WO2018082266A1 - Water-soluble nano-organic carbon fertilizer and preparation method therefor, and organic compound fertilizer - Google Patents

Water-soluble nano-organic carbon fertilizer and preparation method therefor, and organic compound fertilizer Download PDF

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Publication number
WO2018082266A1
WO2018082266A1 PCT/CN2017/080940 CN2017080940W WO2018082266A1 WO 2018082266 A1 WO2018082266 A1 WO 2018082266A1 CN 2017080940 W CN2017080940 W CN 2017080940W WO 2018082266 A1 WO2018082266 A1 WO 2018082266A1
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Prior art keywords
water
extraction
organic
nano
organic waste
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PCT/CN2017/080940
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French (fr)
Chinese (zh)
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曾济天
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曾济天
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    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F5/00Fertilisers from distillery wastes, molasses, vinasses, sugar plant or similar wastes or residues, e.g. from waste originating from industrial processing of raw material of agricultural origin or derived products thereof
    • 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
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/50Improvements relating to the production of bulk chemicals
    • Y02P20/54Improvements relating to the production of bulk chemicals using solvents, e.g. supercritical solvents or ionic liquids

Definitions

  • the invention relates to the field of environmental protection and agricultural special fertilizer technology, in particular to a water-soluble nano organic carbon fertilizer, a preparation method thereof and an organic compound fertilizer.
  • the treatment methods for organic waste include the following: direct agricultural, compost (including bio-humic acid BFA compost), landfill, biogas fermentation and incineration.
  • direct agricultural including bio-humic acid BFA compost
  • landfill including bio-humic acid BFA compost
  • biogas fermentation including biogas fermentation and incineration.
  • various processing methods have their own drawbacks and weaknesses.
  • the method of composting covers a large area, labor, time-consuming, low processing efficiency, unstable product quality, low commodity value, and the same amount of farmer's fertilizer, and farmers are not willing to use it in large quantities. Sales are difficult. Pollution problems such as harmful gases are also generated during the production process. Landfill is a common method for urban domestic garbage disposal. It accounts for more than 80% of the amount of garbage disposal in China. It not only fails to use resources reasonably, but also occupies a large amount of land, and is prone to secondary pollution such as leachate and methane gas.
  • One of the objects of the present invention is to provide a method for preparing a water-soluble nano-organic carbon fertilizer, which solves the problems in the prior art that the treatment of organic waste occupies a large area, consumes high energy, is expensive, has complicated processes, and even causes The problem of secondary pollution.
  • the method for preparing water-soluble nano organic carbon fertilizer by using organic waste has the advantages of small land occupation, low labor consumption, low energy consumption, high efficiency, low cost, simple process and suitable for industrial production. Moreover, the method does not require excessive raw materials, and can treat all industrial and agricultural organic wastes to make them all water-soluble nano organic carbon fertilizers.
  • the treatment method provided by the invention completely treats the organic waste, has no residue, no secondary pollution, and can completely convert and utilize the organic waste.
  • Another object of the present invention is to provide a water-soluble nano organic carbon fertilizer prepared by the method for preparing a water-soluble nano organic carbon fertilizer, wherein the water-soluble nano organic carbon fertilizer can also be added with a chemical fertilizer to produce a whole nutrient solution.
  • Sexual nano-organic carbon fertilizer and also contains a large number of beneficial microorganisms, with the advantages of comprehensive balance of fertilizer efficiency.
  • Another object of the present invention is to provide an organic compound fertilizer which has good fertilizer efficiency, is easy to degrade, and is environmentally friendly.
  • a method for preparing a water-soluble nano organic carbon fertilizer comprising the following steps:
  • the bio-dynamic regulator is added to the organic waste to remove the odor by the biological enzyme, and then pulverized, pulverized, and then water is added for refining.
  • the chemical waste cracking agent is added to the organic waste slurry, and the homogeneous emulsification treatment is performed. And then performing a nano-extraction treatment, and then concentrating and drying to obtain the liquid or solid water-soluble nano organic carbon fertilizer;
  • the biodynamic regulator comprises a combination of one or more of Bacillus subtilis, Bacillus licheniformis, yeast, photosynthetic bacteria, cellulase, glucanase and xylanase;
  • the chemical catalytic cracking agent comprises one or a combination of a hydroxide and a peroxide
  • the hydroxide comprises one or a combination of ammonium hydroxide, potassium hydroxide, sodium hydroxide, calcium hydroxide and magnesium hydroxide, the peroxide comprising potassium persulfate or One or two of ammonium sulfate.
  • the proportion of carbon-containing particles having a particle diameter of less than 1000 nm in the solution is greater than 95%.
  • the method for preparing water-soluble nano-organic carbon fertilizer by using organic waste firstly comprises a large amount of biodynamic regulators, and the biodynamic regulator is composed of high-activity composite probiotics and complex enzymes, through the action of probiotics and enzymes. Can effectively eliminate the odor of organic waste.
  • the biodynamic regulator is preferably composed of Bacillus subtilis, Bacillus licheniformis, yeast, photosynthetic bacteria, cellulase, glucanase and xylanase, but may depend on the specific composition of the organic waste, and may be The combination of one or more of the above enzymes and bacteria may also contain enzymes or bacteria other than the microorganisms listed above.
  • the deodorized organic waste is pulverized and refined, and then pulverized and then chemically oxidized by adding a chemical material having strong oxidizing property.
  • the liquid or solid water-soluble nano organic carbon fertilizer is obtained by homogeneous emulsification, nano-extraction, concentration and drying. Concentration is carried out using a low-temperature vacuum concentrating device to make the water content less than 50%, and a liquid water-soluble nano organic carbon fertilizer is obtained. Further, the low-temperature vacuum drying operation is performed, so that the water-soluble nano-organic carbon fertilizer has a water content of less than 10%, and a solid water-soluble nano organic carbon fertilizer is obtained.
  • the method combines the methods of biological enzymatic hydrolysis and chemical degradation, and combines homogeneous emulsification and nano-extraction technology, is a low-cost, high-efficiency, rapid and simple method for producing water-soluble nano-organic carbon fertilizer by using organic waste.
  • the organic waste comprises: industrial organic waste water, agricultural organic waste and urban domestic waste.
  • Industrial organic wastewater includes: molasses liquid, yeast liquid, and sperm liquid.
  • Agricultural organic waste includes: livestock and poultry manure, biogas slurry, crop straw, sawdust, vegetable and fruit residues, distiller's cake, mushroom residue and sputum.
  • Urban domestic garbage includes: kitchen waste and urban sewage sludge.
  • the method before adding the biodynamic regulator to the organic waste, the method further comprises the steps of: removing the inorganic solids and plastics contained in the organic waste.
  • inorganic solids include metals, glass, batteries, ceramics, and stones.
  • the pulverizing process specifically comprises the steps of: pulverizing the organic waste deodorized by the biological enzyme to particles having a particle diameter of less than 5 mm;
  • the particles have a particle size of less than 3 mm;
  • the pulverization is carried out using a wet pulverizer.
  • the pulverized particles facilitate the refining of water.
  • the process of adding water to refine specifically comprising the steps of: adding 1 to 2 times the mass of water to the pulverized organic waste, and refining until the obtained slurry has a particle diameter of less than 10 micrometers. a more preferred slurry having a particle size of less than 5 microns;
  • the refining is operated by a colloid mill or a cone mill.
  • Adding water refining further reduces the particle size of the organic waste raw material, and helps to improve the water solubility of the organic carbon fertilizer.
  • the mass ratio of the chemical catalytic cracking agent to the slurry is (1 to 2): 100.
  • the method further comprises: adding a fertilizer.
  • the nano-extraction comprises: one or a combination of supercritical extraction, microwave extraction, ultrasonic extraction, ultra-high pressure extraction and nano-abrasive extraction;
  • the solvent for the nano-extraction is an inorganic solvent, and the number of extractions is 1 to 2 times. Further preferably, the solvent is water or carbon dioxide.
  • Nano-extraction is beneficial to fully extract water-soluble components, improve the utilization of organic waste, and maximize the utilization of organic waste.
  • the supercritical extraction has a pressure of 25 to 80 MPa, a power of 5 to 25 KW, a temperature of 45 to 80 ° C, a liquid flow rate of 1000 to 2000 L/h, and an extraction time of 45 to 60 min;
  • the frequency of the microwave extraction is 300-915 MHz
  • the power is 5-25 KW
  • the temperature is 35-80 ° C
  • the volume of the reaction tank is 1000-3000 L or the liquid flow rate is 1000-3000 L/h
  • the extraction time is 45-60 min;
  • the ultrasonic extraction frequency is 20 to 50 KHz
  • the power is 5 to 25 KW
  • the temperature is 30 to 60 ° C
  • the reaction tank volume is 1000 to 3000 L or the liquid flow rate is 1000 to 3000 L/h
  • the extraction time is 45 to 60 min;
  • the ultrahigh pressure extraction has a pressure of 250 to 380 MPa, a power of 5 to 25 KW, a temperature of 30 to 60 ° C, a liquid flow rate of 1000 to 2000 L/h, and an overpressure time of 2 to 5 min.
  • the nano-grinding extraction pressure is 50-80 MPa
  • the power is 5-25 KW
  • the temperature is 30-60 ° C
  • the reaction tank volume is 100-500 L or the liquid flow rate is 1000-5000 L/h
  • the overpressure time is 2 ⁇ 5min.
  • one of supercritical extraction, microwave extraction, ultrasonic extraction, ultra-high pressure extraction, nano-abrasive extraction, or repeated multiple extraction by the same means, or a combination of several means may be employed.
  • ultra-high pressure extraction for 2 to 5 minutes it is again extracted by ultra-high pressure for 2 to 5 minutes
  • nano-grinding extraction for 2 to 5 minutes it is again extracted by nano-milling for 2 to 5 minutes
  • ultrasonic extraction is carried out for 10 to 5 minutes.
  • the nano-abrasive extraction is carried out for 2 to 5 minutes.
  • the parameters such as the frequency, power, and temperature of the extraction are the same as those defined above.
  • the water-soluble nano organic carbon fertilizer prepared by the method for preparing a water-soluble nano organic carbon fertilizer as described above.
  • particles having a particle diameter of less than 800 nm of carbon-containing particles reach 99% or more.
  • the method for preparing a water-soluble nano organic carbon fertilizer by using organic waste has a particle size of generally less than 600-800 nm.
  • the proportion of carbonaceous particles having a particle diameter of less than 800 nm can reach 99% or more.
  • the organic matter of plants is essentially carbon, but the elemental carbon is insoluble in water and cannot be absorbed.
  • the water-soluble nano-organic carbon fertilizer provided in this application has an effective carbon molecular particle size of less than 800 nm and excellent water solubility. Plant roots and soil Microorganisms are directly absorbed and utilized. At present, the use of organic carbon fertilizer alone cannot achieve the desired effect. Therefore, the present application also adds a fertilizer based on the water-soluble nano organic carbon fertilizer.
  • Fertilizer is also called inorganic fertilizer, including nitrogen fertilizer, phosphate fertilizer, potassium fertilizer, medium and trace element fertilizer, compound fertilizer and so on. Fertilizer generally does not contain organic matter, and does not have the effect of improving soil and fertilization. It can be used with organic carbon fertilizer, and it can improve the fertilizer efficiency with half the effort.
  • a water-soluble nano organic carbon fertilizer prepared by the above preparation method.
  • An organic compound fertilizer comprising water-soluble nano organic carbon fertilizer and inorganic fertilizer, and the water-soluble nano organic carbon fertilizer is prepared by the following steps: preparing organic waste after bio-enzyme deodorization by biodynamic regulator Waste slurry; adding chemical catalytic cracking agent to organic waste slurry; homogenizing emulsification treatment of organic waste slurry; performing nano-extraction treatment on organic waste slurry; and concentrating and drying.
  • chemical fertilizers are also called inorganic fertilizers, including nitrogen fertilizers, phosphate fertilizers, potassium fertilizers, medium and trace element fertilizers, compound fertilizers, etc.
  • the above biodynamic regulator comprises a combination of one or more of Bacillus subtilis, Bacillus licheniformis, yeast, photosynthetic bacteria, cellulase, glucanase and xylanase.
  • the mass ratio of the above chemical catalytic cracking agent to the slurry is (1 to 2): 100, and the chemical catalytic cracking agent comprises one or a combination of two of a hydroxide and a peroxide.
  • the above hydroxide comprises one or a combination of ammonium hydroxide, potassium hydroxide, sodium hydroxide, calcium hydroxide and magnesium hydroxide.
  • the above peroxide comprises one or both of potassium persulfate and ammonium persulfate.
  • the preparation of the above organic waste slurry comprises: removing inorganic solids and plastics contained in the organic waste before adding the biodynamic regulator to the organic waste; pulverizing the organic waste after the biological enzyme is deodorized to the particle size Particles of less than 5 mm; and the pulverized organic waste is added to water having a mass of 1-2 times, and is ground to a particle size of the obtained slurry of less than 10 ⁇ m.
  • the above nano-extraction comprises one or a combination of supercritical extraction, microwave extraction, ultrasonic extraction, ultrahigh pressure extraction and nano-abrasive extraction.
  • the above-mentioned solvent for nano-extraction is an inorganic solvent.
  • particles having a particle diameter of less than 800 nm of carbon-containing particles reach 99% or more.
  • the beneficial effects of the present invention include at least:
  • the preparation method of a water-soluble nano organic carbon fertilizer provided by the present application uses organic waste as a raw material, has small land occupation, low labor consumption, low energy consumption, high efficiency, low cost, simple process, and is suitable for industrial production. Etc.
  • the preparation method of the water-soluble nano organic carbon fertilizer provided by the application can effectively and thoroughly treat the organic waste, improve the utilization rate of the organic waste, has no residue in the treatment process, and has no secondary pollution, and is highly efficient. An environmentally friendly method that thoroughly utilizes organic waste.
  • the water-soluble nano organic carbon fertilizer prepared by the method for preparing a water-soluble nano organic carbon fertilizer provided by the present application can also be added with chemical fertilizer to produce a nutrient-soluble nano-organic carbon fertilizer, and also contains a large amount of Beneficial microorganisms have the advantages of comprehensive balance of fertilizer efficiency.
  • the water-soluble nano organic carbon fertilizer prepared by the method for preparing a water-soluble nano organic carbon fertilizer provided by the present application the particle size of the carbonaceous particles having a particle diameter of less than 800 nm is over 99%, and the water solubility is excellent. It can be directly absorbed and utilized by plant roots and soil microorganisms.
  • a biodynamic regulator consisting of photosynthetic bacteria, cellulase, glucanase, and xylanase is deactivated by a biological enzyme, and then pulverized into particles of 3 mm or less by a wet pulverizer. After pulverization, water was added in a ratio of dry to wet ratio of 1:1, and then ground to a slurry of 5 ⁇ m or less by a colloid mill.
  • waste metal, waste plastics, waste glass, waste batteries, ceramic stones, etc. in organic waste, and spray them on Bacillus subtilis, Bacillus licheniformis, yeast, etc. after sorting and removing impurities.
  • the biodynamic regulator consisting of photosynthetic bacteria, cellulase, glucanase and xylanase carries out bio-enzyme deodorization.
  • the organic waste which has been deodorized by sorting the detoxification enzyme is pulverized into particles of 5 mm or less by a wet pulverizer.
