CN115417724A - Composite active slow-release organic fertilizer and preparation method thereof - Google Patents

Composite active slow-release organic fertilizer and preparation method thereof Download PDF

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CN115417724A
CN115417724A CN202211151590.9A CN202211151590A CN115417724A CN 115417724 A CN115417724 A CN 115417724A CN 202211151590 A CN202211151590 A CN 202211151590A CN 115417724 A CN115417724 A CN 115417724A
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organic fertilizer
slow
fertilizer
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CN115417724B (en
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陈奕齐
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    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05GMIXTURES 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
    • C05G3/00Mixtures of one or more fertilisers with additives not having a specially fertilising activity
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05BPHOSPHATIC FERTILISERS
    • C05B7/00Fertilisers based essentially on alkali or ammonium orthophosphates
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05GMIXTURES 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
    • C05G3/00Mixtures of one or more fertilisers with additives not having a specially fertilising activity
    • C05G3/40Mixtures of one or more fertilisers with additives not having a specially fertilising activity for affecting fertiliser dosage or release rate; for affecting solubility
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05GMIXTURES 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
    • C05G5/00Fertilisers characterised by their form
    • C05G5/10Solid or semi-solid fertilisers, e.g. powders
    • C05G5/12Granules or flakes

Abstract

The invention discloses a compound active slow-release organic fertilizer and a preparation method thereof. The compound active slow-release organic fertilizer comprises the following components in percentage by mass: 4-6% of modified mineral soil, 8-10% of algae slurry, 4-6% of natural flocculent gel, 3-5% of fertilizer efficiency polymer, 1-3% of active buffering agent and 70-80% of water. The invention compounds the algae slurry with remarkable fertilizer efficiency performance and the modified mineral soil with unique water absorption expansion, dispersion, suspension, adsorption and other performances, adds the natural flocculent gel, the fertilizer efficiency polymer and the active buffer agent to prepare the slow release fertilizer, can supplement nitrogen, phosphorus nutrients and organic matter nutrients for the barren soil when being applied to the barren soil, can reduce environmental pollution, reduce cost, remarkably improve crop yield and quality, and does not generate secondary pollution.

