CN112723949A - Tea acidified soil remediation bio-organic fertilizer and preparation method thereof - Google Patents
Tea acidified soil remediation bio-organic fertilizer and preparation method thereof Download PDFInfo
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- C05B13/02—Fertilisers produced by pyrogenic processes from phosphatic materials from rock phosphates
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- 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
- C05G—MIXTURES OF FERTILISERS COVERED INDIVIDUALLY BY DIFFERENT SUBCLASSES OF CLASS C05; MIXTURES OF ONE OR MORE FERTILISERS WITH MATERIALS NOT HAVING A SPECIFIC FERTILISING ACTIVITY, e.g. PESTICIDES, SOIL-CONDITIONERS, WETTING AGENTS; FERTILISERS CHARACTERISED BY THEIR FORM
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- C05—FERTILISERS; MANUFACTURE THEREOF
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- C05G3/80—Soil conditioners
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Abstract
The invention belongs to the technical field of soil improvement and discloses a tea acidified soil restoration bio-organic fertilizer and a preparation method thereof, wherein the tea acidified soil restoration bio-organic fertilizer comprises, by mass, 20-25 parts of biochar, 10-15 parts of plant ash, 10-15 parts of river silt, 15-20 parts of earthworm powder, 8-10 parts of animal manure, 5-10 parts of calcium magnesium phosphate fertilizer, 5-8 parts of silkworm excrement, 5-8 parts of zinc oxide, 5-8 parts of montmorillonite, 1-3 parts of clay minerals, 1-3 parts of chaff silica alkali and 1-3 parts of bacillus amyloliquefaciens. The organic fertilizer can effectively improve the pH value of soil and improve the yield and quality of tea; meanwhile, the cost is low, the raw materials are easy to obtain, the manufacturing method is simple and convenient, and the soil disinfectant contains rich medium and trace elements and has a soil disinfection function. The invention can improve the physical and chemical properties of soil: the soil pH value can be adjusted, soil hardening is prevented, the soil aggregate structure is improved, the soil is loosened, and air and moisture are increased.
Description
Technical Field
The invention belongs to the technical field of soil improvement, and particularly relates to a tea acidified soil restoration bio-organic fertilizer and a preparation method thereof.
Background
At present: tea trees are typical acid-loving crops, and the suitable pH value of the tea trees is 4.5-5.5. After the tea trees are planted, the soil can be gradually acidified due to physiological effects of organic acid secretion and the like of the tea trees; acid rain, excessive application of fertilizers, particularly urea and ammonium nitrogen fertilizers, can aggravate soil acidification. The research shows that the tea garden soil is continuously acidified, according to the research of tea institute of Chinese academy of agricultural sciences, the pH value of most tea garden soil in the three provinces of Jiang, Zhe and Wan in 1990 and 1991 is above 4.5, the pH value is only 13.7% when the pH value is less than 4.0, the measurement result in 1998 is increased to 43.9%, and the recent research shows that the pH value of nearly half of tea garden soil is less than 4.0. On the national scale, tea garden soil also shows a continuous acidification trend, and at present, the pH value of the soil is less than 4.0 by about one third.
Tea trees are acid-loving crops, the pH value of soil is more than 6.5, the growth and development of the tea trees are not facilitated, but the excessive acidification causes serious imbalance of soil nutrients, poor biological properties and soil hardening, and the growth and development of the tea trees are also influenced. If the pH value of the soil is about 5.0, the tea tree has developed root system and vigorous growth, tea buds are strong, and young shoots grow quickly; when the pH value is less than 4.0, the root tip is atrophied and growth is inhibited, at the moment, the absorption of nitrogen, phosphorus and potassium by the tea tree is sharply reduced, germination is retarded, and young shoots grow slowly. In addition, excessive acidification can also lead to the improvement of the bioavailability of heavy metal elements such as lead in the soil, thereby affecting the safety quality and the quality of the tea. Therefore, the method for improving the severely acidified tea garden soil not only can obviously improve the soil quality level, but also has an important effect on improving the tea yield and quality.