  • pulverized organic waste water is added in a ratio of dry to wet ratio of 1..1, and then ground to a slurry of 10 ⁇ m or less by a colloid mill or a cone mill. 2% by weight of potassium hydroxide and 1% by weight of ammonium persulfate were added to the organic waste slurry after water refining, and the mixture was homogenized and emulsified by chemical cracking in a reaction tank by a homogenizer. Adding large and medium trace elements such as NPK, silicocalcium and magnesium to homogenize emulsification again.
  • the homogeneous mixture after emulsification is extracted by ultrasonic extraction equipment, and the proportion of carbonaceous particles having a particle diameter of less than 1000 nm in the solution is greater than 95%, the frequency of ultrasonic extraction is 20 KHz, and the power is 5 KW.
  • the temperature was 30 ° C and the extraction time was 60 min. Then, it is concentrated under low temperature vacuum to control the water content to below 50%. Finally, it is filled by a liquid quantitative filling machine to obtain the liquid water-soluble nano organic carbon fertilizer.
  • nano-abrasive extraction is then carried out so that the proportion of carbonaceous particles having a particle size of less than 1000 nm in the solution is greater than 95%.
  • the pressure of nano-grinding is 50MPa, power 5KW, temperature 30 ° C, liquid flow rate 1000L / h, overpressure time 2min. Then, it is concentrated under low temperature vacuum to control the water content to less than 50%, and then the water content is reduced to less than 10% by vacuum drying, and finally packaged by a solid powder quantitative packaging machine to obtain the solid powdery water-soluble nano organic Carbon fertilizer.
  • This embodiment is basically the same as Embodiment 1, and the main difference is that the process parameters of supercritical extraction are different.
  • a biodynamic regulator consisting of photosynthetic bacteria, cellulase, glucanase, and xylanase is deactivated by a biological enzyme, and then pulverized into particles of 3 mm or less by a wet pulverizer. After pulverization, water was added in a ratio of dry to wet ratio of 1:1, and then ground to a slurry of 5 ⁇ m or less by a colloid mill.
  • This embodiment is basically the same as Embodiment 1, and the main difference is that the process parameters of supercritical extraction are different.
  • This embodiment is basically the same as Embodiment 2, and the main difference is that the process parameters of the ultrahigh pressure extraction are different.
  • This embodiment is basically the same as Embodiment 2, and the main difference is that the process parameters of the ultrahigh pressure extraction are different.
  • the enzyme is used to deodorize the enzyme. After deodorization, it was pulverized into particles of 5 mm or less by a wet pulverizer. After pulverization, water is added in a ratio of dry to wet ratio of 1..2, and then ground to a slurry of 10 ⁇ m or less by a colloid mill or a cone mill.
  • This embodiment is basically the same as Embodiment 3, and the main difference is that the process parameters of microwave extraction are different.
  • This embodiment is basically the same as Embodiment 3, and the main difference is that the process parameters of microwave extraction are different.
  • Scrap metal, waste plastics, waste glass, waste batteries, ceramic stones, etc. in organic waste, and then sprayed by Bacillus subtilis, Bacillus licheniformis, yeast, photosynthetic bacteria, cellulase and A biodynamic regulator consisting of a glucanase is used to deodorize the enzyme. After deodorization, it was pulverized into particles of 5 mm or less by a wet pulverizer. After pulverization, water is added in a ratio of dry to wet ratio of 1..1, and then ground to a slurry of 10 ⁇ m or less by a colloid mill or a cone mill.
  • This embodiment is basically the same as Embodiment 4, and the main difference is that the process parameters of ultrasonic extraction are different.
  • waste metal, waste plastics, waste glass, waste batteries, ceramic stones, etc. in organic waste, and spray them on Bacillus subtilis, Bacillus licheniformis, yeast, etc. after sorting and removing impurities.
  • the biodynamic regulator consisting of photosynthetic bacteria, cellulase, glucanase and xylanase carries out bio-enzyme deodorization.
  • the organic waste which has been deodorized by sorting the detoxification enzyme is pulverized into particles of 5 mm or less by a wet pulverizer.
  • pulverized organic waste water is added in a ratio of dry to wet ratio of 1..1, and then ground to a slurry of 10 ⁇ m or less by a colloid mill or a cone mill. 2% by weight of potassium hydroxide and 1% by weight of ammonium persulfate were added to the organic waste slurry after water refining, and the mixture was homogenized and emulsified by chemical cracking in a reaction tank by a homogenizer. Adding large and medium trace elements such as NPK, silicocalcium and magnesium to homogenize emulsification again.
  • the homogeneous mixture after emulsification is extracted by an ultrasonic extraction device, and the proportion of carbonaceous particles having a particle diameter of less than 1000 nm in the solution is greater than 95%, and the frequency of ultrasonic extraction is 50 kHz, and the power is 25 KW, temperature is 60 ° C, extraction time is 60 min. Then, it is concentrated under low temperature vacuum to control the water content to below 50%. Finally, it is filled by a liquid quantitative filling machine to obtain the liquid water-soluble nano organic carbon fertilizer.
  • This embodiment is basically the same as Embodiment 4, and the main difference is that the process parameters of ultrasonic extraction are different.
  • Waste metal, waste plastics, waste glass, waste batteries, ceramic stones, etc. in organic waste are sorted and removed, and biodynamic regulation of Bacillus licheniformis and yeast is sprayed after sorting and removing impurities.
  • the enzyme is used to deodorize the enzyme.
  • the organic waste which has been deodorized by sorting the detoxification enzyme is pulverized into particles of 5 mm or less by a wet pulverizer.
  • water is added in a ratio of dry to wet ratio of 1..1, and then ground to a slurry of 10 ⁇ m or less by a colloid mill or a cone mill.
  • the homogeneous mixture after emulsification is extracted by an ultrasonic extraction device, and the proportion of carbonaceous particles having a particle diameter of less than 1000 nm in the solution is greater than 95%, and the frequency of ultrasonic extraction is 30 kHz, and the power is 20 KW, temperature is 45 ° C, extraction time is 60 min. Then, it is concentrated under low temperature vacuum to control the water content to below 50%. Finally, it is filled by a liquid quantitative filling machine to obtain the liquid water-soluble nano organic carbon fertilizer.
  • This embodiment is basically the same as Embodiment 5, and the main difference is that the process parameters of the nano-grinding extraction are different.
  • the nano-abrasive extraction is then carried out so that the proportion of carbonaceous particles having a particle size of less than 1000 nm in the solution is greater than 95%.
  • the nano-grinding extraction pressure is 80 MPa
  • the power is 25 KW
  • the temperature is 60 ° C
  • the liquid flow rate is 2000 L/h
  • the overpressure time is 5 min.
  • it is concentrated under low temperature vacuum to control the water content to less than 50%, and then the water content is reduced to less than 10% by vacuum drying, and finally packaged by a solid powder quantitative packaging machine to obtain the solid powdery water-soluble nano organic Carbon fertilizer.
  • This embodiment is basically the same as Embodiment 5, and the main difference is that the process parameters of the nano-grinding extraction are different.
  • the scrap metal, waste plastic, waste glass, waste battery, ceramic stone, etc. in the organic waste are sorted and removed, and then the biodynamic regulator composed of cellulase is sprayed to carry out the biological enzyme to remove the odor.
  • the biodynamic regulator composed of cellulase is sprayed to carry out the biological enzyme to remove the odor.
  • it was pulverized into particles of 5 mm or less by a wet pulverizer.
  • water is added in a ratio of dry to wet ratio of 1..2, and then ground to a slurry of 10 ⁇ m or less by a colloid mill or a cone mill.
  • the nano-abrasive extraction is then carried out so that the proportion of carbonaceous particles having a particle size of less than 1000 nm in the solution is greater than 95%.
  • the nano-abrasive extraction pressure was 70 MPa
  • the power was 15 KW
  • the temperature was 45 ° C
  • the liquid flow rate was 1600 L/h
  • the overpressure time was 3 min. Then, it is concentrated under low temperature vacuum to control the water content to less than 50%, and then the water content is reduced to less than 10% by vacuum drying, and finally packaged by a solid powder quantitative packaging machine to obtain the solid powdery water-soluble nano organic Carbon fertilizer.
  • the experimental results show that after applying the water-soluble nano-organic carbon fertilizer provided in the examples of the present invention, all the greenhouse peppers and eggplants returned to normal growth after one week, and then the vegetable vegetables grew well, the plants were neat, and the flowers were more and more.
  • the average yield per mu of pepper and eggplant is still as high as 11,000 kg. If it is not affected, the average yield of pepper and eggplant can reach about 15,000 kg.
  • the water-soluble nano-organic carbon fertilizer provided by the present invention is not used, and only the vegetable field of common organic fertilizer is used, and the yield is extremely low.
  • the water-soluble nano organic carbon fertilizer provided by the embodiments 1-5 of the invention is detected by a total organic carbon detector and a nanometer particle size detector, and the organic carbon (biohumic acid) content is between 21% and 40%, and the effective carbon is used.
  • the EC content is between 15% and 29%; the nano-particle size is more than 99% below 800 nm, 90% or less under 900 nm, 100% below 1000 nm, and more than 10% below 200 nm, accounting for less than 500 nm. above 50.
  • Example 1 and Example 6 are basically the same, except that the process parameters of the supercritical extraction are different.
  • the water-soluble nano-organic carbon fertilizer was prepared according to the same preparation method as in Example 1, except that the process parameters of the supercritical extraction were different, as shown in Table 2.
  • the present invention also verifies the effect of different process parameters on the efficiency of water-soluble nano-organic carbon fertilizer under other extraction processes. It has been found that no matter which extraction process (ie, microwave extraction, ultrasonic extraction, ultra-high pressure extraction and nano-abrasive extraction) is selected, when the corresponding process parameters are out of the scope of the present invention, the yield of the crop is inferior to the present invention.
  • extraction process ie, microwave extraction, ultrasonic extraction, ultra-high pressure extraction and nano-abrasive extraction
  • the water-soluble nano-organic carbon fertilizer has an organic carbon (biohumic acid) content of 21% to 40%, and contains a large number of beneficial microorganisms, is easily soluble in the soil and is absorbed and utilized by plants, and can promote soil agglomeration. Structure formation, improvement Soil permeability, water retention, and fertility are beneficial to the reproduction and increase of microorganisms, which enhances the ability of the soil to absorb nutrients and store nutrients. From the source, it solves the problems of frequent application of chemical fertilizers, large quantity, easy loss, and low utilization rate. Ultimately reflected in the growth, yield and quality of crops.
  • organic carbon biohumic acid
  • the water-soluble nano organic carbon fertilizer produced by the invention has the organic carbon (biohumic acid) produced by biological, chemical and physical effects, and is different from the organic carbon in the general organic fertilizer (biohumus) acid). Because the present invention has completely converted all the components of organic waste into simple, water-soluble substances, it is more easily taken up by plants.

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Pest Control & Pesticides (AREA)
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Abstract

Provided are a water-soluble nano-organic carbon fertilizer and a preparation method therefor, and an organic compound fertilizer. The method involves adding a biodynamic regulator to organic waste for biological enzymolysis and deodorization, then pulverizing same; after pulverizing, adding water for slurrying; and after slurrying, adding a chemical catalytic cracking agent to the resulting organic waste slurry, performing homogenization and emulsification treatments, then performing a nano-extraction treatment, and then concentrating and drying same to obtain the water-soluble nano-organic carbon fertilizer. The method uses organic waste as a raw material, and has the advantages of a small floor space, less labor, low energy consumption, high efficiency, low costs, being technologically simple and convenient, being suitable for industrialized production, etc., with the treatment being thorough, and free of residues and secondary pollution. If a chemical fertilizer is added, the water-soluble nano-organic carbon fertilizer can be produced as a full-nutrition water-soluble nano-organic carbon fertilizer, and has the advantages of fertilizer efficiency being balanced overall, etc., has an excellent water solubility, and can be directly and fully absorbed and utilized by plant root systems and soil microorganisms.

Description

一种水溶性纳米有机碳肥及其制备方法以及有机复合肥Water-soluble nano organic carbon fertilizer, preparation method thereof and organic compound fertilizer
相关申请的交叉引用Cross-reference to related applications
本申请要求于2016年11月04日提交中国专利局、申请号为2016109616588、名称为“一种水溶性纳米有机碳肥及其制备方法”的中国专利申请的优先权,其全部内容通过引用结合在本申请中。The present application claims priority to Chinese Patent Application No. 2016109616588, entitled "A Water-Soluble Nano-Organic Carbon Fertilizer and Its Preparation Method", filed on November 4, 2016, the entire contents of which are incorporated by reference. In this application.
技术领域Technical field
本发明涉及环境保护和农业特种肥料技术领域,具体而言,涉及一种水溶性纳米有机碳肥及其制备方法以及有机复合肥。The invention relates to the field of environmental protection and agricultural special fertilizer technology, in particular to a water-soluble nano organic carbon fertilizer, a preparation method thereof and an organic compound fertilizer.
背景技术Background technique
我国有机废弃物排放量以年均8-10%的速度逐年递增,其中工业有机废水(糖蜜液、酵母液、味精液等)的产生量约为20亿吨,农业有机废弃物(畜禽粪便、沼液沼渣、作物秸秆、锯沫木屑、蔬果残渣、酒糟饼粕、菌菇残渣、蚯蚓粪便等)的产生量约为25亿吨,城镇生活垃圾(餐厨余物、城镇粪池污泥等)的产生量约为1.9亿吨,得到处理的有机废弃物不足1/3,无害化处理率不到10%,即使得到处理的有机废弃物,仍然没有消除其对环境的负面影响。从资源学的观点看,有机废弃物也是资源,而且是当前世界上唯一不断增长的潜在资源。The discharge of organic waste in China is increasing at an annual rate of 8-10%, and the production of industrial organic wastewater (sugar liquid, yeast liquid, sperm liquid, etc.) is about 2 billion tons. Agricultural organic waste (animal waste) The production of biogas slurry, crop straw, sawdust, vegetable and fruit residues, distiller's cake, mushroom residue, sputum, etc. is about 2.5 billion tons, and urban domestic garbage (food waste, urban sewage) The production of mud, etc. is about 190 million tons, less than 1/3 of the treated organic waste, and the harmless treatment rate is less than 10%. Even if the treated organic waste is treated, the negative impact on the environment is not eliminated. . From a resource science perspective, organic waste is also a resource and is currently the only potential source of growth in the world.
目前,对于有机废弃物的处理方法,包括以下几种:直接农用、堆肥(包括生物腐植酸BFA堆肥)、填埋、沼气发酵和焚烧等方法。然而,各种处理方法都有自身的弊端和弱点。At present, the treatment methods for organic waste include the following: direct agricultural, compost (including bio-humic acid BFA compost), landfill, biogas fermentation and incineration. However, various processing methods have their own drawbacks and weaknesses.