Description

Composite active slow-release organic fertilizer and preparation method thereof
Technical Field
The invention relates to the field of organic fertilizers, and in particular relates to a compound active slow-release organic fertilizer and a preparation method thereof.
Background
In recent years, in order to avoid that the fertilizer effect substances are released from the soil along with rainfall runoff and are greatly lost due to rainfall erosion, a soil improvement method adopting slow release fertilizer gradually attracts attention. The modified mineral soil is widely used as a slow/controlled release fertilizer carrier due to the special layered nano structure and the unique properties of water absorption expansion, dispersion, suspension, adsorption and the like. At present, researches on modified mineral soil as slow release fertilizer mainly focus on compounding inorganic nitrogen and phosphate fertilizer with modified mineral soil, and the slow release fertilizer prepared by compounding organic nitrogen and phosphate fertilizer with modified mineral soil has not attracted attention. In addition, in terms of soil improvement, the poor soil needs to be supplemented with organic nutrients such as humic acid as well as nitrogen and phosphorus nutrients. Therefore, the prepared composite active slow-release organic fertilizer has wide prospect in improving barren soil into nutrient soil.
Disclosure of Invention
The invention provides a compound active slow-release organic fertilizer and a preparation method thereof, aiming at solving the problem that the existing modified mineral soil compound slow-release fertilizer is lack of organic nitrogen and phosphorus, and meeting the use requirement of organic nutrition of barren soil.
In a first aspect, the invention provides a composite active slow-release organic fertilizer, which is realized by adopting the following technical scheme.
The composite active slow-release organic fertilizer comprises the following components in percentage by mass: 4-6% of modified mineral soil, 8-10% of algae slurry, 4-6% of natural flocculent gel, 3-5% of fertilizer efficiency polymer, 1-3% of active buffering agent and 70-80% of water.
Preferably, the compound active slow-release organic fertilizer comprises the following components in percentage by mass: 5% of modified mineral soil, 10% of algae slurry, 4% of natural flocculent gel, 4% of fertilizer efficiency polymer, 2% of active buffer and 75% of water.
Further, the modified mineral soil is modified natural mineral soil loaded with calcium base, sodium base or potassium base.
Further, the algae slurry is the algae liquid of the microalgae cultured in the effluent of the eutrophic river water after coagulation dephosphorization, and the nitrogen-phosphorus ratio of the effluent after coagulation dephosphorization is (40-60): 1; the nitrogen-phosphorus ratio of the effluent is preferably 50. The eutrophic river water is treated by chemical coagulation or chemical precipitation, etc. to obtain water quality suitable for the growth of non-toxic green algae and inhibit the growth of toxic Microcystis aeruginosa.
Furthermore, the preparation method of the algae slurry comprises the following steps: microalgae cells obtained by filtering eutrophic water through a 0.45-micron filter membrane are inoculated in the eutrophic river water after coagulation and dephosphorization, and the inoculation density is 1.5 multiplied by 10 6 ~2×10 6 cell/mL, the culture illumination intensity is 3500-4000 Lx, the temperature is 24-26 ℃, and the light-dark ratio is (1.0-1.5): 1; after culturing for 25-40 days, harvesting the algae liquid, and preparing the algae slurry with the water content of 80-90% through centrifugal dehydration.
Furthermore, the microalgae are nontoxic green algae capable of significantly accumulating fertilizer-like biomass, and include Chlorella (Chlorella), scenedesmus (Scenedesmus), chlorella (chlorecoccum), chlamydomonas (Chlamydomonas), and Dunaliella (Dunaliella).
Preferably, the microalgae cells are cultured in a column type microalgae incubator under the conditions of illumination intensity of 4000Lx, temperature of 25 ℃ and light-dark ratio of 1.4.
Further, the fertilizer efficiency polymer is a precipitate obtained after eutrophic river water is subjected to coagulation dephosphorization. The polymer precipitate of the eutrophic river water after coagulation and dephosphorization is rich in N, P and other nutrient elements and can be used as a fertilizer efficiency polymer for soil nutrient improvement.
Furthermore, the agent for coagulating and removing phosphorus is one or two of magnesium sulfate and ferric sulfate. If the agent is magnesium sulfate, the obtained precipitate is magnesium ammonium phosphate; if the agent is ferric sulfate, the obtained precipitate is ammoniojarosite and/or ferric phosphate.
Further, the preparation method of the natural flocculent gel comprises the following steps: the natural rotten black solid is crushed and sieved by a 60-100 mesh sieve by adopting an extraction method, an alkaline extracting solution is extracted for 6-10 h, the vibration is carried out for 6-10 h, the pH is adjusted to be 1.0-2.0, the centrifugation is carried out for 20min at 5000-8000 r/min, and the precipitate is dried at 50-70 ℃ to obtain the natural rotten black solid.
Preferably, the preparation method of the natural flocculent gel comprises the following steps: crushing the rotten black solid, sieving with a 80-mesh sieve, leaching with 0.5mol/L alkaline extract for 8h, shaking for 8h, adjusting the pH to 1.0 with 0.5mol/L hydrochloric acid, centrifuging at 6000r/min for 20min, and drying the precipitate at 60 ℃ to obtain the fertilizer.
Furthermore, the natural black rot solid is selected from one or more of peat, lignite and weathered coal.
Furthermore, the alkaline leaching liquor is selected from one or more of potassium hydroxide, magnesium hydroxide and sodium hydroxide.
Furthermore, the active buffering agent is prepared from waste crop materials, wherein the waste crop materials comprise coconut shells, chestnut shells, pine nut shells and broad bean hulls, and the active buffering agent belongs to natural biomass resource utilization.
In a second aspect, the invention provides a preparation method of a composite active slow-release organic fertilizer, which is realized by adopting the following technical scheme.
A preparation method of the composite active slow-release organic fertilizer comprises the following steps:
s1, mixing specified amount of modified mineral soil, algae slurry, natural flocculent gel, fertilizer efficiency polymer, active buffer and water;
s2, drying the uniformly mixed compound to obtain a solid substance with the water content of 10-20%;
and S3, grinding the solid into powder, granulating, introducing steam, adjusting the granulation temperature to 50-60 ℃, and preparing the solid particle composite organic fertilizer with the particle size of 2-6 mm.
