during the fermentation period to evaporate the percolate, shoveling the compost fermentation pile to a cement stacking platform by using the forklift after the humidity of the compost fermentation pile is reduced to 20%, finely loosening the compost fermentation pile, stacking again to perform fourth pile turning fermentation for 25-27 days, drying the compost fermentation pile due to water evaporation, and beginning to reduce the fermentation temperature, wherein the color of the compost fermentation pile becomes deep brown black, namely the fermentation rotten process of the compost fermentation pile is completed for later use;
and step 3: in the step 2, the compost fermentation pile is conveyed to an automatic blanking machine in batches after four times of fermentation is finished, then conveyed to a crusher by a conveyer belt to be crushed twice, and conveyed to a mesh screen machine to be screened into primary powder after being crushed, and then is subjected to deodorization treatment by a dust removal deodorizer after being screened, and the powder fertilizer enters the next procedure after meeting the requirement, and returns to an aerobic fermentation workshop to mix chicken manure blocks to be stirred for rework treatment because the powder fertilizer does not meet the requirement due to uneven mixing of a decomposing agent;
step five: and (4) feeding the qualified powdery fertilizer in the step (4) into a stirrer, controlling stirring to turn at a speed of 55r/pm, spraying bacillus subtilis and bacillus licheniformis into the stirrer by using an automatic strain spraying machine, uniformly stirring the bacillus subtilis and the bacillus licheniformis with the powdery fertilizer, sampling and inspecting, conveying the qualified powdery fertilizer into an automatic weighing and packaging machine to measure and package the qualified powdery fertilizer into a finished product, and conveying the unqualified powdery fertilizer after inspection into the step (1) according to process requirements to process the unqualified powdery fertilizer.
2. The preparation process of the chicken manure stacking fermentation bio-organic fertilizer as claimed in claim 1, wherein the preparation process comprises the following steps: each ton of powdery fertilizer contains 60 percent of chicken manure, 15 percent of mushroom residue, 9 percent of plant ash, 5 percent of bovine bone meal, 5 percent of organic bean dregs, 4.5 percent of calcium superphosphate, 0.6 percent of bacillus subtilis, 0.4 percent of bacillus licheniformis and 0.5 percent of decomposing agent.
3. The preparation process of the chicken manure stacking fermentation bio-organic fertilizer as claimed in claim 1, wherein the preparation process comprises the following steps: the organic bean dregs are peanut bran.
4. The preparation process of the chicken manure stacking fermentation bio-organic fertilizer as claimed in claim 1, wherein the preparation process comprises the following steps: the decomposing inoculant is an organic material decomposing inoculant with the effective viable count of more than or equal to 0.50 hundred million/g.
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Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN114671715A (en) * | 2022-02-09 | 2022-06-28 | 浙江千源环保科技有限公司 | Method for preparing regenerated nutrient soil by adopting urban organic wastes and agricultural and forestry wastes |
| CN116217296A (en) * | 2023-03-17 | 2023-06-06 | 山东庞大生物集团有限公司 | Production process for carbon fixation and emission reduction of bio-organic fertilizer |
Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101948336A (en) * | 2010-09-06 | 2011-01-19 | 上海京瓷电子有限公司 | Apparatus and method for completely-mixed fermentation treatment of kitchen/bathroom organic wastes |
| CN103524161A (en) * | 2013-10-21 | 2014-01-22 | 谢明英 | Process for fermenting organic fertilizer by poultry and livestock excrement |
| CN107879843A (en) * | 2017-11-17 | 2018-04-06 | 辽宁天牧生物科技有限公司 | A kind of method that compound bacteria-fermented chicken manure prepares organic fertilizer |
-
2021
- 2021-06-10 CN CN202110649916.XA patent/CN113321542A/en active Pending
Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101948336A (en) * | 2010-09-06 | 2011-01-19 | 上海京瓷电子有限公司 | Apparatus and method for completely-mixed fermentation treatment of kitchen/bathroom organic wastes |
| CN103524161A (en) * | 2013-10-21 | 2014-01-22 | 谢明英 | Process for fermenting organic fertilizer by poultry and livestock excrement |
| CN107879843A (en) * | 2017-11-17 | 2018-04-06 | 辽宁天牧生物科技有限公司 | A kind of method that compound bacteria-fermented chicken manure prepares organic fertilizer |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN114671715A (en) * | 2022-02-09 | 2022-06-28 | 浙江千源环保科技有限公司 | Method for preparing regenerated nutrient soil by adopting urban organic wastes and agricultural and forestry wastes |
| CN116217296A (en) * | 2023-03-17 | 2023-06-06 | 山东庞大生物集团有限公司 | Production process for carbon fixation and emission reduction of bio-organic fertilizer |
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Application publication date: 20210831 |
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