其中,农业有机废弃物直接农用还田是我国的传统,由于劳动力成本上涨,农家肥量大体沉,人力搬运到田间施肥费时费力,除非自己吃用的粮食蔬果,农民绝不愿意大量使用农家肥,这也是化肥大量使用的重要原因,农家肥的生产没有经过合理的处理,缺少科技含量,导致大量农业有机废弃物资源浪费和产生有害气体、污染地下水源等新的污染问题。采用堆肥(包括生物腐植酸BFA堆肥)的方法占地大,费工、耗时,处理效率不高,产品质量不稳定,商品价值低,与农家肥一样量大体沉,农民不愿意大量使用,销售困难。生产过程中同样会产生有害气体等污染问题。填埋是城镇生活垃圾处理的常用方法,在我国占垃圾处理量的80%以上,不仅没能合理地利用资源,而且还占用大量的土地,容易产生渗滤液、甲烷气等二次污染。利用有机废弃物产生沼气是一项好技术,但前期的投入、操作技术和潜在隐患,技术推广和可操作性的难度均很大,还存在沼液、沼渣的二次处理问题。焚烧处理有机废弃物同样存在技术难度大和二次污染问题,不适合我国的国情。Among them, the direct agricultural use of agricultural organic waste is a tradition in China. Due to the rising labor costs, the amount of farmyard fertilizer is generally heavy, and manpower is transferred to the field to fertilize time and effort. Unless they eat the fruits and vegetables themselves, farmers are not willing to use farmyard manure extensively. This is also an important reason for the large-scale use of chemical fertilizers. The production of farmyard manure has not been properly treated and lacks scientific and technological content, resulting in a large amount of agricultural organic waste resources waste and the generation of harmful gases, pollution of groundwater sources and other new pollution problems. The method of composting (including bio-humic acid BFA composting) covers a large area, labor, time-consuming, low processing efficiency, unstable product quality, low commodity value, and the same amount of farmer's fertilizer, and farmers are not willing to use it in large quantities. Sales are difficult. Pollution problems such as harmful gases are also generated during the production process. Landfill is a common method for urban domestic garbage disposal. It accounts for more than 80% of the amount of garbage disposal in China. It not only fails to use resources reasonably, but also occupies a large amount of land, and is prone to secondary pollution such as leachate and methane gas. The use of organic waste to produce biogas is a good technology, but the initial investment, operational technology and potential hidden dangers, the difficulty of technology promotion and operability are very large, there are secondary treatment problems of biogas slurry and biogas residue. Incineration of organic waste also has technical difficulties and secondary pollution problems, and is not suitable for China's national conditions.
目前,对有机废弃物的处理还有一种方法,就是用来生产生物腐植酸。生物腐植酸加 工工艺涉及微生物工程、化学工程和生物化学、物理化学等多边沿学科,概括起来大致分为以下技术流派:以秸秆或木屑为原料,通过固体发酵,然后经碱液浸泡、酸中和,固液分离,用分离后的液体生产生物腐植酸液,残渣生产固体有机肥;以粪便残渣为原料,经液体发酵,固液分离,用分离后的液体生产生物腐植酸液,残渣生产固体有机肥;以有机废水为原料,经浓缩、活化、催化,固液分离,用分离后的液体生产生物腐植酸液,残渣生产固体有机肥。以上阐述的是目前我国对有机废弃物的主要处理方法,特别介绍了目前我国生物腐植酸行业对有机废弃物处理的主要技术流派,它们有以下共同弊端。At present, there is a method for the treatment of organic waste, which is used to produce biohumic acid. Biological humic acid plus The engineering process involves microbiology engineering, chemical engineering, biochemistry, physical chemistry and other multilateral disciplines. It is broadly divided into the following technical genres: using straw or wood chips as raw materials, passing solid fermentation, then soaking in lye, acid neutralization, solidification Separation of liquid, production of biological humic acid solution with separated liquid, residue production of solid organic fertilizer; use of fecal residue as raw material, liquid fermentation, solid-liquid separation, production of biological humic acid solution with separated liquid, residue to produce solid organic fertilizer The organic waste water is used as raw material, concentrated, activated, catalyzed, solid-liquid separation, and the biological humic acid solution is produced by using the separated liquid, and the residue is used to produce solid organic fertilizer. The above is the main treatment methods for organic waste in China. In particular, the main technical genres of organic waste treatment in the bio-humic acid industry in China are introduced. They have the following common drawbacks.
上述方法总体看来,占地大、用工多、费时耗能、费用昂贵、工艺复杂。生产加工过程容易产生二次污染,并且对有机废弃物转化不彻底,利用率较低。不能进行工业化生产。有鉴于此,特提出本发明。The above methods generally appear to occupy a large area, have more labor, consume time and energy, are expensive, and have complicated processes. The production and processing process is prone to secondary pollution, and the conversion of organic waste is not complete, and the utilization rate is low. Industrial production cannot be carried out. In view of this, the present invention has been specifically proposed.
发明内容Summary of the invention
本发明的目的之一在于提供一种水溶性纳米有机碳肥的制备方法,以解决现有技术中,对有机废弃物的处理方式占地大、能耗高、价格昂贵、工艺复杂、甚至造成二次污染的问题。所述的应用有机废弃物制备水溶性纳米有机碳肥的的方法,具有占地小、用工少、低能耗、效率高、费用低廉,工艺简便,适合工业化生产等优点。并且,该方法对原料没有过多的要求,对一切工、农业有机废弃物都能进行处理,使其全部成为水溶性纳米有机碳肥。并且本发明提供的处理方法,对有机废弃物处理彻底,无残渣,无二次污染,可以使有机废弃物得到完全地转化和利用。One of the objects of the present invention is to provide a method for preparing a water-soluble nano-organic carbon fertilizer, which solves the problems in the prior art that the treatment of organic waste occupies a large area, consumes high energy, is expensive, has complicated processes, and even causes The problem of secondary pollution. The method for preparing water-soluble nano organic carbon fertilizer by using organic waste has the advantages of small land occupation, low labor consumption, low energy consumption, high efficiency, low cost, simple process and suitable for industrial production. Moreover, the method does not require excessive raw materials, and can treat all industrial and agricultural organic wastes to make them all water-soluble nano organic carbon fertilizers. Moreover, the treatment method provided by the invention completely treats the organic waste, has no residue, no secondary pollution, and can completely convert and utilize the organic waste.
本发明另一目的在于提供一种所述的水溶性纳米有机碳肥的制备方法所制备的水溶性纳米有机碳肥,该水溶性纳米有机碳肥中还可以添加化肥,使其生产成全营养水溶性纳米有机碳肥,并且还包含大量的有益微生物,具有肥效全面均衡等优点。Another object of the present invention is to provide a water-soluble nano organic carbon fertilizer prepared by the method for preparing a water-soluble nano organic carbon fertilizer, wherein the water-soluble nano organic carbon fertilizer can also be added with a chemical fertilizer to produce a whole nutrient solution. Sexual nano-organic carbon fertilizer, and also contains a large number of beneficial microorganisms, with the advantages of comprehensive balance of fertilizer efficiency.
本发明再一目的在于提供一种有机复合肥,其肥效好,易降解,绿色环保。Another object of the present invention is to provide an organic compound fertilizer which has good fertilizer efficiency, is easy to degrade, and is environmentally friendly.
为了实现本发明的上述目的,特采用以下技术方案:In order to achieve the above object of the present invention, the following technical solutions are adopted:
一种水溶性纳米有机碳肥的制备方法,包括以下步骤:A method for preparing a water-soluble nano organic carbon fertilizer, comprising the following steps:
在有机废弃物中加入生物动力调控素进行生物酶解除臭,然后进行粉碎,粉碎后加水进行磨浆,在磨浆后得到有机废弃物浆料中加入化学催化裂解剂,并进行均质乳化处理,然后进行纳米萃取处理,再经过浓缩和干燥,得到该液体或固体水溶性纳米有机碳肥;The bio-dynamic regulator is added to the organic waste to remove the odor by the biological enzyme, and then pulverized, pulverized, and then water is added for refining. After the refining, the chemical waste cracking agent is added to the organic waste slurry, and the homogeneous emulsification treatment is performed. And then performing a nano-extraction treatment, and then concentrating and drying to obtain the liquid or solid water-soluble nano organic carbon fertilizer;
优选的,所述生物动力调控素包括枯草芽孢杆菌、胶冻芽孢杆菌、酵母菌、光合细菌、纤维素酶、葡聚糖酶和木聚糖酶中的一种或几种的组合;Preferably, the biodynamic regulator comprises a combination of one or more of Bacillus subtilis, Bacillus licheniformis, yeast, photosynthetic bacteria, cellulase, glucanase and xylanase;
优选的,所述化学催化裂解剂包括氢氧化物和过氧化物中的一种或者两种的组合;Preferably, the chemical catalytic cracking agent comprises one or a combination of a hydroxide and a peroxide;
更优选的,所述氢氧化物包括氢氧化铵、氢氧化钾、氢氧化钠、氢氧化钙和氢氧化镁中的一种或者几种的组合,所述过氧化物包括过硫酸钾或过硫酸铵中的一种或者两种。 More preferably, the hydroxide comprises one or a combination of ammonium hydroxide, potassium hydroxide, sodium hydroxide, calcium hydroxide and magnesium hydroxide, the peroxide comprising potassium persulfate or One or two of ammonium sulfate.
优选的,所述纳米萃取处理,溶液中粒径小于1000纳米的含碳粒子所占的比例大于95%。Preferably, in the nano-extraction treatment, the proportion of carbon-containing particles having a particle diameter of less than 1000 nm in the solution is greater than 95%.
本申请所提供的利用有机废弃物制备水溶性纳米有机碳肥的方法,首先通过大量喷洒生物动力调控素,生物动力调控素由高活性复合益生菌和复合酶组成,通过益生菌和酶的作用,可以有效消除有机废弃物的臭味。生物动力调控素优选由枯草芽孢杆菌、胶冻芽孢杆菌、酵母菌、光合细菌、纤维素酶、葡聚糖酶和木聚糖酶组成,然而可以视有机废弃物的具体成分而定,可以是上述酶和细菌中一种或者几种的组合,也可以包含上述所列举的微生物之外的酶或细菌。对经过除臭的有机废弃物进行粉碎和磨浆,粉碎后再加入具有强氧化性的化学原料,进行化学催化处理。经过均质乳化、纳米萃取、浓缩和干燥得到液体或固体水溶性纳米有机碳肥。浓缩采用低温真空浓缩设备,使其含水量低于50%,获得液体水溶性纳米有机碳肥。进一步进行低温真空干燥操作,使得到的水溶性纳米有机碳肥的含水量低于10%,获得固体水溶性纳米有机碳肥。该方法结合了生物酶解和化学降解的方法,同时结合均质乳化和纳米萃取技术,是一种低耗、高效、快速、简便地采用有机废弃物生产水溶纳米有机碳肥的方法。The method for preparing water-soluble nano-organic carbon fertilizer by using organic waste provided by the present application firstly comprises a large amount of biodynamic regulators, and the biodynamic regulator is composed of high-activity composite probiotics and complex enzymes, through the action of probiotics and enzymes. Can effectively eliminate the odor of organic waste. The biodynamic regulator is preferably composed of Bacillus subtilis, Bacillus licheniformis, yeast, photosynthetic bacteria, cellulase, glucanase and xylanase, but may depend on the specific composition of the organic waste, and may be The combination of one or more of the above enzymes and bacteria may also contain enzymes or bacteria other than the microorganisms listed above. The deodorized organic waste is pulverized and refined, and then pulverized and then chemically oxidized by adding a chemical material having strong oxidizing property. The liquid or solid water-soluble nano organic carbon fertilizer is obtained by homogeneous emulsification, nano-extraction, concentration and drying. Concentration is carried out using a low-temperature vacuum concentrating device to make the water content less than 50%, and a liquid water-soluble nano organic carbon fertilizer is obtained. Further, the low-temperature vacuum drying operation is performed, so that the water-soluble nano-organic carbon fertilizer has a water content of less than 10%, and a solid water-soluble nano organic carbon fertilizer is obtained. The method combines the methods of biological enzymatic hydrolysis and chemical degradation, and combines homogeneous emulsification and nano-extraction technology, is a low-cost, high-efficiency, rapid and simple method for producing water-soluble nano-organic carbon fertilizer by using organic waste.
优选的,所述有机废弃物包括:工业有机废水、农业有机废弃物和城镇生活垃圾。Preferably, the organic waste comprises: industrial organic waste water, agricultural organic waste and urban domestic waste.
工业有机废水包括:糖蜜液、酵母液、味精液等。农业有机废弃物包括:畜禽粪便、沼液沼渣、作物秸秆、锯沫木屑、蔬果残渣、酒糟饼粕、菌菇残渣和蚯蚓粪便等。城镇生活垃圾包括:餐厨余物和城镇粪池污泥等。Industrial organic wastewater includes: molasses liquid, yeast liquid, and sperm liquid. Agricultural organic waste includes: livestock and poultry manure, biogas slurry, crop straw, sawdust, vegetable and fruit residues, distiller's cake, mushroom residue and sputum. Urban domestic garbage includes: kitchen waste and urban sewage sludge.
优选的,所述在有机废弃物中加入生物动力调控素之前,还包括以下步骤:去除有机废弃物中夹杂的无机固体和塑料。Preferably, before adding the biodynamic regulator to the organic waste, the method further comprises the steps of: removing the inorganic solids and plastics contained in the organic waste.
在有机废弃物中,去除不能制备肥料的固体部分,包括无机固体和塑料。其中,无机固体包括金属、玻璃、电池、陶瓷和石块等。In organic waste, solid parts that cannot produce fertilizer, including inorganic solids and plastics, are removed. Among them, inorganic solids include metals, glass, batteries, ceramics, and stones.
优选的,所述粉碎的过程,具体包括以下步骤:将生物酶解除臭后的有机废弃物粉碎至粒径小于5毫米的颗粒;Preferably, the pulverizing process specifically comprises the steps of: pulverizing the organic waste deodorized by the biological enzyme to particles having a particle diameter of less than 5 mm;
更优选的,所述颗粒的粒径小于3毫米;More preferably, the particles have a particle size of less than 3 mm;
进一步优选的,所述粉碎采用湿料粉碎机进行操作。Further preferably, the pulverization is carried out using a wet pulverizer.
粉碎后的颗粒便于加水磨浆。The pulverized particles facilitate the refining of water.
优选的,所述加水进行磨浆的过程,具体包括以下步骤:在所述粉碎后的有机废弃物中加入其质量1~2倍的水,磨浆至得到的浆料的粒径小于10微米,更优选的料浆的粒径小于5微米;Preferably, the process of adding water to refine, specifically comprising the steps of: adding 1 to 2 times the mass of water to the pulverized organic waste, and refining until the obtained slurry has a particle diameter of less than 10 micrometers. a more preferred slurry having a particle size of less than 5 microns;
进一步优选的,所述磨浆采用通过胶体磨或锥体磨进行操作。Further preferably, the refining is operated by a colloid mill or a cone mill.
加水磨浆,进一步减小有机废弃物原料的粒径,更有助于提高有机碳肥的水溶性。 Adding water refining further reduces the particle size of the organic waste raw material, and helps to improve the water solubility of the organic carbon fertilizer.
优选的,所述化学催化裂解剂与所述料浆的质量比为(1~2):100。Preferably, the mass ratio of the chemical catalytic cracking agent to the slurry is (1 to 2): 100.
优选的,在所述纳米萃取处理之前,还包括:加入化肥。Preferably, before the nano-extraction treatment, the method further comprises: adding a fertilizer.