Preferably, in step S2, the uniformly mixed composite is cyclone-dried to obtain a solid with a water content of 15%.
Preferably, in step S3, the mixed solid after cyclone drying is processed into homogeneous powder by a grinder, and then the homogeneous powder is put into a drum granulator for granulation, steam is introduced, the granulation temperature is adjusted to 60 ℃, and the solid particle composite organic fertilizer with the particle size of 5mm is prepared by the granulator.
The present application has the following advantageous effects.
In the composite active slow-release organic fertilizer provided by the invention, microalgae is cultured by using effluent obtained after eutrophic river water is subjected to coagulation and dephosphorization, and the effluent can inhibit the growth of toxic green algae such as microcystis aeruginosa and the like after the nitrogen-phosphorus ratio is adjusted, so that the growth of the nontoxic green algae is promoted, and the microalgae can obviously accumulate fertilizer-effect biomass such as protein, polysaccharide, carotenoid and the like. The polymer precipitate left after the eutrophic river water is subjected to coagulating sedimentation nitrogen and phosphorus removal is rich in N, P and other nutrient elements, and can provide organic nutrition for the barren soil. The natural active buffer agent is rich in crude fiber, has a good pore structure, strong water retention capacity and strong buffer effect, and is a strong degradable active matrix. Meanwhile, the natural flocculent gel prepared by the humins can be used as a slow release agent and a stabilizing agent of a nitrogen fertilizer, a synergist of a phosphate fertilizer, a protective agent of a potassium fertilizer, and more importantly, as a regulator and a chelating agent of trace elements, so that the soil can tightly adsorb nutrient substances. Therefore, the algae slurry with obvious fertilizer efficiency performance is compounded with the modified mineral soil with unique water absorption expansion, dispersion, suspension, adsorption and other performances, and the natural flocculent gel, the fertilizer efficiency polymer and the active buffering agent are added to prepare the slow release fertilizer for improving the nutrition of the barren soil, so that the slow release fertilizer can supplement nitrogen, phosphorus nutrients and organic matter nutrition for the barren soil, and has the advantages of reducing environmental pollution, reducing cost, prolonging the release period, obviously improving the yield and quality of crops and the like.
The compound active slow-release organic fertilizer can be directly scattered into soil to be doped for improving the soil fertility, or the organic fertilizer is dissolved in water and sprayed to the roots of crops to promote the growth of the crops. When the organic fertilizer is used, no peculiar smell is diffused, and the contained substances have no organic toxicity, so that the organic fertilizer cannot cause harm to workers in the using process, and cannot cause secondary pollution to the environmental air and water.
Detailed Description
The present patent application is further illustrated below with reference to the following examples.
Example 1
And carrying out coagulation treatment on the eutrophic river water by taking magnesium sulfate as a coagulant, wherein the adding concentration of the magnesium sulfate is 5mg/L, so that the total nitrogen concentration and the total phosphorus concentration of the treated water are respectively 10.0mg/L and 0.2mg/L to meet the nitrogen-phosphorus ratio of 50. And filtering and cleaning precipitates in the treatment process, and drying at 60 ℃ to obtain the fertilizer efficiency polymer magnesium ammonium phosphate.
And (2) inoculating microalgae cells obtained by filtering the eutrophic river water through a 0.45-micron filter membrane into a column type microalgae incubator, wherein the culture solution is the eutrophic river water effluent water of which the nitrogen-phosphorus ratio is adjusted to be 50 by coagulating sedimentation. Initial inoculum density was 2X 10 6 cell/mL (0.05 g/L), and the culture conditions are illumination intensity 4000Lx, temperature 25 ℃, light-dark ratio 1.4. After culturing for 30 days, harvesting algae liquid, and centrifugally dewatering to prepare algae slurry with water content of 90%.
Crushing and sieving natural mineral soil (B802109 from Shanghai Bai Ka chemical technology Co., ltd.), sieving at 27 deg.C, sieving with 100 mesh bentonite, and adding 0.05mol/L Na 2 CO 3 And carrying out sodium treatment by shaking for 24 h. Centrifuging after 24h to obtain oreAnd (5) producing soil slurry, and drying to obtain the sodium-based modified mineral soil.
Crushing the solid matters of the black rot, sieving the solid matters with a sieve of 80 meshes, leaching 0.5mol/L alkaline extract for 8h, shaking for 8h, adjusting the pH value to 1.0 by 0.5mol/L hydrochloric acid, centrifuging at 6000r/min for 20min, and drying the precipitate at 60 ℃ to obtain the natural flocculent gel.
Coconut shells of waste crops (purchased from special coconut chaff factories in Hainan), chestnut shells (purchased from Jindi chestnut food Co., ltd. In Qianxi county), pine cone shells (purchased from Hepan tobacco handicraft article commercial company in Guangzhou) and broad bean shells (Heiviteng feed trade Co., ltd. In Anhui) are mixed and crushed to prepare the active buffering agent with the thickness of 8 mm.
Uniformly mixing 5% of modified mineral soil, 10% of nontoxic green algae slurry, 4% of natural flocculent gel, 4% of fertilizer efficiency polymer, 2% of active buffer and 75% of water, and performing cyclone drying to obtain a solid substance with the water content of 15%; and (3) after cyclone drying, processing the mixture into homogeneous powder by a grinder, then entering a rotary drum granulator for granulation, introducing steam, adjusting the granulation temperature to 60 ℃, and preparing the solid particle composite active slow-release organic fertilizer A with the particle size of 5mm by the granulator.
And uniformly mixing 10% of modified mineral soil, 15% of nontoxic green algae slurry and 75% of water, and preparing the organic fertilizer B with the particle size of 5mm by the same preparation process of the active slow-release organic fertilizer A.
The purchasing component is nutrient soil C (purchased from Bonney biotechnology limited of Fuyang city) of humus soil, coconut husk and perlite.
And excavating the common soil D outdoors.
The specific application method is as follows:
and (3) adding an organic fertilizer A, B into the common soil D, and uniformly mixing, wherein the organic fertilizer is 30% of the dry weight of the soil. The mixed components are respectively put into polyethylene plastic basins K1 and K2. The polyethylene plastic pot K3 is filled with nutrient soil C, and the polyethylene plastic pot K4 is filled with common soil D. The seeding rate of the lettuce in each polyethylene plastic pot is 100 grains per pot, and each treatment group repeats the experiment for 3 times. Water is supplied in time during the planting period so as to ensure the water required by the growth of the plants. And measuring the seedling height of the lettuce plant sample by adopting a steel rule with the accuracy of 1mm at the 50 th day, and measuring the fresh weight of the plant by using an electronic balance. The culture results are shown in Table 1.
TABLE 1 Effect of active slow-release organic fertilizer applied to soil on growth of clover and ryegrass plants
Figure BDA0003856673630000051
The result shows that the composite active slow-release organic fertilizer A and the organic fertilizer B can obviously promote the increase of the plant height and the biomass of the lettuce, the K1 group is improved by 40 percent compared with the blank group K4, and the soil fertility is superior to that of common nutrient soil and common soil after the organic fertilizer is added. The K1 group and the K2 group are compared to find that the lettuce plant height and biomass of the K1 group are obviously superior to those of the K2 group, and the organic fertilizer A added with organic nutrient components such as natural flocculent gel, fertilizer efficiency polymers, active buffering agents and the like can enable the soil to have higher water retention capacity, buffering capacity and adsorption capacity, can obviously improve the soil nutrient condition and promote the growth of crops.
Example 2
In this embodiment, the solid particle composite active slow-release organic fertilizer a prepared in example 1 is applied by the following method:
the composite slow-release organic fertilizer is soaked and dissolved by tap water, the proportion of the organic fertilizer to the water is 1:2, equal-diameter filter paper is placed in a 9cm culture dish to serve as a germination bed, 10mL of organic fertilizer dissolving liquid is added, and the organic fertilizer dissolving liquid is added along the wall so as to avoid bubbles generated below the filter paper. Tap water was used as a blank. Uniformly and tidily arranging 50 clover seeds and 50 ryegrass seeds on a germination bed by using tweezers, covering a culture dish cover, placing the germination bed cover in a constant-temperature incubator at 25 ℃ for culture, and regularly observing during culture to replenish water timely. And (3) determining the germination potential and the germination rate according to different plant species, namely testing the germination potential and the germination rate of the clover for 3 days and 5 days and the ryegrass for 5 days and 7 days respectively, and testing the total bud length of the clover for 7 days and the ryegrass for 10 days. Abnormal or infected seeds are removed in time during the cultivation. The culture results are shown in Table 2.
TABLE 2 promoting effect of active slow-release organic fertilizer dissolved in water on germination rate of clover and ryegrass
Figure BDA0003856673630000052
Figure BDA0003856673630000061
The germination rate of clover on the 5 th day of the test group is 83 +/-6%, and the germination rate of ryegrass on the 7 th day of the test group is 95 +/-6%, which is 15-30% higher than that of the blank group. The experimental result shows that the fertilizer efficiency of the compound active slow-release organic fertilizer has obvious enhancement effect on seed germination and growth.
Example 3
Carrying out coagulation treatment on eutrophic river water by taking ferric sulfate as a coagulant, and adding the ferric sulfate with the concentration of 8mg/L to ensure that the total nitrogen concentration and the total phosphorus concentration of the treated water are respectively 10.0mg/L and 0.2mg/L so as to meet the nitrogen-phosphorus ratio of 50. And simultaneously filtering and cleaning precipitates in the treatment process, and drying at 60 ℃ to obtain the fertilizer efficiency polymer iron phosphate. And (2) inoculating microalgae cells obtained by filtering eutrophic water through a 0.45-micron filter membrane into a column type microalgae incubator, wherein the culture solution is eutrophic river water with the nitrogen-phosphorus ratio adjusted to 50 by coagulating sedimentation. Initial inoculum density was 2X 10 6 cell/mL (0.05 g/L), and the culture conditions are 3500Lx of illumination intensity, 25 ℃ of temperature and 1.5 of light-dark ratio. After culturing for 30 days, harvesting algae liquid, and centrifugally dewatering to prepare algae slurry with water content of 90%.
4 percent of modified mineral soil (the preparation method is the same as that of the example 1), 10 percent of nontoxic green algae slurry, 3 percent of natural flocculent gel (the preparation method is the same as that of the example 1), 5 percent of fertilizer efficiency polymer, 3 percent of active buffer (the preparation method is the same as that of the example 1) and 75 percent of water are mixed evenly. The uniformly mixed compound is dried by cyclone to obtain a solid with the water content of 10 percent. After cyclone drying, processing the mixture into homogeneous powder by a grinder, then entering a rotary drum granulator for granulation, introducing steam, adjusting the granulation temperature to 60 ℃, and preparing the solid particle composite organic fertilizer with the particle size of 5mm by the granulator.
The specific application method is as follows:
setting the application proportion of the organic fertilizer to the dry weight of soil to be 0% (CK), 10% (S10), 20% (S20) and 30% (S30), and respectively filling the mixed groups into polyethylene plastic basins. The seeding rate of ryegrass and clover is 100 grains per pot, and each treatment group repeats the experiment for 3 times. Water is supplied in time during the planting period so as to ensure the water required by the growth of the plants. The height of seedlings of clover and ryegrass plant samples was measured on day 50 using a steel ruler with an accuracy of 1mm, and the fresh weight of the plants was determined using an electronic balance. The culture results are shown in Table 3.
TABLE 3 Effect of active slow-release organic fertilizer applied to soil on growth of clover and ryegrass plants
Figure BDA0003856673630000062
Figure BDA0003856673630000071
Experimental results show that when the fertilizing amount of the compound active slow-release organic fertilizer is 10% -30%, the increase of the plant height and biomass of ryegrass and clover is obviously promoted, particularly 30%, and the compound active slow-release organic fertilizer obviously improves the soil nutrient condition to promote the growth of crops.
The embodiments of the present invention are preferred embodiments of the present invention, and the scope of the present invention is not limited by these embodiments, so: all equivalent changes made according to the structure, shape and principle of the invention are covered by the protection scope of the invention.