At present, lime substances are generally used for improving acidified soil in agricultural production, the problem of soil acidification cannot be fundamentally solved by applying lime, and certain adverse effects exist, such as: reduce the water permeability of soil, slow down the growth of leguminous and non-leguminous crops, reduce the phosphorus absorption of plants and the like. The nitrogenous fertilizer in the chemical fertilizer market of China mainly contains urea and ammonium nitrogen, the phosphatic fertilizer market mainly contains monoammonium phosphate, diammonium phosphate and calcium superphosphate, and the potash fertilizer mainly contains potassium sulfate and potassium chloride.
Through the above analysis, the problems and defects of the prior art are as follows: the existing acidified soil improvement can not solve the problem of soil acidification, and can affect the yield and quality of tea leaves.
Disclosure of Invention
Aiming at the problems in the prior art, the invention provides a tea acidified soil remediation bio-organic fertilizer and a preparation method thereof.
The invention is realized by the following steps that the tea acidified soil restoration bio-organic fertilizer is composed of, by mass, 20-25 parts of biochar, 10-15 parts of plant ash, 10-15 parts of river sludge, 15-20 parts of earthworm powder, 8-10 parts of animal manure, 5-10 parts of calcium magnesium phosphate fertilizer, 5-8 parts of silkworm excrement, 5-8 parts of zinc oxide, 5-8 parts of montmorillonite, 1-3 parts of clay minerals, 1-3 parts of chaff silica alkali and 1-3 parts of bacillus amyloliquefaciens (purchased in the market).
The invention also provides a preparation method of the tea-leaf acidified soil restoration bio-organic fertilizer, which comprises the following steps:
step one, preparing biochar and modifying with mild alkali; weighing biochar, plant ash, river silt, earthworm powder, animal manure, calcium magnesium phosphate fertilizer, silkworm excrement, zinc oxide, montmorillonite, clay minerals, chaff silica and bacillus amyloliquefaciens according to the proportion;
decomposing the weighed animal wastes, primarily crushing the prepared biochar, river sludge, silkworm excrement, montmorillonite and clay minerals, and processing the crushed biochar into a powdery mixture of 80-90 meshes by using a ball mill or a high-speed Raymond mill;
step three, uniformly mixing the obtained subpackaged mixture with plant ash, earthworm powder, zinc oxide, decomposed animal manure and calcium magnesium phosphate fertilizer, adding water, and adjusting the water content of the mixed material to 50-55% to obtain a mixed material;
step four, performing compost fermentation on the mixed material; adding the mixed fermentation product into a bacillus amyloliquefaciens liquid culture, and naturally airing until the water content of the material is lower than 20%;
and fifthly, placing the aired natural materials in a closed reaction kettle, introducing steam, pressurizing to 16 atmospheric pressure, performing steam curing and activating treatment for 4-6 hours, and controlling the temperature at 110-120 ℃ to obtain the tea acidified soil remediation bio-organic fertilizer.
Further, in the first step, the preparation of the biochar comprises the following steps:
1) the municipal sludge is sequentially subjected to concentration, conditioning modification and high-dry dehydration to form a dehydrated mud cake; sequentially crushing and drying the dehydrated mud cakes;
2) putting the crushed and dried dehydrated mud cakes into a muffle furnace, introducing nitrogen for oxygen isolation, continuously heating to 450-600 ℃, firing at constant temperature for 4-6h, and carrying out pyrolysis carbonization to obtain primary biochar;
3) and cooling the preliminary biochar to room temperature, grinding and sieving the preliminary biochar by a 90-mesh sieve, washing the preliminary biochar by water for a plurality of times, removing surface ash, and drying to obtain the biochar.
Further, in the step one, the performing of the mild alkali modification of the biochar comprises:
firstly, adding the prepared biochar into mild alkali reaction liquid for soaking modification;
and secondly, washing the treated biochar with water until the eluate is neutral, and drying.
Further, the mild alkali reaction solution is prepared from a 3% sodium hydroxide solution and a 2% hydrogen peroxide solution according to the mass part ratio of 5: 3 is configured.