优选的,所述纳米萃取包括:超临界萃取、微波萃取、超声波萃取、超高压萃取和纳米研磨萃取的一种或者几种的组合;Preferably, the nano-extraction comprises: one or a combination of supercritical extraction, microwave extraction, ultrasonic extraction, ultra-high pressure extraction and nano-abrasive extraction;
更优选的,所述纳米萃取的溶剂为无机溶剂,所述萃取的次数为1~2次,进一步优选的,所述溶剂为水或二氧化碳。More preferably, the solvent for the nano-extraction is an inorganic solvent, and the number of extractions is 1 to 2 times. Further preferably, the solvent is water or carbon dioxide.
纳米萃取有利于充分提取水溶性成分,提高有机废弃物的利用率,使有机废弃物得到最大限度的利用。Nano-extraction is beneficial to fully extract water-soluble components, improve the utilization of organic waste, and maximize the utilization of organic waste.
优选的,所述超临界萃取的压力为25~80MPa,功率为5~25KW,温度45~80℃,液体流量为1000~2000L/h,萃取时间45~60min;Preferably, the supercritical extraction has a pressure of 25 to 80 MPa, a power of 5 to 25 KW, a temperature of 45 to 80 ° C, a liquid flow rate of 1000 to 2000 L/h, and an extraction time of 45 to 60 min;
优选的,所述微波萃取的频率为300~915MHz,功率为5~25KW,温度为35~80℃,反应罐容积为1000~3000L或液体流量为1000~3000L/h,萃取时间45~60min;Preferably, the frequency of the microwave extraction is 300-915 MHz, the power is 5-25 KW, the temperature is 35-80 ° C, the volume of the reaction tank is 1000-3000 L or the liquid flow rate is 1000-3000 L/h, and the extraction time is 45-60 min;
优选的,所述超声波萃取的频率为20~50KHz,功率为5~25KW,温度为30~60℃,反应罐容积为1000~3000L或液体流量为1000~3000L/h,萃取时间45~60min;Preferably, the ultrasonic extraction frequency is 20 to 50 KHz, the power is 5 to 25 KW, the temperature is 30 to 60 ° C, the reaction tank volume is 1000 to 3000 L or the liquid flow rate is 1000 to 3000 L/h, and the extraction time is 45 to 60 min;
优选的,所述超高压萃取的压力为250~380MPa,功率为5~25KW,温度为30-60℃,液体流量为1000~2000L/h,过压时间2~5min。Preferably, the ultrahigh pressure extraction has a pressure of 250 to 380 MPa, a power of 5 to 25 KW, a temperature of 30 to 60 ° C, a liquid flow rate of 1000 to 2000 L/h, and an overpressure time of 2 to 5 min.
优选的,所述纳米研磨萃取的压力为50~80MPa,功率为5~25KW,温度为30-60℃,反应罐容积为100~500L或液体流量为1000~5000L/h,过压时间2~5min。Preferably, the nano-grinding extraction pressure is 50-80 MPa, the power is 5-25 KW, the temperature is 30-60 ° C, the reaction tank volume is 100-500 L or the liquid flow rate is 1000-5000 L/h, and the overpressure time is 2~ 5min.
对于纳米萃取的手段,可以采用超临界萃取、微波萃取、超声波萃取、超高压萃取、纳米研磨萃取中的一种,或同一种手段的重复多次萃取,或者几种手段的组合。例如,超高压萃取2~5分钟后再次用超高压萃取2~5分钟;纳米研磨萃取2~5分钟后再次用纳米研磨萃取2~5分钟;超临界萃取5~10分钟后超声波萃取10~15分钟;超临界萃取5~10分后超高压萃取2~5分钟;微波萃取10~15分钟后超高压萃取2~5分钟;超声波萃取10~15分钟后超高压萃取2~5分钟;或者超高压萃取2~5分钟后纳米研磨萃取2~5分钟。萃取的频率、功率、温度等参数同上述所限定的工艺条件。For the means of nano-extraction, one of supercritical extraction, microwave extraction, ultrasonic extraction, ultra-high pressure extraction, nano-abrasive extraction, or repeated multiple extraction by the same means, or a combination of several means may be employed. For example, after ultra-high pressure extraction for 2 to 5 minutes, it is again extracted by ultra-high pressure for 2 to 5 minutes; after nano-grinding extraction for 2 to 5 minutes, it is again extracted by nano-milling for 2 to 5 minutes; after supercritical extraction for 5 to 10 minutes, ultrasonic extraction is carried out for 10 to 5 minutes. 15 minutes; supercritical extraction 5 to 10 minutes, ultra-high pressure extraction for 2 to 5 minutes; microwave extraction for 10 to 15 minutes, ultra-high pressure extraction for 2 to 5 minutes; ultrasonic extraction for 10 to 15 minutes, ultra-high pressure extraction for 2 to 5 minutes; or After ultra-high pressure extraction for 2 to 5 minutes, the nano-abrasive extraction is carried out for 2 to 5 minutes. The parameters such as the frequency, power, and temperature of the extraction are the same as those defined above.
如上所述的水溶性纳米有机碳肥的制备方法所制备的水溶性纳米有机碳肥。The water-soluble nano organic carbon fertilizer prepared by the method for preparing a water-soluble nano organic carbon fertilizer as described above.
优选的,在所述水溶性纳米有机碳肥中,含碳粒子的粒径小于800纳米的颗粒达到99%以上。Preferably, in the water-soluble nano organic carbon fertilizer, particles having a particle diameter of less than 800 nm of carbon-containing particles reach 99% or more.
本申请所提供的应用有机废弃物进行制备水溶性纳米有机碳肥的方法,其含碳粒子的粒径普遍小于600~800纳米。粒径小于800纳米的含碳粒子的比例可以达到99%以上。植物的有机质营养本质上就是碳元素,但单质碳不溶于水,不能被吸收,本申请所提供的水溶性纳米有机碳肥,有效碳的分子粒径小于800纳米,水溶性极好,可被植物根系和土壤 微生物直接全部吸收利用。目前,单独使用有机碳肥无法达到所预期的效果,因此,本申请还在水溶性纳米有机碳肥的基础上,加入化肥。化肥也称无机肥料,包括氮肥、磷肥、钾肥、中微量元素肥、复合肥料等。化肥中一般不含有机质,无改土培肥的作用,搭配有机碳肥使用,事半功倍,可以提高肥效。The method for preparing a water-soluble nano organic carbon fertilizer by using organic waste provided by the present application has a particle size of generally less than 600-800 nm. The proportion of carbonaceous particles having a particle diameter of less than 800 nm can reach 99% or more. The organic matter of plants is essentially carbon, but the elemental carbon is insoluble in water and cannot be absorbed. The water-soluble nano-organic carbon fertilizer provided in this application has an effective carbon molecular particle size of less than 800 nm and excellent water solubility. Plant roots and soil Microorganisms are directly absorbed and utilized. At present, the use of organic carbon fertilizer alone cannot achieve the desired effect. Therefore, the present application also adds a fertilizer based on the water-soluble nano organic carbon fertilizer. Fertilizer is also called inorganic fertilizer, including nitrogen fertilizer, phosphate fertilizer, potassium fertilizer, medium and trace element fertilizer, compound fertilizer and so on. Fertilizer generally does not contain organic matter, and does not have the effect of improving soil and fertilization. It can be used with organic carbon fertilizer, and it can improve the fertilizer efficiency with half the effort.
一种水溶性纳米有机碳肥,其是由上述的制备方法制备而成的。A water-soluble nano organic carbon fertilizer prepared by the above preparation method.
一种有机复合肥,包括水溶性纳米有机碳肥和无机化肥,水溶性纳米有机碳肥由以下步骤制备而成:将经生物动力调控素进行生物酶接除臭后的有机废弃物制备成有机废弃物浆料;向有机废弃物浆料中加入化学催化裂解剂;对有机废弃物浆料进行均质乳化处理;将有机废弃物浆料进行纳米萃取处理;以及浓缩和干燥。其中,化肥也称无机肥料,包括氮肥、磷肥、钾肥、中微量元素肥、复合肥料等An organic compound fertilizer comprising water-soluble nano organic carbon fertilizer and inorganic fertilizer, and the water-soluble nano organic carbon fertilizer is prepared by the following steps: preparing organic waste after bio-enzyme deodorization by biodynamic regulator Waste slurry; adding chemical catalytic cracking agent to organic waste slurry; homogenizing emulsification treatment of organic waste slurry; performing nano-extraction treatment on organic waste slurry; and concentrating and drying. Among them, chemical fertilizers are also called inorganic fertilizers, including nitrogen fertilizers, phosphate fertilizers, potassium fertilizers, medium and trace element fertilizers, compound fertilizers, etc.
优选地,上述生物动力调控素包括枯草芽孢杆菌、胶冻芽孢杆菌、酵母菌、光合细菌、纤维素酶、葡聚糖酶和木聚糖酶中的一种或几种的组合。Preferably, the above biodynamic regulator comprises a combination of one or more of Bacillus subtilis, Bacillus licheniformis, yeast, photosynthetic bacteria, cellulase, glucanase and xylanase.
优选地,上述化学催化裂解剂与料浆的质量比为(1~2):100,化学催化裂解剂包括氢氧化物和过氧化物中的一种或者两种的组合。Preferably, the mass ratio of the above chemical catalytic cracking agent to the slurry is (1 to 2): 100, and the chemical catalytic cracking agent comprises one or a combination of two of a hydroxide and a peroxide.
优选地,上述氢氧化物包括氢氧化铵、氢氧化钾、氢氧化钠、氢氧化钙和氢氧化镁中的一种或者几种的组合。Preferably, the above hydroxide comprises one or a combination of ammonium hydroxide, potassium hydroxide, sodium hydroxide, calcium hydroxide and magnesium hydroxide.
优选地,上述过氧化物包括过硫酸钾和过硫酸铵中的一种或者两种。Preferably, the above peroxide comprises one or both of potassium persulfate and ammonium persulfate.
优选地,制备上述有机废弃物浆料包括:在有机废弃物中加入生物动力调控素之前,去除有机废弃物中夹杂的无机固体和塑料;将生物酶解除臭后的有机废弃物粉碎至粒径小于5毫米的颗粒;以及将粉碎后的有机废弃物加入其质量1-2倍的水,磨浆至得到的浆料的粒径小于10微米。Preferably, the preparation of the above organic waste slurry comprises: removing inorganic solids and plastics contained in the organic waste before adding the biodynamic regulator to the organic waste; pulverizing the organic waste after the biological enzyme is deodorized to the particle size Particles of less than 5 mm; and the pulverized organic waste is added to water having a mass of 1-2 times, and is ground to a particle size of the obtained slurry of less than 10 μm.
优选地,上述纳米萃取包括:超临界萃取、微波萃取、超声波萃取、超高压萃取和纳米研磨萃取的一种或者几种的组合。Preferably, the above nano-extraction comprises one or a combination of supercritical extraction, microwave extraction, ultrasonic extraction, ultrahigh pressure extraction and nano-abrasive extraction.
优选地,上述纳米萃取的溶剂为无机溶剂。Preferably, the above-mentioned solvent for nano-extraction is an inorganic solvent.
优选地,经上述纳米萃取后,制得的水溶性纳米有机碳肥中,含碳粒子的粒径小于800纳米的颗粒达到99%以上。Preferably, in the water-soluble nano organic carbon fertilizer prepared by the above nano-extraction, particles having a particle diameter of less than 800 nm of carbon-containing particles reach 99% or more.
与现有技术相比,本发明的有益效果至少包括:Compared with the prior art, the beneficial effects of the present invention include at least:
1)、本申请所提供的一种水溶性纳米有机碳肥的制备方法,采用有机废弃物作为原料,具有占地小、用工少、低能耗、效率高、费用低廉,工艺简便,适合工业化生产等优点。1) The preparation method of a water-soluble nano organic carbon fertilizer provided by the present application uses organic waste as a raw material, has small land occupation, low labor consumption, low energy consumption, high efficiency, low cost, simple process, and is suitable for industrial production. Etc.
2)、本申请所提供的一种水溶性纳米有机碳肥的制备方法,可以有效彻底地处理有机废弃物,提高有机废弃物利用率,处理过程无残渣,无二次污染,是一种高效彻底利用有机废弃物的环保方法。 2) The preparation method of the water-soluble nano organic carbon fertilizer provided by the application can effectively and thoroughly treat the organic waste, improve the utilization rate of the organic waste, has no residue in the treatment process, and has no secondary pollution, and is highly efficient. An environmentally friendly method that thoroughly utilizes organic waste.
3)、本申请所提供的一种水溶性纳米有机碳肥的制备方法所制备的水溶性纳米有机碳肥,还可以添加化肥,使其生产成全营养水溶纳米有机碳肥,并且还包含大量的有益微生物,具有肥效全面均衡等优点。3) The water-soluble nano organic carbon fertilizer prepared by the method for preparing a water-soluble nano organic carbon fertilizer provided by the present application can also be added with chemical fertilizer to produce a nutrient-soluble nano-organic carbon fertilizer, and also contains a large amount of Beneficial microorganisms have the advantages of comprehensive balance of fertilizer efficiency.
4)、本申请所提供的一种水溶性纳米有机碳肥的制备方法所制备的水溶性纳米有机碳肥,含碳粒子的粒径小于800纳米的颗粒达到99%以上,水溶性极好,可被植物根系和土壤微生物直接全部吸收利用。4) The water-soluble nano organic carbon fertilizer prepared by the method for preparing a water-soluble nano organic carbon fertilizer provided by the present application, the particle size of the carbonaceous particles having a particle diameter of less than 800 nm is over 99%, and the water solubility is excellent. It can be directly absorbed and utilized by plant roots and soil microorganisms.
具体实施方式detailed description
下面将结合实施例对本发明的实施方案进行详细描述,但是本领域技术人员将会理解,下列实施例仅用于说明本发明,而不应视为限制本发明的范围。实施例中未注明具体条件者,按照常规条件或制造商建议的条件进行。所用试剂或仪器未注明生产厂商者,均为可以通过市售购买获得的常规产品。The embodiments of the present invention will be described in detail below with reference to the accompanying drawings, but the present invention is to be construed as illustrative only. Those who do not specify the specific conditions in the examples are carried out according to the conventional conditions or the conditions recommended by the manufacturer. The reagents or instruments used are not indicated by the manufacturer, and are conventional products that can be obtained by commercially available purchase.
实施例1Example 1
对有机废弃物中的废金属、废塑料、废玻璃、废电池、陶瓷石块等进行分拣去杂,在分拣去杂后对其喷洒由枯草芽孢杆菌、胶冻芽孢杆菌、酵母菌、光合细菌、纤维素酶、葡聚糖酶和木聚糖酶组成的生物动力调控素进行生物酶解除臭,然后通过湿料粉碎机将其粉碎成3毫米以下颗粒。粉碎后按干湿比1:1的比例加水,然后通过胶体磨将其磨成5微米以下的浆料。在加水磨浆后的有机废弃物浆料中加入1%重量的氢氧化钾,通过均质乳化机在反应罐内对其进行化学裂解均质乳化。然后进行超临界萃取,使溶液中粒径小于1000纳米的含碳粒子所占的比例大于95%,超临界萃取的压力为25MPa,功率为5KW,温度45℃,液体流量为1000L/h,萃取时间45min。然后进行低温真空浓缩,使其含水量控制在50%以下,最后通过液体定量灌装机对其进行灌装,得到该液体水溶性纳米有机碳肥。Dispose of waste metal, waste plastics, waste glass, waste batteries, ceramic stones, etc. in organic waste, and spray them on Bacillus subtilis, Bacillus licheniformis, yeast, etc. after sorting and removing impurities. A biodynamic regulator consisting of photosynthetic bacteria, cellulase, glucanase, and xylanase is deactivated by a biological enzyme, and then pulverized into particles of 3 mm or less by a wet pulverizer. After pulverization, water was added in a ratio of dry to wet ratio of 1:1, and then ground to a slurry of 5 μm or less by a colloid mill. 1% by weight of potassium hydroxide was added to the organic waste slurry after water refining, and it was homogenized and emulsified by chemical cracking in a reaction tank by a homogenizer. Then supercritical extraction is carried out so that the proportion of carbonaceous particles having a particle diameter of less than 1000 nm in the solution is greater than 95%, the pressure of supercritical extraction is 25 MPa, the power is 5 KW, the temperature is 45 ° C, and the liquid flow rate is 1000 L/h. Time 45min. Then, it is concentrated under low temperature vacuum to control the water content to below 50%. Finally, it is filled by a liquid quantitative filling machine to obtain the liquid water-soluble nano organic carbon fertilizer.