Claims (10)

1. A composite active slow-release organic fertilizer is characterized in that: the paint comprises the following components in percentage by mass: 4-6% of modified mineral soil, 8-10% of algae slurry, 4-6% of natural flocculent gel, 3-5% of fertilizer efficiency polymer, 1-3% of active buffer and 70-80% of water.
2. The compound active slow-release organic fertilizer as claimed in claim 1, which is characterized in that: the modified mineral soil is modified natural mineral soil loaded with calcium base, sodium base or potassium base.
3. The compound active slow-release organic fertilizer as claimed in claim 1, which is characterized in that: the algae slurry is the algae liquid of the microalgae cultured in the effluent of eutrophic river water after coagulation dephosphorization, and the nitrogen-phosphorus ratio of the effluent after coagulation dephosphorization is (40-60): 1.
4. The compound active slow-release organic fertilizer as claimed in claim 3, which is characterized in that: the preparation method of the algae slurry comprises the following steps: microalgae cells obtained by filtering eutrophic water through a 0.45-micron filter membrane are inoculated in the eutrophic river water after coagulation and dephosphorization, and the inoculation density is 1.5 multiplied by 10 6 ~2×10 6 cell/mL, the culture illumination intensity is 3500-4000 Lx, the temperature is 24-26 ℃, and the light-dark ratio is (1.0-1.5): 1; after culturing for 25-40 days, harvesting the algae liquid, and preparing the algae slurry with the water content of 80-90% through centrifugal dehydration.
5. The compound active slow-release organic fertilizer as claimed in claim 1, which is characterized in that: the fertilizer efficiency polymer is a precipitate obtained after eutrophic river water is subjected to coagulation dephosphorization.
6. The compound active slow-release organic fertilizer as claimed in any one of claims 3-5, wherein: the agent for coagulating and removing phosphorus is one or two of magnesium sulfate and ferric sulfate.
7. The compound active slow-release organic fertilizer as claimed in claim 1, which is characterized in that: the preparation method of the natural flocculent gel comprises the following steps: crushing the natural rotten black solid, sieving the crushed natural rotten black solid with a 60-100-mesh sieve, leaching an alkaline extracting solution for 6-10 h, shaking the alkaline extracting solution for 6-10 h, adjusting the pH value to 1.0-2.0, centrifuging the alkaline extracting solution for 20min at 5000-8000 r/min, and drying the precipitate at 50-70 ℃ to obtain the natural rotten black solid.
8. The compound active slow-release organic fertilizer as claimed in claim 7, which is characterized in that: the natural black rot solid is one or more of peat, lignite and weathered coal.
9. The compound active slow-release organic fertilizer as claimed in claim 1, which is characterized in that: the active buffering agent is prepared from waste crop materials including coconut shell, chestnut shell, pine nut shell and broad bean hull.
10. A method for preparing the compound active slow-release organic fertilizer as defined in any one of claims 1-9, which is characterized in that: the method comprises the following steps:
s1, mixing specified amount of modified mineral soil, algae slurry, natural flocculent gel, fertilizer efficiency polymer, active buffer and water;
s2, drying the uniformly mixed compound to obtain a solid substance with the water content of 10-20%;
and S3, grinding the solid into powder, granulating, introducing steam, adjusting the granulation temperature to 50-60 ℃, and preparing the solid particle composite organic fertilizer with the particle size of 2-6 mm.
CN202211151590.9A 2022-09-21 2022-09-21 Composite active slow-release organic fertilizer and preparation method thereof Active CN115417724B (en)