Further, the modification treatment parameters are as follows: the temperature is 120 ℃, the solid-to-liquid ratio is 5g:120mL, and the treatment time is 6-8 h.
Further, in the second step, the decomposing the weighed animal wastes comprises:
1) mixing the weighed animal wastes and the decomposing agent, placing the mixture on a stacking rack in a fermentation chamber, controlling the humidity of the uniformly mixed animal wastes and the decomposing agent to be 70%, closing the fermentation chamber, controlling the indoor humidity to be 70%, controlling the indoor pressure to be 0.6 atm, controlling the indoor temperature to be 20-25 ℃, controlling the indoor oxygen content to be 26-27%, and carrying out aerobic fermentation for 7-8 h;
2) taking out the mixture of the aerobic fermented animal waste and the decomposing agent for closed fermentation, controlling the temperature at 20-25 ℃, controlling the humidity at 55-60% and controlling the fermentation time at 9-10 days;
3) raising the temperature to 80-85 ℃, keeping the humidity unchanged, continuing fermenting for 2 days, drying and granulating to obtain the decomposed animal manure.
Further, in the step 1), the decomposing inoculant comprises, by mass, 20-25 parts of rice chaff, 20-25 parts of wheat bran, 10-15 parts of soybean protein powder, 10-15 parts of bacillus subtilis liquid strain and 10-15 parts of urea; 5-10 parts of lactobacillus bulgaricus and 5-8 parts of Cornus canadensis.
Further, the preparation method of the decomposition agent comprises the following steps:
1) respectively activating and propagating bacillus subtilis liquid strains, lactobacillus bulgaricus and xylaria kansei, and uniformly mixing the obtained three kinds of bacteria liquid to obtain a composite microbial inoculum;
2) drying and crushing rice chaff, wheat bran and urea at low temperature, and sieving by a sieve of 60-80 meshes to obtain mixed particles; mixing the mixed particles with the composite microbial inoculum according to the weight ratio of 5: 3, and fermenting for 1-2 days at 65-70 ℃;
3) adding soybean protein powder into the primary fermented product, stirring, and fermenting for 2-3 days to obtain fermented product;
4) and drying the obtained fermentation product at 38-40 ℃ to obtain the decomposing inoculant.
Further, in the fourth step, the compost fermentation comprises: controlling the temperature at 75-80 deg.C, continuing for 5-8 days, turning over and ventilating once a day, and when the water content of the material is reduced to below 20%, obtaining the fermented and decomposed material.
By combining all the technical schemes, the invention has the advantages and positive effects that: the organic fertilizer can effectively improve the pH value of soil and improve the yield and quality of tea; meanwhile, the cost is low, the raw materials are easy to obtain, the manufacturing method is simple and convenient, and the soil disinfectant contains rich medium and trace elements and has a soil disinfection function.
The invention can improve the physical and chemical properties of soil: the soil pH value can be adjusted, the soil is prevented from hardening, the soil aggregate structure is improved, the soil is loosened, and air and moisture are increased; meanwhile, the bacillus amyloliquefaciens contains various nutritional ingredients, can effectively improve the yield and the quality of tea trees, and can improve the biological properties of soil and promote the growth of the tea trees by using beneficial microorganisms with the growth promoting effect of the bacillus amyloliquefaciens on the tea trees.
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In order to more clearly illustrate the technical solutions of the embodiments of the present application, the drawings needed to be used in the embodiments of the present application will be briefly described below, and it is obvious that the drawings described below are only some embodiments of the present application, and it is obvious for those skilled in the art that other drawings can be obtained from the drawings without creative efforts.
Fig. 1 is a flow chart of a preparation method of a tea-leaf-acidified soil remediation bio-organic fertilizer provided by the embodiment of the invention.
FIG. 2 is a flow chart of a method for producing biochar according to an embodiment of the present invention.
FIG. 3 is a flow chart of a method for performing mild alkali modification of biochar according to an embodiment of the present invention.
Fig. 4 is a flow chart of a method for decomposing the feces of the weighed animal according to the embodiment of the present invention.