实施例2Example 2
对有机废弃物中的废金属、废塑料、废玻璃、废电池、陶瓷石块等进行分拣去杂,然后喷洒由枯草芽孢杆菌、胶冻芽孢杆菌、酵母菌、光合细菌、纤维素酶、葡聚糖酶和木聚糖酶组成的生物动力调控素进行生物酶解除臭。除臭后通过湿料粉碎机将其粉碎成5毫米以下颗粒。粉碎后,按干湿比1︰2的比例加水,然后通过胶体磨或锥体磨将其磨成10微米以下的浆料。在加水磨浆后的有机废弃物浆料中加入2%重量的氢氧化铵和1%重量的过硫酸钾,通过均质乳化机在反应罐内对其进行化学裂解均质乳化。然后进行超高压萃取,使溶液中粒径小于1000纳米的含碳粒子所占的比例大于95%。超高压萃取的压力为250MPa,功率为5KW,温度为30℃,液体流量为1000L/h,过压时间2min。然后进行低温真空浓缩,使其含水量控制在50%以下,再通过真空干燥降低含水量至10%以下,最后通过固体粉料定量包装机对其进行包装,得到该固体粉状水溶性纳米有机碳肥。 Disposal of scrap metal, waste plastics, waste glass, waste batteries, ceramic stones, etc. in organic waste, and then spraying by Bacillus subtilis, Bacillus licheniformis, yeast, photosynthetic bacteria, cellulase, A biodynamic regulator consisting of a glucanase and a xylanase is used to deodorize the enzyme. After deodorization, it was pulverized into particles of 5 mm or less by a wet pulverizer. After pulverization, water is added in a ratio of dry to wet ratio of 1..2, and then ground to a slurry of 10 μm or less by a colloid mill or a cone mill. 2% by weight of ammonium hydroxide and 1% by weight of potassium persulfate were added to the organic waste slurry after water refining, and the mixture was homogenized and emulsified by chemical cracking in a reaction tank by a homogenizer. Ultrahigh pressure extraction is then carried out so that the proportion of carbonaceous particles having a particle size of less than 1000 nm in the solution is greater than 95%. The pressure of the ultrahigh pressure extraction is 250 MPa, the power is 5 KW, the temperature is 30 ° C, the liquid flow rate is 1000 L/h, and the overpressure time is 2 min. Then, it is concentrated under low temperature vacuum to control the water content to less than 50%, and then the water content is reduced to less than 10% by vacuum drying, and finally packaged by a solid powder quantitative packaging machine to obtain the solid powdery water-soluble nano organic Carbon fertilizer.
实施例3Example 3
对有机废弃物中的废金属、废塑料、废玻璃、废电池、陶瓷石块等进行分拣去杂,然后喷洒由枯草芽孢杆菌、胶冻芽孢杆菌、酵母菌、光合细菌、纤维素酶、葡聚糖酶和木聚糖酶组成的生物动力调控素进行生物酶解除臭。除臭后,通过湿料粉碎机将其粉碎成5毫米以下颗粒。粉碎后,按干湿比1︰1的比例加水,然后通过胶体磨或锥体磨将其磨成10微米以下的浆料。在加水磨浆后的有机废弃物浆料中加入2%重量的氢氧化钾和1%重量的过硫酸铵,通过均质乳化机在反应罐内对其进行化学裂解均质乳化。加入氮磷钾、硅钙镁等大中微量元素再次进行均质乳化。对均质乳化后的上述混合物料,通过微波萃取设备对其进行萃取,使溶液中粒径小于1000纳米的含碳粒子所占的比例大于95%,微波萃取频率为300MHz,功率为5KW,温度为35℃,反应罐容积为1000L,萃取时间45min。然后进行低温真空浓缩,使其含水量控制在50%以下,最后通过液体定量灌装机对其进行灌装,得到该液体全营养水溶性纳米有机碳肥。Disposal of scrap metal, waste plastics, waste glass, waste batteries, ceramic stones, etc. in organic waste, and then spraying by Bacillus subtilis, Bacillus licheniformis, yeast, photosynthetic bacteria, cellulase, A biodynamic regulator consisting of a glucanase and a xylanase is used to deodorize the enzyme. After deodorization, it was pulverized into particles of 5 mm or less by a wet pulverizer. After pulverization, water is added in a ratio of dry to wet ratio of 1..1, and then ground to a slurry of 10 μm or less by a colloid mill or a cone mill. 2% by weight of potassium hydroxide and 1% by weight of ammonium persulfate were added to the organic waste slurry after water refining, and the mixture was homogenized and emulsified by chemical cracking in a reaction tank by a homogenizer. Adding large and medium trace elements such as NPK, silicocalcium and magnesium to homogenize emulsification again. After homogenizing the emulsified mixture, the mixture is extracted by a microwave extraction device, so that the proportion of the carbonaceous particles having a particle diameter of less than 1000 nm in the solution is greater than 95%, the microwave extraction frequency is 300 MHz, and the power is 5 KW. The temperature was 35 ° C, the reaction tank volume was 1000 L, and the extraction time was 45 min. Then, it is concentrated under low temperature vacuum to control the water content to below 50%. Finally, it is filled by a liquid quantitative filling machine to obtain the liquid total nutrient water-soluble nano organic carbon fertilizer.
实施例4Example 4
对有机废弃物中的废金属、废塑料、废玻璃、废电池、陶瓷石块等进行分拣去杂,在分拣去杂后对其喷洒由枯草芽孢杆菌、胶冻芽孢杆菌、酵母菌、光合细菌、纤维素酶、葡聚糖酶和木聚糖酶组成的生物动力调控素进行生物酶解除臭。对分拣去杂生物酶解除臭后的有机废弃物,通过湿料粉碎机将其粉碎成5毫米以下颗粒。对粉碎后的有机废弃物,按干湿比1︰1的比例加水,然后通过胶体磨或锥体磨将其磨成10微米以下的浆料。在加水磨浆后的有机废弃物浆料中加入2%重量的氢氧化钾和1%重量的过硫酸铵,通过均质乳化机在反应罐内对其进行化学裂解均质乳化。加入氮磷钾、硅钙镁等大中微量元素再次进行均质乳化。对均质乳化后的上述混合物料,通过超声波萃取设备对其进行萃取,使其溶液中粒径小于1000纳米的含碳粒子所占的比例大于95%,超声波萃取的频率为20KHz,功率为5KW,温度为30℃,萃取时间为60min。然后进行低温真空浓缩,使其含水量控制在50%以下,最后通过液体定量灌装机对其进行灌装,得到该液体水溶性纳米有机碳肥。Dispose of waste metal, waste plastics, waste glass, waste batteries, ceramic stones, etc. in organic waste, and spray them on Bacillus subtilis, Bacillus licheniformis, yeast, etc. after sorting and removing impurities. The biodynamic regulator consisting of photosynthetic bacteria, cellulase, glucanase and xylanase carries out bio-enzyme deodorization. The organic waste which has been deodorized by sorting the detoxification enzyme is pulverized into particles of 5 mm or less by a wet pulverizer. For the pulverized organic waste, water is added in a ratio of dry to wet ratio of 1..1, and then ground to a slurry of 10 μm or less by a colloid mill or a cone mill. 2% by weight of potassium hydroxide and 1% by weight of ammonium persulfate were added to the organic waste slurry after water refining, and the mixture was homogenized and emulsified by chemical cracking in a reaction tank by a homogenizer. Adding large and medium trace elements such as NPK, silicocalcium and magnesium to homogenize emulsification again. The homogeneous mixture after emulsification is extracted by ultrasonic extraction equipment, and the proportion of carbonaceous particles having a particle diameter of less than 1000 nm in the solution is greater than 95%, the frequency of ultrasonic extraction is 20 KHz, and the power is 5 KW. The temperature was 30 ° C and the extraction time was 60 min. Then, it is concentrated under low temperature vacuum to control the water content to below 50%. Finally, it is filled by a liquid quantitative filling machine to obtain the liquid water-soluble nano organic carbon fertilizer.
实施例5Example 5
对有机废弃物中的废金属、废塑料、废玻璃、废电池、陶瓷石块等进行分拣去杂,然后喷洒由枯草芽孢杆菌、胶冻芽孢杆菌、酵母菌、光合细菌、纤维素酶、葡聚糖酶和木聚糖酶组成的生物动力调控素进行生物酶解除臭。除臭后通过湿料粉碎机将其粉碎成5毫米以下颗粒。粉碎后,按干湿比1︰2的比例加水,然后通过胶体磨或锥体磨将其磨成10微米以下的浆料。在加水磨浆后的有机废弃物浆料中加入2%重量的氢氧化铵和1%重量的过硫酸铵,通过均质乳化机在反应罐内对其进行化学裂解均质乳化。然后进行纳米研磨萃取,使溶液中粒径小于1000纳米的含碳粒子所占的比例大于95%。纳米研磨萃取的压力为 50MPa,功率为5KW,温度为30℃,液体流量为1000L/h,过压时间2min。然后进行低温真空浓缩,使其含水量控制在50%以下,再通过真空干燥降低含水量至10%以下,最后通过固体粉料定量包装机对其进行包装,得到该固体粉状水溶性纳米有机碳肥。Disposal of scrap metal, waste plastics, waste glass, waste batteries, ceramic stones, etc. in organic waste, and then spraying by Bacillus subtilis, Bacillus licheniformis, yeast, photosynthetic bacteria, cellulase, A biodynamic regulator consisting of a glucanase and a xylanase is used to deodorize the enzyme. After deodorization, it was pulverized into particles of 5 mm or less by a wet pulverizer. After pulverization, water is added in a ratio of dry to wet ratio of 1..2, and then ground to a slurry of 10 μm or less by a colloid mill or a cone mill. 2% by weight of ammonium hydroxide and 1% by weight of ammonium persulfate were added to the organic waste slurry after water refining, and the mixture was homogenized and emulsified by chemical cracking in a reaction tank by a homogenizer. The nano-abrasive extraction is then carried out so that the proportion of carbonaceous particles having a particle size of less than 1000 nm in the solution is greater than 95%. The pressure of nano-grinding is 50MPa, power 5KW, temperature 30 ° C, liquid flow rate 1000L / h, overpressure time 2min. Then, it is concentrated under low temperature vacuum to control the water content to less than 50%, and then the water content is reduced to less than 10% by vacuum drying, and finally packaged by a solid powder quantitative packaging machine to obtain the solid powdery water-soluble nano organic Carbon fertilizer.
实施例6Example 6
本实施例与实施例1基本相同,主要区别在于超临界萃取的工艺参数不同。This embodiment is basically the same as Embodiment 1, and the main difference is that the process parameters of supercritical extraction are different.
对有机废弃物中的废金属、废塑料、废玻璃、废电池、陶瓷石块等进行分拣去杂,在分拣去杂后对其喷洒由枯草芽孢杆菌、胶冻芽孢杆菌、酵母菌、光合细菌、纤维素酶、葡聚糖酶和木聚糖酶组成的生物动力调控素进行生物酶解除臭,然后通过湿料粉碎机将其粉碎成3毫米以下颗粒。粉碎后按干湿比1:1的比例加水,然后通过胶体磨将其磨成5微米以下的浆料。在加水磨浆后的有机废弃物浆料中加入1%重量的氢氧化钾,通过均质乳化机在反应罐内对其进行化学裂解均质乳化。然后进行超临界萃取,使溶液中粒径小于1000纳米的含碳粒子所占的比例大于95%,超临界萃取的压力为80MPa,功率为25KW,温度80℃,液体流量为2000L/h,萃取时间60min。然后进行低温真空浓缩,使其含水量控制在50%以下,最后通过液体定量灌装机对其进行灌装,得到该液体水溶性纳米有机碳肥。Dispose of waste metal, waste plastics, waste glass, waste batteries, ceramic stones, etc. in organic waste, and spray them on Bacillus subtilis, Bacillus licheniformis, yeast, etc. after sorting and removing impurities. A biodynamic regulator consisting of photosynthetic bacteria, cellulase, glucanase, and xylanase is deactivated by a biological enzyme, and then pulverized into particles of 3 mm or less by a wet pulverizer. After pulverization, water was added in a ratio of dry to wet ratio of 1:1, and then ground to a slurry of 5 μm or less by a colloid mill. 1% by weight of potassium hydroxide was added to the organic waste slurry after water refining, and it was homogenized and emulsified by chemical cracking in a reaction tank by a homogenizer. Then supercritical extraction is carried out so that the proportion of carbonaceous particles having a particle diameter of less than 1000 nm in the solution is greater than 95%, the pressure of supercritical extraction is 80 MPa, the power is 25 KW, the temperature is 80 ° C, and the liquid flow rate is 2000 L/h. Time 60min. Then, it is concentrated under low temperature vacuum to control the water content to below 50%. Finally, it is filled by a liquid quantitative filling machine to obtain the liquid water-soluble nano organic carbon fertilizer.
实施例7Example 7
本实施例与实施例1基本相同,主要区别在于超临界萃取的工艺参数不同。This embodiment is basically the same as Embodiment 1, and the main difference is that the process parameters of supercritical extraction are different.
对有机废弃物中的废金属、废塑料、废玻璃、废电池、陶瓷石块等进行分拣去杂,在分拣去杂后对其喷洒由枯草芽孢杆菌和胶冻芽孢杆菌组成的生物动力调控素进行生物酶解除臭,然后通过湿料粉碎机将其粉碎成3毫米以下颗粒。粉碎后按干湿比1:1的比例加水,然后通过胶体磨将其磨成5微米以下的浆料。在加水磨浆后的有机废弃物浆料中加入1%重量的氢氧化钠,通过均质乳化机在反应罐内对其进行化学裂解均质乳化。然后进行超临界萃取,使溶液中粒径小于1000纳米的含碳粒子所占的比例大于95%,超临界萃取的压力为65MPa,功率为15KW,温度60℃,液体流量为1500L/h,萃取时间50min。然后进行低温真空浓缩,使其含水量控制在50%以下,最后通过液体定量灌装机对其进行灌装,得到该液体水溶性纳米有机碳肥。Disposal of scrap metal, waste plastics, waste glass, waste batteries, ceramic stones, etc. in organic waste, and spraying biodynamics consisting of Bacillus subtilis and Bacillus licheniformis after sorting and removing impurities The regulator regulates the odor by the biological enzyme, and then pulverizes it into particles of 3 mm or less by a wet pulverizer. After pulverization, water was added in a ratio of dry to wet ratio of 1:1, and then ground to a slurry of 5 μm or less by a colloid mill. 1% by weight of sodium hydroxide was added to the organic waste slurry after water refining, and it was homogenized and emulsified by chemical cracking in a reaction tank through a homogenizer. Then supercritical extraction is carried out so that the proportion of carbonaceous particles having a particle diameter of less than 1000 nm in the solution is greater than 95%, the pressure of supercritical extraction is 65 MPa, the power is 15 KW, the temperature is 60 ° C, and the liquid flow rate is 1500 L/h. Time 50min. Then, it is concentrated under low temperature vacuum to control the water content to below 50%. Finally, it is filled by a liquid quantitative filling machine to obtain the liquid water-soluble nano organic carbon fertilizer.