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Publication number Priority date Publication date Assignee Title
CN105886404A (en) * 2016-06-14 2016-08-24 华东理工大学 Polyculture type microalgae cultivation method capable of inhibiting growth of microcystis aeruginosa
CN108409465A (en) * 2018-05-30 2018-08-17 景德镇陶瓷大学 A kind of ammonium magnesium phosphate-phosphorus fertilizer slow release fertilizer and preparation method thereof
CN111094541A (en) * 2017-07-15 2020-05-01 阿鲁恩·维塔尔·沙旺特 Novel crop fortification, crop nutrition and crop protection compositions

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Publication number Priority date Publication date Assignee Title
CN105886404A (en) * 2016-06-14 2016-08-24 华东理工大学 Polyculture type microalgae cultivation method capable of inhibiting growth of microcystis aeruginosa
CN111094541A (en) * 2017-07-15 2020-05-01 阿鲁恩·维塔尔·沙旺特 Novel crop fortification, crop nutrition and crop protection compositions
CN108409465A (en) * 2018-05-30 2018-08-17 景德镇陶瓷大学 A kind of ammonium magnesium phosphate-phosphorus fertilizer slow release fertilizer and preparation method thereof

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* Cited by examiner, † Cited by third party
Title
黄占斌: "《环境材料学》", vol. 1, 冶金工业出版社, pages: 163 - 170 *

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