Fig. 5 is a flow chart of a method for preparing the decomposing inoculant provided by the embodiment of the invention.
Detailed Description
In order to make the objects, technical solutions and advantages of the present invention more apparent, the present invention is further described in detail with reference to the following embodiments. It should be understood that the specific embodiments described herein are merely illustrative of the invention and are not intended to limit the invention.
Aiming at the problems in the prior art, the invention provides a tea leaf acidified soil remediation bio-organic fertilizer, which is described in detail in the following with reference to the accompanying drawings.
The tea acidified soil remediation bio-organic fertilizer provided by the embodiment of the invention comprises, by mass, 20-25 parts of biochar, 10-15 parts of plant ash, 10-15 parts of river sludge, 15-20 parts of earthworm powder, 8-10 parts of animal manure, 5-10 parts of calcium magnesium phosphate fertilizer, 5-8 parts of silkworm excrement, 5-8 parts of zinc oxide, 5-8 parts of montmorillonite, 1-3 parts of clay minerals, 1-3 parts of chaff silicane and 1-3 parts of bacillus amyloliquefaciens.
The bacillus amyloliquefaciens provided by the embodiment of the invention can be purchased from the market.
As shown in fig. 1, the preparation method of the bio-organic fertilizer for restoring tea-acidified soil provided by the embodiment of the invention comprises the following steps:
s101, preparing biochar and modifying with mild alkali; weighing biochar, plant ash, river silt, earthworm powder, animal manure, calcium magnesium phosphate fertilizer, silkworm excrement, zinc oxide, montmorillonite, clay minerals, chaff silica and bacillus amyloliquefaciens according to the proportion;
s102, decomposing the weighed animal wastes, primarily crushing the prepared biochar, river sludge, silkworm excrement, montmorillonite and clay minerals, and processing the crushed biochar into a powdery mixture of 80-90 meshes by using a ball mill or a high-speed Raymond mill;
s103, uniformly mixing the obtained subpackaged mixture with plant ash, earthworm powder, zinc oxide, decomposed animal manure and calcium magnesium phosphate fertilizer, adding water, and adjusting the water content of the mixed material to 50-55% to obtain a mixed material;
s104, performing compost fermentation on the mixed material; adding the mixed fermentation product into a bacillus amyloliquefaciens liquid culture, and naturally airing until the water content of the material is lower than 20%;
s105, placing the aired natural materials in a closed reaction kettle, introducing steam, pressurizing to 16 atmospheric pressure, performing steam curing and activating treatment for 4-6 hours, and controlling the temperature at 110-120 ℃ to obtain the tea acidified soil remediation bio-organic fertilizer.
As shown in fig. 2, in step S101, the preparation of biochar according to the embodiment of the present invention includes:
s201, sequentially concentrating, conditioning, modifying and dehydrating municipal sludge to obtain dehydrated mud cakes; sequentially crushing and drying the dehydrated mud cakes;
s202, placing the crushed and dried dehydrated mud cakes into a muffle furnace, introducing nitrogen for oxygen isolation, continuously heating to the temperature of 450-class sand 600 ℃, firing at a constant temperature for 4-6h, and carrying out pyrolysis carbonization to obtain primary biochar;
s203, cooling the preliminary biochar to room temperature, grinding and sieving the preliminary biochar by a 90-mesh sieve, washing the preliminary biochar by water for a plurality of times, removing surface ash, and drying to obtain the biochar.
As shown in fig. 3, in step S101, performing mild alkali modification of biochar according to an embodiment of the present invention includes:
s301, adding the prepared biochar into a mixture of a 3% sodium hydroxide solution and a 2% hydrogen peroxide solution according to the mass part ratio of 5: 3 soaking and modifying the prepared mild alkali reaction solution;
s302, washing the treated biochar with water until the eluate is neutral, and drying.
In step S301, the modification processing parameters provided in the embodiment of the present invention are: the temperature is 120 ℃, the solid-to-liquid ratio is 5g:120mL, and the treatment time is 6-8 h.