实施例8Example 8
本实施例与实施例2基本相同,主要区别在于超高压萃取的工艺参数不同。This embodiment is basically the same as Embodiment 2, and the main difference is that the process parameters of the ultrahigh pressure extraction are different.
对有机废弃物中的废金属、废塑料、废玻璃、废电池、陶瓷石块等进行分拣去杂,然后喷洒由枯草芽孢杆菌、胶冻芽孢杆菌、酵母菌、光合细菌、纤维素酶、葡聚糖酶和木聚糖酶组成的生物动力调控素进行生物酶解除臭。除臭后通过湿料粉碎机将其粉碎成5毫米以下颗粒。粉碎后,按干湿比1︰2的比例加水,然后通过胶体磨或锥体磨将其磨成10微米以下的浆料。在加水磨浆后的有机废弃物浆料中加入2%重量的氢氧化铵和1%重量的过硫 酸钾,通过均质乳化机在反应罐内对其进行化学裂解均质乳化。然后进行超高压萃取,使溶液中粒径小于1000纳米的含碳粒子所占的比例大于95%。超高压萃取的压力为380MPa,功率为25KW,温度为60℃,液体流量为2000L/h,过压时间5min。然后进行低温真空浓缩,使其含水量控制在50%以下,再通过真空干燥降低含水量至10%以下,最后通过固体粉料定量包装机对其进行包装,得到该固体粉状水溶性纳米有机碳肥。Disposal of scrap metal, waste plastics, waste glass, waste batteries, ceramic stones, etc. in organic waste, and then spraying by Bacillus subtilis, Bacillus licheniformis, yeast, photosynthetic bacteria, cellulase, A biodynamic regulator consisting of a glucanase and a xylanase is used to deodorize the enzyme. After deodorization, it was pulverized into particles of 5 mm or less by a wet pulverizer. After pulverization, water is added in a ratio of dry to wet ratio of 1..2, and then ground to a slurry of 10 μm or less by a colloid mill or a cone mill. Add 2% by weight of ammonium hydroxide and 1% by weight of persulfuric acid to the organic waste slurry after water refining Potassium acid is homogenized and emulsified by chemical cracking in a reaction tank through a homogenizer. Ultrahigh pressure extraction is then carried out so that the proportion of carbonaceous particles having a particle size of less than 1000 nm in the solution is greater than 95%. The pressure of the ultrahigh pressure extraction is 380 MPa, the power is 25 KW, the temperature is 60 ° C, the liquid flow rate is 2000 L/h, and the overpressure time is 5 min. Then, it is concentrated under low temperature vacuum to control the water content to less than 50%, and then the water content is reduced to less than 10% by vacuum drying, and finally packaged by a solid powder quantitative packaging machine to obtain the solid powdery water-soluble nano organic Carbon fertilizer.
实施例9Example 9
本实施例与实施例2基本相同,主要区别在于超高压萃取的工艺参数不同。This embodiment is basically the same as Embodiment 2, and the main difference is that the process parameters of the ultrahigh pressure extraction are different.
对有机废弃物中的废金属、废塑料、废玻璃、废电池、陶瓷石块等进行分拣去杂,然后喷洒由枯草芽孢杆菌、胶冻芽孢杆菌、酵母菌和光合细菌组成的生物动力调控素进行生物酶解除臭。除臭后通过湿料粉碎机将其粉碎成5毫米以下颗粒。粉碎后,按干湿比1︰2的比例加水,然后通过胶体磨或锥体磨将其磨成10微米以下的浆料。在加水磨浆后的有机废弃物浆料中加入2%重量的氢氧化铵和1%重量的过硫酸钾,通过均质乳化机在反应罐内对其进行化学裂解均质乳化。然后进行超高压萃取,使溶液中粒径小于1000纳米的含碳粒子所占的比例大于95%。超高压萃取的压力为300MPa,功率为15KW,温度为40℃,液体流量为1500L/h,过压时间3min。然后进行低温真空浓缩,使其含水量控制在50%以下,再通过真空干燥降低含水量至10%以下,最后通过固体粉料定量包装机对其进行包装,得到该固体粉状水溶性纳米有机碳肥。Sorting and removing waste metal, waste plastics, waste glass, waste batteries, ceramic stones, etc. in organic waste, and then spraying biodynamic regulation consisting of Bacillus subtilis, Bacillus licheniformis, yeast and photosynthetic bacteria The enzyme is used to deodorize the enzyme. After deodorization, it was pulverized into particles of 5 mm or less by a wet pulverizer. After pulverization, water is added in a ratio of dry to wet ratio of 1..2, and then ground to a slurry of 10 μm or less by a colloid mill or a cone mill. 2% by weight of ammonium hydroxide and 1% by weight of potassium persulfate were added to the organic waste slurry after water refining, and the mixture was homogenized and emulsified by chemical cracking in a reaction tank by a homogenizer. Ultrahigh pressure extraction is then carried out so that the proportion of carbonaceous particles having a particle size of less than 1000 nm in the solution is greater than 95%. The pressure of the ultrahigh pressure extraction is 300 MPa, the power is 15 KW, the temperature is 40 ° C, the liquid flow rate is 1500 L/h, and the overpressure time is 3 min. Then, it is concentrated under low temperature vacuum to control the water content to less than 50%, and then the water content is reduced to less than 10% by vacuum drying, and finally packaged by a solid powder quantitative packaging machine to obtain the solid powdery water-soluble nano organic Carbon fertilizer.
实施例10Example 10
本实施例与实施例3基本相同,主要区别在于微波萃取的工艺参数不同。This embodiment is basically the same as Embodiment 3, and the main difference is that the process parameters of microwave extraction are different.
对有机废弃物中的废金属、废塑料、废玻璃、废电池、陶瓷石块等进行分拣去杂,然后喷洒由枯草芽孢杆菌、胶冻芽孢杆菌、酵母菌、光合细菌、纤维素酶、葡聚糖酶和木聚糖酶组成的生物动力调控素进行生物酶解除臭。除臭后,通过湿料粉碎机将其粉碎成5毫米以下颗粒。粉碎后,按干湿比1︰1的比例加水,然后通过胶体磨或锥体磨将其磨成10微米以下的浆料。在加水磨浆后的有机废弃物浆料中加入2%重量的氢氧化钾和1%重量的过硫酸铵,通过均质乳化机在反应罐内对其进行化学裂解均质乳化。加入氮磷钾、硅钙镁等大中微量元素再次进行均质乳化。对均质乳化后的上述混合物料,通过微波萃取设备对其进行萃取,使溶液中粒径小于1000纳米的含碳粒子所占的比例大于95%,微波萃取频率为915MHz,功率为25KW,温度为80℃,反应罐容积为3000L,萃取时间60min。然后进行低温真空浓缩,使其含水量控制在50%以下,最后通过液体定量灌装机对其进行灌装,得到该液体全营养水溶性纳米有机碳肥。Disposal of scrap metal, waste plastics, waste glass, waste batteries, ceramic stones, etc. in organic waste, and then spraying by Bacillus subtilis, Bacillus licheniformis, yeast, photosynthetic bacteria, cellulase, A biodynamic regulator consisting of a glucanase and a xylanase is used to deodorize the enzyme. After deodorization, it was pulverized into particles of 5 mm or less by a wet pulverizer. After pulverization, water is added in a ratio of dry to wet ratio of 1..1, and then ground to a slurry of 10 μm or less by a colloid mill or a cone mill. 2% by weight of potassium hydroxide and 1% by weight of ammonium persulfate were added to the organic waste slurry after water refining, and the mixture was homogenized and emulsified by chemical cracking in a reaction tank by a homogenizer. Adding large and medium trace elements such as NPK, silicocalcium and magnesium to homogenize emulsification again. The homogeneous mixture after emulsification is extracted by a microwave extraction device, so that the proportion of carbonaceous particles having a particle diameter of less than 1000 nm in the solution is greater than 95%, the microwave extraction frequency is 915 MHz, and the power is 25 KW. The temperature was 80 ° C, the reaction tank volume was 3000 L, and the extraction time was 60 min. Then, it is concentrated under low temperature vacuum to control the water content to below 50%. Finally, it is filled by a liquid quantitative filling machine to obtain the liquid total nutrient water-soluble nano organic carbon fertilizer.
实施例11Example 11
本实施例与实施例3基本相同,主要区别在于微波萃取的工艺参数不同。 This embodiment is basically the same as Embodiment 3, and the main difference is that the process parameters of microwave extraction are different.
对有机废弃物中的废金属、废塑料、废玻璃、废电池、陶瓷石块等进行分拣去杂,然后喷洒由枯草芽孢杆菌、胶冻芽孢杆菌、酵母菌、光合细菌、纤维素酶和葡聚糖酶组成的生物动力调控素进行生物酶解除臭。除臭后,通过湿料粉碎机将其粉碎成5毫米以下颗粒。粉碎后,按干湿比1︰1的比例加水,然后通过胶体磨或锥体磨将其磨成10微米以下的浆料。在加水磨浆后的有机废弃物浆料中加入2%重量的氢氧化镁和1%重量的过硫酸铵,通过均质乳化机在反应罐内对其进行化学裂解均质乳化。加入氮磷钾、硅钙镁等大中微量元素再次进行均质乳化。对均质乳化后的上述混合物料,通过微波萃取设备对其进行萃取,使溶液中粒径小于1000纳米的含碳粒子所占的比例大于95%,微波萃取频率为600MHz,功率为18KW,温度为56℃,反应罐容积为2000L,萃取时间50min。然后进行低温真空浓缩,使其含水量控制在50%以下,最后通过液体定量灌装机对其进行灌装,得到该液体全营养水溶性纳米有机碳肥。Scrap metal, waste plastics, waste glass, waste batteries, ceramic stones, etc. in organic waste, and then sprayed by Bacillus subtilis, Bacillus licheniformis, yeast, photosynthetic bacteria, cellulase and A biodynamic regulator consisting of a glucanase is used to deodorize the enzyme. After deodorization, it was pulverized into particles of 5 mm or less by a wet pulverizer. After pulverization, water is added in a ratio of dry to wet ratio of 1..1, and then ground to a slurry of 10 μm or less by a colloid mill or a cone mill. 2% by weight of magnesium hydroxide and 1% by weight of ammonium persulfate were added to the organic waste slurry after water refining, and the mixture was homogenized and emulsified by chemical cracking in a reaction tank by a homogenizer. Adding large and medium trace elements such as NPK, silicocalcium and magnesium to homogenize emulsification again. The homogeneous mixture after emulsification is extracted by a microwave extraction device, so that the proportion of carbonaceous particles having a particle diameter of less than 1000 nm in the solution is greater than 95%, the microwave extraction frequency is 600 MHz, and the power is 18 KW. At 56 ° C, the reactor tank volume was 2000 L and the extraction time was 50 min. Then, it is concentrated under low temperature vacuum to control the water content to below 50%. Finally, it is filled by a liquid quantitative filling machine to obtain the liquid total nutrient water-soluble nano organic carbon fertilizer.
实施例12Example 12
本实施例与实施例4基本相同,主要区别在于超声波萃取的工艺参数不同。This embodiment is basically the same as Embodiment 4, and the main difference is that the process parameters of ultrasonic extraction are different.
对有机废弃物中的废金属、废塑料、废玻璃、废电池、陶瓷石块等进行分拣去杂,在分拣去杂后对其喷洒由枯草芽孢杆菌、胶冻芽孢杆菌、酵母菌、光合细菌、纤维素酶、葡聚糖酶和木聚糖酶组成的生物动力调控素进行生物酶解除臭。对分拣去杂生物酶解除臭后的有机废弃物,通过湿料粉碎机将其粉碎成5毫米以下颗粒。对粉碎后的有机废弃物,按干湿比1︰1的比例加水,然后通过胶体磨或锥体磨将其磨成10微米以下的浆料。在加水磨浆后的有机废弃物浆料中加入2%重量的氢氧化钾和1%重量的过硫酸铵,通过均质乳化机在反应罐内对其进行化学裂解均质乳化。加入氮磷钾、硅钙镁等大中微量元素再次进行均质乳化。对均质乳化后的上述混合物料,通过超声波萃取设备对其进行萃取,使其溶液中粒径小于1000纳米的含碳粒子所占的比例大于95%,超声波萃取的的频率为50KHz,功率为25KW,温度为60℃,萃取时间为60min。然后进行低温真空浓缩,使其含水量控制在50%以下,最后通过液体定量灌装机对其进行灌装,得到该液体水溶性纳米有机碳肥。Dispose of waste metal, waste plastics, waste glass, waste batteries, ceramic stones, etc. in organic waste, and spray them on Bacillus subtilis, Bacillus licheniformis, yeast, etc. after sorting and removing impurities. The biodynamic regulator consisting of photosynthetic bacteria, cellulase, glucanase and xylanase carries out bio-enzyme deodorization. The organic waste which has been deodorized by sorting the detoxification enzyme is pulverized into particles of 5 mm or less by a wet pulverizer. For the pulverized organic waste, water is added in a ratio of dry to wet ratio of 1..1, and then ground to a slurry of 10 μm or less by a colloid mill or a cone mill. 2% by weight of potassium hydroxide and 1% by weight of ammonium persulfate were added to the organic waste slurry after water refining, and the mixture was homogenized and emulsified by chemical cracking in a reaction tank by a homogenizer. Adding large and medium trace elements such as NPK, silicocalcium and magnesium to homogenize emulsification again. The homogeneous mixture after emulsification is extracted by an ultrasonic extraction device, and the proportion of carbonaceous particles having a particle diameter of less than 1000 nm in the solution is greater than 95%, and the frequency of ultrasonic extraction is 50 kHz, and the power is 25 KW, temperature is 60 ° C, extraction time is 60 min. Then, it is concentrated under low temperature vacuum to control the water content to below 50%. Finally, it is filled by a liquid quantitative filling machine to obtain the liquid water-soluble nano organic carbon fertilizer.
实施例13Example 13
本实施例与实施例4基本相同,主要区别在于超声波萃取的工艺参数不同。This embodiment is basically the same as Embodiment 4, and the main difference is that the process parameters of ultrasonic extraction are different.
对有机废弃物中的废金属、废塑料、废玻璃、废电池、陶瓷石块等进行分拣去杂,在分拣去杂后对其喷洒由胶冻芽孢杆菌和酵母菌组成的生物动力调控素进行生物酶解除臭。对分拣去杂生物酶解除臭后的有机废弃物,通过湿料粉碎机将其粉碎成5毫米以下颗粒。对粉碎后的有机废弃物,按干湿比1︰1的比例加水,然后通过胶体磨或锥体磨将其磨成10微米以下的浆料。在加水磨浆后的有机废弃物浆料中加入1%重量的氢氧化钾、1%重量的氢氧化镁和1%重量的过硫酸铵,通过均质乳化机在反应罐内对其进行化学裂解均质乳化。 加入氮磷钾、硅钙镁等大中微量元素再次进行均质乳化。对均质乳化后的上述混合物料,通过超声波萃取设备对其进行萃取,使其溶液中粒径小于1000纳米的含碳粒子所占的比例大于95%,超声波萃取的的频率为30KHz,功率为20KW,温度为45℃,萃取时间为60min。然后进行低温真空浓缩,使其含水量控制在50%以下,最后通过液体定量灌装机对其进行灌装,得到该液体水溶性纳米有机碳肥。Waste metal, waste plastics, waste glass, waste batteries, ceramic stones, etc. in organic waste are sorted and removed, and biodynamic regulation of Bacillus licheniformis and yeast is sprayed after sorting and removing impurities. The enzyme is used to deodorize the enzyme. The organic waste which has been deodorized by sorting the detoxification enzyme is pulverized into particles of 5 mm or less by a wet pulverizer. For the pulverized organic waste, water is added in a ratio of dry to wet ratio of 1..1, and then ground to a slurry of 10 μm or less by a colloid mill or a cone mill. Add 1% by weight of potassium hydroxide, 1% by weight of magnesium hydroxide and 1% by weight of ammonium persulfate to the organic waste slurry after water refining, and chemically liquefy it in a reaction tank by a homogenizer The cleavage is homogeneous emulsification. Adding large and medium trace elements such as NPK, silicocalcium and magnesium to homogenize emulsification again. The homogeneous mixture after emulsification is extracted by an ultrasonic extraction device, and the proportion of carbonaceous particles having a particle diameter of less than 1000 nm in the solution is greater than 95%, and the frequency of ultrasonic extraction is 30 kHz, and the power is 20 KW, temperature is 45 ° C, extraction time is 60 min. Then, it is concentrated under low temperature vacuum to control the water content to below 50%. Finally, it is filled by a liquid quantitative filling machine to obtain the liquid water-soluble nano organic carbon fertilizer.
实施例14Example 14
本实施例与实施例5基本相同,主要区别在于纳米研磨萃取的工艺参数不同。This embodiment is basically the same as Embodiment 5, and the main difference is that the process parameters of the nano-grinding extraction are different.
对有机废弃物中的废金属、废塑料、废玻璃、废电池、陶瓷石块等进行分拣去杂,然后喷洒由枯草芽孢杆菌、胶冻芽孢杆菌、酵母菌、光合细菌、纤维素酶、葡聚糖酶和木聚糖酶组成的生物动力调控素进行生物酶解除臭。除臭后通过湿料粉碎机将其粉碎成5毫米以下颗粒。粉碎后,按干湿比1︰2的比例加水,然后通过胶体磨或锥体磨将其磨成10微米以下的浆料。在加水磨浆后的有机废弃物浆料中加入2%重量的氢氧化铵和1%重量的过硫酸铵,通过均质乳化机在反应罐内对其进行化学裂解均质乳化。然后进行纳米研磨萃取,使溶液中粒径小于1000纳米的含碳粒子所占的比例大于95%。纳米研磨萃取的压力为80MPa,功率为25KW,温度为60℃,液体流量为2000L/h,过压时间5min。然后进行低温真空浓缩,使其含水量控制在50%以下,再通过真空干燥降低含水量至10%以下,最后通过固体粉料定量包装机对其进行包装,得到该固体粉状水溶性纳米有机碳肥。Disposal of scrap metal, waste plastics, waste glass, waste batteries, ceramic stones, etc. in organic waste, and then spraying by Bacillus subtilis, Bacillus licheniformis, yeast, photosynthetic bacteria, cellulase, A biodynamic regulator consisting of a glucanase and a xylanase is used to deodorize the enzyme. After deodorization, it was pulverized into particles of 5 mm or less by a wet pulverizer. After pulverization, water is added in a ratio of dry to wet ratio of 1..2, and then ground to a slurry of 10 μm or less by a colloid mill or a cone mill. 2% by weight of ammonium hydroxide and 1% by weight of ammonium persulfate were added to the organic waste slurry after water refining, and the mixture was homogenized and emulsified by chemical cracking in a reaction tank by a homogenizer. The nano-abrasive extraction is then carried out so that the proportion of carbonaceous particles having a particle size of less than 1000 nm in the solution is greater than 95%. The nano-grinding extraction pressure is 80 MPa, the power is 25 KW, the temperature is 60 ° C, the liquid flow rate is 2000 L/h, and the overpressure time is 5 min. Then, it is concentrated under low temperature vacuum to control the water content to less than 50%, and then the water content is reduced to less than 10% by vacuum drying, and finally packaged by a solid powder quantitative packaging machine to obtain the solid powdery water-soluble nano organic Carbon fertilizer.
实施例15Example 15
本实施例与实施例5基本相同,主要区别在于纳米研磨萃取的工艺参数不同。This embodiment is basically the same as Embodiment 5, and the main difference is that the process parameters of the nano-grinding extraction are different.
对有机废弃物中的废金属、废塑料、废玻璃、废电池、陶瓷石块等进行分拣去杂,然后喷洒由纤维素酶组成的生物动力调控素进行生物酶解除臭。除臭后通过湿料粉碎机将其粉碎成5毫米以下颗粒。粉碎后,按干湿比1︰2的比例加水,然后通过胶体磨或锥体磨将其磨成10微米以下的浆料。在加水磨浆后的有机废弃物浆料中加入2%重量的氢氧化铵和1%重量的过硫酸铵,通过均质乳化机在反应罐内对其进行化学裂解均质乳化。然后进行纳米研磨萃取,使溶液中粒径小于1000纳米的含碳粒子所占的比例大于95%。纳米研磨萃取的压力为70MPa,功率为15KW,温度为45℃,液体流量为1600L/h,过压时间3min。然后进行低温真空浓缩,使其含水量控制在50%以下,再通过真空干燥降低含水量至10%以下,最后通过固体粉料定量包装机对其进行包装,得到该固体粉状水溶性纳米有机碳肥。The scrap metal, waste plastic, waste glass, waste battery, ceramic stone, etc. in the organic waste are sorted and removed, and then the biodynamic regulator composed of cellulase is sprayed to carry out the biological enzyme to remove the odor. After deodorization, it was pulverized into particles of 5 mm or less by a wet pulverizer. After pulverization, water is added in a ratio of dry to wet ratio of 1..2, and then ground to a slurry of 10 μm or less by a colloid mill or a cone mill. 2% by weight of ammonium hydroxide and 1% by weight of ammonium persulfate were added to the organic waste slurry after water refining, and the mixture was homogenized and emulsified by chemical cracking in a reaction tank by a homogenizer. The nano-abrasive extraction is then carried out so that the proportion of carbonaceous particles having a particle size of less than 1000 nm in the solution is greater than 95%. The nano-abrasive extraction pressure was 70 MPa, the power was 15 KW, the temperature was 45 ° C, the liquid flow rate was 1600 L/h, and the overpressure time was 3 min. Then, it is concentrated under low temperature vacuum to control the water content to less than 50%, and then the water content is reduced to less than 10% by vacuum drying, and finally packaged by a solid powder quantitative packaging machine to obtain the solid powdery water-soluble nano organic Carbon fertilizer.
实验例1水溶性纳米有机碳肥肥效作用Experimental Example 1 Effect of Water-Soluble Nano-Organic Carbon Fertilizer
2008年6月,四川省宜宾市张姓农户50多亩正处盛产期的大棚菜椒、茄子被洪水整整淹没五天,洪水退去后,在该地区的50亩地,每十亩一组,每亩补施了25公斤本发明实施例1~5所提供的水溶性纳米有机碳肥。在另外的十亩地中每亩补施了250公斤普通有 机肥,作为对比例1。上述所有地块在被洪水淹没前均按正常栽培施足了普通有机肥和化肥。实验结果如表1所示。In June 2008, more than 50 mu of farmer households in Zhangbin, Yibin City, Sichuan Province, were inundated with greenhouse peppers and eggplants for five days. After the flood receded, in the area of 50 mu of land in the area, every 10 mu. 25 kg of the water-soluble nano organic carbon fertilizer provided in Examples 1 to 5 of the present invention was applied per acre. In the other ten acres of land, 250 kilograms per acre is applied. Machine fat, as a comparison of 1. All the above-mentioned plots were given ordinary organic fertilizer and fertilizer according to normal cultivation before being flooded. The experimental results are shown in Table 1.
表1肥效作用测试结果Table 1 results of fertilizer effect test
Figure PCTCN2017080940-appb-000001
Figure PCTCN2017080940-appb-000001
实验结果表明,施用本发明实施例所提供的水溶性纳米有机碳肥的菜地,一周后所有大棚菜椒和茄子全部恢复正常生长,之后菜地蔬菜生长良好,植株整齐,花多果多,至最后采收期结束,菜椒和茄子平均亩产量仍然高达1.1万公斤左右,如果不受灾,菜椒和茄子的平均亩产量可达1.5万公斤左右。而未采用本发明提供的水溶性纳米有机碳肥,只采用了普通有机肥的菜地,产量极低。The experimental results show that after applying the water-soluble nano-organic carbon fertilizer provided in the examples of the present invention, all the greenhouse peppers and eggplants returned to normal growth after one week, and then the vegetable vegetables grew well, the plants were neat, and the flowers were more and more. By the end of the final harvesting period, the average yield per mu of pepper and eggplant is still as high as 11,000 kg. If it is not affected, the average yield of pepper and eggplant can reach about 15,000 kg. However, the water-soluble nano-organic carbon fertilizer provided by the present invention is not used, and only the vegetable field of common organic fertilizer is used, and the yield is extremely low.
实验例2水溶性纳米有机碳肥粒径测试Experimental Example 2 Particle size test of water-soluble nano organic carbon fertilizer
本发明实施例1-5所提供的水溶性纳米有机碳肥经过总有机碳检测仪和纳米粒径检测仪检测,其有机碳(生物腐植酸)含量在21%~40%之间,有效碳EC含量在15%~29%之间;纳米粒径在800纳米以下占99%以上,900纳米以下占90%以上,1000纳米以下占100%,200纳米以下占10%以上,500纳米以下占50%以上。The water-soluble nano organic carbon fertilizer provided by the embodiments 1-5 of the invention is detected by a total organic carbon detector and a nanometer particle size detector, and the organic carbon (biohumic acid) content is between 21% and 40%, and the effective carbon is used. The EC content is between 15% and 29%; the nano-particle size is more than 99% below 800 nm, 90% or less under 900 nm, 100% below 1000 nm, and more than 10% below 200 nm, accounting for less than 500 nm. above 50.
实验例3超临界萃取的工艺参数优选 Experimental Example 3 Optimization of Process Parameters for Supercritical Extraction
实施例1和实施例6的制备方法基本相同,其区别在于超临界萃取的工艺参数不同。按照实施例1相同的制备方法制备水溶性纳米有机碳肥,区别在于超临界萃取的工艺参数不同,详见表2。The preparation methods of Example 1 and Example 6 are basically the same, except that the process parameters of the supercritical extraction are different. The water-soluble nano-organic carbon fertilizer was prepared according to the same preparation method as in Example 1, except that the process parameters of the supercritical extraction were different, as shown in Table 2.
表2超临界萃取的工艺参数Table 2 Process parameters of supercritical extraction
序号Serial number 压力(MPa)Pressure (MPa) 功率(KW)Power (KW) 温度(℃)Temperature (°C) 液体流量(L/h)Liquid flow rate (L/h) 萃取时间(min)Extraction time (min)
实施例1Example 1 2525 55 4545 10001000 4545
实施例6Example 6 8080 2525 8080 20002000 6060
对比例2Comparative example 2 23twenty three 22 4040 900900 3030
对比例3Comparative example 3 8282 2828 8383 21002100 7070
2008年6月,四川省宜宾市张姓农户50多亩正处盛产期的大棚菜椒、茄子被洪水整整淹没五天,洪水退去后,在该地区的50亩地,每十亩一组,每亩补施了25公斤本发明实施例1~5所提供的水溶性纳米有机碳肥。在另外的十亩地中每亩补施了250公斤对比例2和3所提供的水溶性纳米有机碳肥,实验结果如表3所示。In June 2008, more than 50 mu of farmer households in Zhangbin, Yibin City, Sichuan Province, were inundated with greenhouse peppers and eggplants for five days. After the flood receded, in the area of 50 mu of land in the area, every 10 mu. 25 kg of the water-soluble nano organic carbon fertilizer provided in Examples 1 to 5 of the present invention was applied per acre. The water-soluble nano-organic carbon fertilizer provided by 250 kg of the proportions 2 and 3 was applied per acre in another ten mu of land. The experimental results are shown in Table 3.
表3肥效作用测试结果Table 3 results of fertilizer effect test
Figure PCTCN2017080940-appb-000002
Figure PCTCN2017080940-appb-000002
从表3可以看出,当萃取的工艺参数不在本发明实施例所限定的范围内时,即:超临界萃取的压力为25~80MPa,功率为5~25KW,温度45~80℃,液体流量为1000~2000L/h,萃取时间45~60min,虽然对比例2和3与实施例1和6的制备过程相同,但是对比例2和3的产量仍不及本发明实施例1和6。因此,在本发明限定的工艺参数范围内,制备的出的水溶性纳米有机碳肥才具有更优良的肥效。It can be seen from Table 3 that when the extraction process parameters are not within the range defined by the embodiments of the present invention, that is, the supercritical extraction pressure is 25 to 80 MPa, the power is 5 to 25 KW, the temperature is 45 to 80 ° C, and the liquid flow rate is It was 1000 to 2000 L/h, and the extraction time was 45 to 60 min. Although Comparative Examples 2 and 3 were the same as those of Examples 1 and 6, the yields of Comparative Examples 2 and 3 were still inferior to Examples 1 and 6 of the present invention. Therefore, the prepared water-soluble nano organic carbon fertilizer has better fertilizer efficiency within the range of process parameters defined by the present invention.
同样地,按照上述思路,本发明还验证了其他萃取工艺下不同的工艺参数对水溶性纳米有机碳肥肥效的影响。经研究发现,无论选取那种萃取工艺(即,微波萃取、超声波萃取、超高压萃取和纳米研磨萃取),当对应的工艺参数均超出本发明所限定的范围时,农作物的产量均不及本发明实施例。Similarly, according to the above ideas, the present invention also verifies the effect of different process parameters on the efficiency of water-soluble nano-organic carbon fertilizer under other extraction processes. It has been found that no matter which extraction process (ie, microwave extraction, ultrasonic extraction, ultra-high pressure extraction and nano-abrasive extraction) is selected, when the corresponding process parameters are out of the scope of the present invention, the yield of the crop is inferior to the present invention. Example.