As shown in fig. 4, in step S102, the decomposing the weighed animal feces according to the embodiment of the present invention includes:
s401, mixing the weighed animal wastes with a decomposing agent, placing the mixture on a stacking rack in a fermentation chamber, wherein the stacking thickness is not more than 16cm, controlling the humidity of the uniformly mixed animal wastes and the decomposing agent at 70%, closing the fermentation chamber, controlling the indoor humidity at 70%, controlling the indoor pressure at 0.6 atmospheric pressure, controlling the indoor temperature at 20-25 ℃, controlling the indoor oxygen content at 26-27%, and carrying out aerobic fermentation for 7-8 h;
s402, taking out the mixture of the aerobic fermented animal manure and the decomposing agent for closed fermentation, controlling the temperature at 20-25 ℃, controlling the humidity at 55-60% and controlling the fermentation time at 9-10 days;
and S403, raising the temperature to 80-85 ℃, keeping the humidity unchanged, continuing fermenting for 2 days, and drying and granulating to obtain the decomposed animal manure.
In step S401, the decomposing inoculant provided by the embodiment of the invention comprises, by mass, 20-25 parts of rice chaff, 20-25 parts of wheat bran, 10-15 parts of soybean protein powder, 10-15 parts of bacillus subtilis liquid strains and 10-15 parts of urea; 5-10 parts of lactobacillus bulgaricus and 5-8 parts of Cornus canadensis.
As shown in fig. 5, in step S102, the preparation method of the decomposing inoculant provided by the embodiment of the invention includes:
s501, respectively carrying out activation and propagation culture on a bacillus subtilis liquid strain, lactobacillus bulgaricus and xylaria kansei, and uniformly mixing the obtained three kinds of bacteria liquid to obtain a composite microbial inoculum;
s502, drying and crushing rice chaff, wheat bran and urea at low temperature, and sieving by a 60-80-mesh sieve to obtain mixed particles; mixing the mixed particles with the composite microbial inoculum according to the weight ratio of 5: 3, and fermenting for 1-2 days at 65-70 ℃;
s503, adding the soybean protein powder into the primary fermentation product, uniformly stirring, and continuing to ferment for 2-3 days to obtain a fermentation product;
s504, drying the obtained fermentation product at 38-40 ℃ to obtain the decomposing inoculant.
In step S104, the compost fermentation provided by the embodiment of the present invention includes: controlling the temperature at 75-80 deg.C, continuing for 5-8 days, turning over and ventilating once a day, and when the water content of the material is reduced to below 20%, obtaining the fermented and decomposed material.
The above description is only for the purpose of illustrating the preferred embodiments of the present invention, and the scope of the present invention is not limited thereto, and any modification, equivalent replacement, and improvement made by those skilled in the art within the technical scope of the present invention disclosed herein, which is within the spirit and principle of the present invention, should be covered by the present invention.
Claims (10)
1. The tea acidified soil restoration bio-organic fertilizer is characterized by comprising, by mass, 20-25 parts of biochar, 10-15 parts of plant ash, 10-15 parts of river sludge, 15-20 parts of earthworm powder, 8-10 parts of animal manure, 5-10 parts of calcium magnesium phosphate fertilizer, 5-8 parts of silkworm excrement, 5-8 parts of zinc oxide, 5-8 parts of montmorillonite, 1-3 parts of clay minerals, 1-3 parts of chaff silica alkali and 1-3 parts of bacillus amyloliquefaciens.