综上所述,水溶纳米有机碳肥的有机碳(生物腐植酸)含量在21%~40%之间,并且含有大量的有益微生物,易溶于土壤中及被植物吸收利用,可促进土壤团粒结构形成,提高 土壤通透性、保水性、保肥力,利于微生物的繁殖和增加,使土壤吸收养分和储存养分的能力增强,从源头上解决化肥施用次数多、量大、易流失、利用率低等问题,最终体现在作物的生长发育、产量及品质上。In summary, the water-soluble nano-organic carbon fertilizer has an organic carbon (biohumic acid) content of 21% to 40%, and contains a large number of beneficial microorganisms, is easily soluble in the soil and is absorbed and utilized by plants, and can promote soil agglomeration. Structure formation, improvement Soil permeability, water retention, and fertility are beneficial to the reproduction and increase of microorganisms, which enhances the ability of the soil to absorb nutrients and store nutrients. From the source, it solves the problems of frequent application of chemical fertilizers, large quantity, easy loss, and low utilization rate. Ultimately reflected in the growth, yield and quality of crops.
应用本发明所生产的水溶纳米有机碳肥,其所含的有机碳(生物腐植酸)是经过生物、化学、物理多种作用后生产出来的,不同于一般有机肥中的有机碳(生物腐植酸)。因为本发明已经把一切有机废弃物的成分完全彻底转化成了简单、易溶于水的物质,更容易被植物摄取。The water-soluble nano organic carbon fertilizer produced by the invention has the organic carbon (biohumic acid) produced by biological, chemical and physical effects, and is different from the organic carbon in the general organic fertilizer (biohumus) acid). Because the present invention has completely converted all the components of organic waste into simple, water-soluble substances, it is more easily taken up by plants.
尽管已用具体实施例来说明和描述了本发明,然而应意识到,在不背离本发明的精神和范围的情况下可以作出许多其它的更改和修改。因此,这意味着在所附权利要求中包括属于本发明范围内的所有这些变化和修改。 While the invention has been illustrated and described with reference to the embodiments of the present invention, it will be understood that many modifications and changes can be made without departing from the spirit and scope of the invention. Accordingly, it is intended to embrace in the appended claims

Claims (20)

  1. 一种水溶性纳米有机碳肥的制备方法,其特征在于,包括以下步骤:A method for preparing a water-soluble nano organic carbon fertilizer, comprising the steps of:
    在有机废弃物中加入生物动力调控素进行生物酶解除臭,然后进行粉碎,粉碎后加水进行磨浆,在磨浆后得到有机废弃物浆料中加入化学催化裂解剂,并进行均质乳化处理,然后进行纳米萃取处理,再经过浓缩和干燥,得到该水溶性纳米有机碳肥;The bio-dynamic regulator is added to the organic waste to remove the odor by the biological enzyme, and then pulverized, pulverized, and then water is added for refining. After the refining, the chemical waste cracking agent is added to the organic waste slurry, and the homogeneous emulsification treatment is performed. And then performing nano-extraction treatment, and then concentrating and drying to obtain the water-soluble nano organic carbon fertilizer;
    优选的,所述生物动力调控素包括枯草芽孢杆菌、胶冻芽孢杆菌、酵母菌、光合细菌、纤维素酶、葡聚糖酶和木聚糖酶中的一种或几种的组合;Preferably, the biodynamic regulator comprises a combination of one or more of Bacillus subtilis, Bacillus licheniformis, yeast, photosynthetic bacteria, cellulase, glucanase and xylanase;
    优选的,所述化学催化裂解剂包括氢氧化物和过氧化物中的一种或者两种的组合;Preferably, the chemical catalytic cracking agent comprises one or a combination of a hydroxide and a peroxide;
    更优选的,所述氢氧化物包括氢氧化铵、氢氧化钾、氢氧化钠、氢氧化钙和氢氧化镁中的一种或者几种的组合,所述过氧化物包括过硫酸钾和过硫酸铵中的一种或者两种。More preferably, the hydroxide comprises one or a combination of ammonium hydroxide, potassium hydroxide, sodium hydroxide, calcium hydroxide and magnesium hydroxide, the peroxide comprising potassium persulfate and One or two of ammonium sulfate.
  2. 根据权利要求1所述的水溶性纳米有机碳肥的制备方法,其特征在于,所述有机废弃物包括:工业有机废水、农业有机废弃物和城镇生活垃圾中的一种或几种组合。The method for preparing a water-soluble nano organic carbon fertilizer according to claim 1, wherein the organic waste comprises one or a combination of industrial organic wastewater, agricultural organic waste, and municipal solid waste.
  3. 根据权利要求1所述的水溶性纳米有机碳肥的制备方法,其特征在于,所述在有机废弃物中加入生物动力调控素之前,还包括以下步骤:去除有机废弃物中夹杂的无机固体和塑料。The method for preparing a water-soluble nano-organic carbon fertilizer according to claim 1, wherein the step of adding the biodynamic regulator to the organic waste further comprises the steps of: removing the inorganic solids contained in the organic waste and plastic.
  4. 根据权利要求1所述的水溶性纳米有机碳肥的制备方法,其特征在于,所述粉碎的过程,具体包括以下步骤:将生物酶解除臭后的有机废弃物粉碎至粒径小于5毫米的颗粒;The method for preparing a water-soluble nano-organic carbon fertilizer according to claim 1, wherein the pulverizing process comprises the following steps: pulverizing the organic waste deodorized by the biological enzyme to a particle diameter of less than 5 mm. Granule
    优选的,所述颗粒的粒径小于3毫米;Preferably, the particles have a particle size of less than 3 mm;
    更优选的,所述粉碎采用湿料粉碎机进行操作。More preferably, the pulverization is carried out using a wet pulverizer.
  5. 根据权利要求1所述的水溶性纳米有机碳肥的制备方法,其特征在于,所述加水进行磨浆的过程,具体包括以下步骤:在所述粉碎后的有机废弃物中加入其质量1~2倍的水,磨浆至得到的浆料的粒径小于10微米,优选的料浆的粒径小于5微米;The method for preparing a water-soluble nano-organic carbon fertilizer according to claim 1, wherein the step of adding water for refining comprises the following steps: adding the mass 1 to the pulverized organic waste. 2 times of water, refining until the obtained slurry has a particle size of less than 10 microns, and the preferred slurry has a particle size of less than 5 microns;
    更优选的,所述磨浆采用通过胶体磨或锥体磨进行操作。More preferably, the refining is operated by a colloid mill or a cone mill.
  6. 根据权利要求1所述的水溶性纳米有机碳肥的制备方法,其特征在于,所述化学催化裂解剂与所述料浆的质量比为(1~2):100。The method for preparing a water-soluble nano organic carbon fertilizer according to claim 1, wherein a mass ratio of the chemical catalytic cracking agent to the slurry is (1 to 2): 100.
  7. 根据权利要求1所述的水溶性纳米有机碳肥的制备方法,其特征在于,所述纳米萃取包括:超临界萃取、微波萃取、超声波萃取、超高压萃取和纳米研磨萃取的一种或者几种的组合;The method for preparing a water-soluble nano-organic carbon fertilizer according to claim 1, wherein the nano-extraction comprises one or more of supercritical extraction, microwave extraction, ultrasonic extraction, ultrahigh pressure extraction and nano-abrasive extraction. The combination;
    优选的,在所述纳米萃取处理之前,还包括:加入化肥;Preferably, before the nano-extraction treatment, the method further comprises: adding a fertilizer;
    优选的,所述纳米萃取的溶剂为无机溶剂,所述纳米萃取的次数为1~2次;更优选的,所述溶剂为水或二氧化碳;Preferably, the solvent for the nano-extraction is an inorganic solvent, and the number of times of the nano-extraction is 1-2 times; more preferably, the solvent is water or carbon dioxide;
    优选的,所述纳米萃取处理后,溶液中粒径小于1000纳米的含碳粒子所占的比例大于 95%。Preferably, after the nano-extraction treatment, the proportion of carbon-containing particles having a particle diameter of less than 1000 nm in the solution is greater than 95%.
  8. 根据权利要求7所述的水溶性纳米有机碳肥的制备方法,其特征在于,所述超临界萃取的压力为25~80MPa,功率为5~25KW,温度45~80℃,液体流量为1000~2000L/h,萃取时间45~60min;The method for preparing a water-soluble nano organic carbon fertilizer according to claim 7, wherein the supercritical extraction has a pressure of 25 to 80 MPa, a power of 5 to 25 KW, a temperature of 45 to 80 ° C, and a liquid flow rate of 1000 ~. 2000L / h, extraction time 45 ~ 60min;
    所述微波萃取的频率为300~915MHz,功率为5~25KW,温度为35~80℃,反应罐容积为1000~3000L或液体流量为1000~3000L/h,萃取时间45~60min;The frequency of the microwave extraction is 300-915 MHz, the power is 5-25KW, the temperature is 35-80 ° C, the volume of the reaction tank is 1000-3000 L or the liquid flow rate is 1000-3000 L/h, and the extraction time is 45-60 min;
    所述超声波萃取的频率为20~50KHz,功率为5~25KW,温度为30~60℃,反应罐容积为1000~3000L或液体流量为1000~3000L/h,萃取时间45~60min;The ultrasonic extraction frequency is 20 to 50 KHz, the power is 5 to 25 KW, the temperature is 30 to 60 ° C, the reaction tank volume is 1000 to 3000 L or the liquid flow rate is 1000 to 3000 L/h, and the extraction time is 45 to 60 min;
    所述超高压萃取的压力为250~380MPa,功率为5~25KW,温度为30-60℃,液体流量为1000~2000L/h,过压时间2~5min;The ultrahigh pressure extraction has a pressure of 250 to 380 MPa, a power of 5 to 25 KW, a temperature of 30 to 60 ° C, a liquid flow rate of 1000 to 2000 L/h, and an overpressure time of 2 to 5 min;
    所述纳米研磨萃取的压力为50~80MPa,功率为5~25KW,温度为30-60℃,反应罐容积为100~500L或液体流量为1000~5000L/h,过压时间2~5min。The nano-abrasive extraction pressure is 50-80 MPa, the power is 5-25 KW, the temperature is 30-60 ° C, the reaction tank volume is 100-500 L or the liquid flow rate is 1000-5000 L/h, and the over-pressure time is 2-5 min.
  9. 一种根据权利要求1-8任一项所述的水溶性纳米有机碳肥的制备方法所制备的水溶性纳米有机碳肥40阿斯蒂芬。A water-soluble nano organic carbon fertilizer 40 astep prepared by the method for preparing a water-soluble nano organic carbon fertilizer according to any one of claims 1-8.
  10. 根据权利要求9所述的水溶性纳米有机碳肥,其特征在于,在所述水溶性纳米有机碳肥中,含碳粒子的粒径小于800纳米的颗粒达到99%以上。The water-soluble nano organic carbon fertilizer according to claim 9, wherein in the water-soluble nano organic carbon fertilizer, particles having a particle diameter of less than 800 nm of carbon-containing particles are more than 99%.
  11. 一种水溶性纳米有机碳肥,其特征在于,其是由权利要求1-8中任一项所述的制备方法制备而成的。A water-soluble nanoorganic carbon fertilizer prepared by the production method according to any one of claims 1-8.
  12. 一种有机复合肥,其特征在于,包括水溶性纳米有机碳肥和无机化肥,所述水溶性纳米有机碳肥由以下步骤制备而成:将经生物动力调控素进行生物酶接除臭后的有机废弃物制备成有机废弃物浆料;向所述有机废弃物浆料中加入化学催化裂解剂;对所述有机废弃物浆料进行均质乳化处理;将所述有机废弃物浆料进行纳米萃取处理;以及浓缩和干燥。An organic compound fertilizer characterized in that it comprises a water-soluble nano organic carbon fertilizer and an inorganic fertilizer, and the water-soluble nano organic carbon fertilizer is prepared by the following steps: after bio-enzyme coupling and deodorization by biodynamic regulator The organic waste is prepared into an organic waste slurry; a chemical catalytic cracking agent is added to the organic waste slurry; the organic waste slurry is subjected to homogeneous emulsification treatment; and the organic waste slurry is subjected to nanometer Extraction treatment; and concentration and drying.
  13. 根据权利要求12所述的有机复合肥,其特征在于,所述生物动力调控素包括枯草芽孢杆菌、胶冻芽孢杆菌、酵母菌、光合细菌、纤维素酶、葡聚糖酶和木聚糖酶中的一种或几种的组合。The organic compound fertilizer according to claim 12, wherein the biodynamic regulator comprises Bacillus subtilis, Bacillus licheniformis, yeast, photosynthetic bacteria, cellulase, glucanase, and xylanase. One or a combination of several.
  14. 根据权利要求12所述的有机复合肥,其特征在于,所述化学催化裂解剂与所述料浆的质量比为(1~2):100,所述化学催化裂解剂包括氢氧化物和过氧化物中的一种或者两种的组合。The organic compound fertilizer according to claim 12, wherein a mass ratio of said chemical catalytic cracking agent to said slurry is (1 to 2): 100, and said chemical catalytic cracking agent comprises hydroxide and One or a combination of two of the oxides.
  15. 根据权利要求14所述的有机复合肥,其特征在于,所述氢氧化物包括氢氧化铵、氢氧化钾、氢氧化钠、氢氧化钙和氢氧化镁中的一种或者几种的组合。The organic compound fertilizer according to claim 14, wherein the hydroxide comprises one or a combination of ammonium hydroxide, potassium hydroxide, sodium hydroxide, calcium hydroxide and magnesium hydroxide.
  16. 根据权利要求14所述的有机复合肥,其特征在于,所述过氧化物包括过硫酸钾和 过硫酸铵中的一种或者两种。The organic compound fertilizer according to claim 14, wherein said peroxide comprises potassium persulfate and One or two of ammonium persulfate.
  17. 根据权利要求12所述的有机复合肥,其特征在于,制备所述有机废弃物浆料包括:在有机废弃物中加入生物动力调控素之前,去除有机废弃物中夹杂的无机固体和塑料;将生物酶解除臭后的有机废弃物粉碎至粒径小于5毫米的颗粒;以及将粉碎后的有机废弃物加入其质量1-2倍的水,磨浆至得到的浆料的粒径小于10微米。The organic compound fertilizer according to claim 12, wherein the preparation of the organic waste slurry comprises: removing inorganic solids and plastics contained in the organic waste before adding the biodynamic regulator to the organic waste; The organic waste deodorized organic waste is pulverized to particles having a particle diameter of less than 5 mm; and the pulverized organic waste is added to water having a mass of 1-2 times, and the slurry is refined to a particle size of less than 10 μm. .
  18. 根据权利要求12所述的有机复合肥,其特征在于,所述纳米萃取包括:超临界萃取、微波萃取、超声波萃取、超高压萃取和纳米研磨萃取的一种或者几种的组合。The organic compound fertilizer according to claim 12, wherein the nano-extraction comprises one or a combination of supercritical extraction, microwave extraction, ultrasonic extraction, ultrahigh pressure extraction, and nano-abrasive extraction.
  19. 根据权利要求18所述的有机复合肥,其特征在于,所述纳米萃取的溶剂为无机溶剂。The organic compound fertilizer according to claim 18, wherein the nano-extraction solvent is an inorganic solvent.
  20. 根据权利要求18所述的有机复合肥,其特征在于,经所述纳米萃取后,制得的水溶性纳米有机碳肥中,含碳粒子的粒径小于800纳米的颗粒达到99%以上。 The organic compound fertilizer according to claim 18, wherein, in the water-soluble nano-organic carbon fertilizer obtained by the nano-extraction, particles having a particle diameter of less than 800 nm of carbon-containing particles are more than 99%.
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