2. A method for preparing the tea-leaf-acidification-soil-restoration bio-organic fertilizer according to claim 1, wherein the method for preparing the tea-leaf-acidification-soil-restoration bio-organic fertilizer comprises the following steps:
step one, preparing biochar and modifying with mild alkali; weighing biochar, plant ash, river silt, earthworm powder, animal manure, calcium magnesium phosphate fertilizer, silkworm excrement, zinc oxide, montmorillonite, clay minerals, chaff silica and bacillus amyloliquefaciens according to the proportion;
decomposing the weighed animal wastes, primarily crushing the prepared biochar, river sludge, silkworm excrement, montmorillonite and clay minerals, and processing the crushed biochar into a powdery mixture of 80-90 meshes by using a ball mill or a high-speed Raymond mill;
step three, uniformly mixing the obtained subpackaged mixture with plant ash, earthworm powder, zinc oxide, decomposed animal manure and calcium magnesium phosphate fertilizer, adding water, and adjusting the water content of the mixed material to 50-55% to obtain a mixed material;
step four, performing compost fermentation on the mixed material; adding the mixed fermentation product into a bacillus amyloliquefaciens liquid culture, and naturally airing until the water content of the material is lower than 20%;
and fifthly, placing the aired natural materials in a closed reaction kettle, introducing steam, pressurizing to 16 atmospheric pressure, performing steam curing and activating treatment for 4-6 hours, and controlling the temperature at 110-120 ℃ to obtain the tea acidified soil remediation bio-organic fertilizer.
3. The method for preparing the bio-organic fertilizer for restoring the acidified soil with tea leaves as claimed in claim 2, wherein in the first step, the preparation of the biochar comprises the following steps:
1) the municipal sludge is sequentially subjected to concentration, conditioning modification and high-dry dehydration to form a dehydrated mud cake; sequentially crushing and drying the dehydrated mud cakes;
2) putting the crushed and dried dehydrated mud cakes into a muffle furnace, introducing nitrogen for oxygen isolation, continuously heating to 450-600 ℃, firing at constant temperature for 4-6h, and carrying out pyrolysis carbonization to obtain primary biochar;
3) and cooling the preliminary biochar to room temperature, grinding and sieving the preliminary biochar by a 90-mesh sieve, washing the preliminary biochar by water for a plurality of times, removing surface ash, and drying to obtain the biochar.
4. The method for preparing the bio-organic fertilizer for restoring the acidified soil with tea leaves as claimed in claim 2, wherein in the first step, the mild alkali modification of the biochar comprises:
firstly, adding the prepared biochar into mild alkali reaction liquid for soaking modification;
and secondly, washing the treated biochar with water until the eluate is neutral, and drying.
5. The preparation method of the tea acidification soil remediation bio-organic fertilizer as claimed in claim 4, wherein the mild alkali reaction solution is prepared from 3% sodium hydroxide solution and 2% hydrogen peroxide solution in parts by mass of 5: 3 is configured.
6. The method for preparing the bio-organic fertilizer for remediating the acidified soil with tea as claimed in claim 4, wherein the modification treatment parameters are as follows: the temperature is 120 ℃, the solid-to-liquid ratio is 5g:120mL, and the treatment time is 6-8 h.
7. The method for preparing the bio-organic fertilizer for remediating the acidified soil with tea as claimed in claim 2, wherein in the second step, the step of decomposing the weighed animal wastes comprises the steps of:
1) mixing the weighed animal wastes and the decomposing agent, placing the mixture on a stacking rack in a fermentation chamber, controlling the humidity of the uniformly mixed animal wastes and the decomposing agent to be 70%, closing the fermentation chamber, controlling the indoor humidity to be 70%, controlling the indoor pressure to be 0.6 atm, controlling the indoor temperature to be 20-25 ℃, controlling the indoor oxygen content to be 26-27%, and carrying out aerobic fermentation for 7-8 h;
2) taking out the mixture of the aerobic fermented animal waste and the decomposing agent for closed fermentation, controlling the temperature at 20-25 ℃, controlling the humidity at 55-60% and controlling the fermentation time at 9-10 days;
3) raising the temperature to 80-85 ℃, keeping the humidity unchanged, continuing fermenting for 2 days, drying and granulating to obtain the decomposed animal manure.
8. The method for preparing the bio-organic fertilizer for restoring the acidified soil of tea as claimed in claim 7, wherein in the step 1), the decomposition agent comprises, by mass, 20-25 parts of rice chaff, 20-25 parts of wheat bran, 10-15 parts of soybean protein powder, 10-15 parts of bacillus subtilis liquid strain, and 10-15 parts of urea; 5-10 parts of lactobacillus bulgaricus and 5-8 parts of Cornus canadensis.
9. The method for preparing the bio-organic fertilizer for restoring the acidified soil by the tea leaves according to claim 8, wherein the preparation method of the decomposition agent comprises the following steps:
1) respectively activating and propagating bacillus subtilis liquid strains, lactobacillus bulgaricus and xylaria kansei, and uniformly mixing the obtained three kinds of bacteria liquid to obtain a composite microbial inoculum;
2) drying and crushing rice chaff, wheat bran and urea at low temperature, and sieving by a sieve of 60-80 meshes to obtain mixed particles; mixing the mixed particles with the composite microbial inoculum according to the weight ratio of 5: 3, and fermenting for 1-2 days at 65-70 ℃;
3) adding soybean protein powder into the primary fermented product, stirring, and fermenting for 2-3 days to obtain fermented product;
4) and drying the obtained fermentation product at 38-40 ℃ to obtain the decomposing inoculant.
10. The method for preparing the bio-organic fertilizer for remediating the acidified soil with tea leaves as claimed in claim 2, wherein in the fourth step, the fermentation of the compost comprises: controlling the temperature at 75-80 deg.C, continuing for 5-8 days, turning over and ventilating once a day, and when the water content of the material is reduced to below 20%, obtaining the fermented and decomposed material.
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Cited By (6)
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| CN112703849A (en) * | 2020-12-24 | 2021-04-27 | 湖南工业大学 | Method for improving tea planting soil |
| CN113461446A (en) * | 2021-07-27 | 2021-10-01 | 信阳农林学院 | Biological soil remediation fertilizer and preparation method and application thereof |
| CN113754494A (en) * | 2021-10-22 | 2021-12-07 | 天津科技大学 | Preparation method and product of biological modified clay mineral continuous cropping soil remediation agent |
| CN113800973A (en) * | 2021-09-27 | 2021-12-17 | 浙江益壤环保科技有限公司 | Soil conditioner suitable for acidic farmland and preparation method thereof |
| CN115368188A (en) * | 2022-08-19 | 2022-11-22 | 辽东学院 | Biochar-based corn fertilizer and preparation method thereof |
| CN115643847A (en) * | 2022-10-17 | 2023-01-31 | 中国农业科学院北京畜牧兽医研究所 | Method for repairing medium and light salinized grassland |
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| CN108299122A (en) * | 2017-12-08 | 2018-07-20 | 江苏省农业科学院 | A kind of soil conditioner for repairing acidified soil |
| CN108441222A (en) * | 2018-03-30 | 2018-08-24 | 华中农业大学 | A kind of tea place acidified soil conditioner and preparation method thereof |
| CN109748746A (en) * | 2017-11-08 | 2019-05-14 | 丹阳圣丽园农业发展有限公司 | A kind of acidified soil conditioner |
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2021
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Cited By (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN112703849A (en) * | 2020-12-24 | 2021-04-27 | 湖南工业大学 | Method for improving tea planting soil |
| CN112703849B (en) * | 2020-12-24 | 2022-02-11 | 湖南工业大学 | Method for improving tea planting soil |
| CN113461446A (en) * | 2021-07-27 | 2021-10-01 | 信阳农林学院 | Biological soil remediation fertilizer and preparation method and application thereof |
| CN113800973A (en) * | 2021-09-27 | 2021-12-17 | 浙江益壤环保科技有限公司 | Soil conditioner suitable for acidic farmland and preparation method thereof |
| CN113754494A (en) * | 2021-10-22 | 2021-12-07 | 天津科技大学 | Preparation method and product of biological modified clay mineral continuous cropping soil remediation agent |
| CN115368188A (en) * | 2022-08-19 | 2022-11-22 | 辽东学院 | Biochar-based corn fertilizer and preparation method thereof |
| CN115643847A (en) * | 2022-10-17 | 2023-01-31 | 中国农业科学院北京畜牧兽医研究所 | Method for repairing medium and light salinized grassland |
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Application publication date: 20210430 |