TW201524939A - A bio-stabilized fertilizer and a method for producing thereof - Google Patents

Abstract

The present invention relates to a bio-stabilized fertilizer, characterized by an organic waste material; a microbial inoculant; and an inorganic compound. The present invention also provides a method for producing a bio-stabilized fertilizer, characterized by the steps of air drying the organic waste material; decomposing the organic waste material to form a compost; inoculating the compost with the microbial inoculant; mixing the inoculated compost with the inorganic compound to form a powder mixture; crushing the powder mixture and pelletizing the crushed powder mixture to form a fertilizer pellet; and cooling the fertilizer pellet.

Description

Bio-stabilized fertilizer and method for producing same

This invention relates to a fertilizer, and more particularly to a method of producing fertilizer from organic waste.

Successful production of plants, including crops, flowers, saplings, etc., involves optimizing soil fertility for production and maturity. It is also hoped that the soil fertility and structure will be maintained for a long time. Animal manure has been used as a source of nutrition since ancient times. The use of animal manure also provides good soil tilting and structure. However, the disadvantage is that animal manure has a relatively low nutritional value, including a non-stable form that readily leaches out plant nutrients, and if the manure is applied as a feedstock, the soil must provide nutrients for the microorganisms involved in the manure degradation process. This can lead to nutrient deficiencies in the soil where the crops are grown.

The soil area adjacent to the root of the plant is called the rhizosphere. The rhizosphere usually coexists with many prokaryotes and eukaryotes that depend on life or symbiosis forever; all provide essential nutrients for nourishing plants. However, the microbes in the rhizosphere are diverse and have many harmful organisms, ie pathogens, which are also fed to the roots of the plant and fed to the rhizosphere. By feeding on their own, at the root of the plant, the pest competes with the plant for nutrients, thus causing the plant to become malnourished. In the case of crop cultivation, this malnutrition causes a large amount of crop loss. Composting is a common method used to reuse organic waste. Composting reduces the volume of organic materials and stabilizes potential nutrients in compost, especially It is nitrogen. Composting reduces environmental pollution and typically significantly reduces the amount of recyclable organic material that requires additional processing methods, which are typically dumped to landfills. During the composting process, carbon and nitrogen-containing compounds in organic materials are converted into a more stable complex type by a continuous microbial population, which is chemically and biologically similar to humic plant matter.

CN 1690020 A relates to a compound fertilizer, in particular to a composite active organic, inorganic, and biochemical fertilizer capable of regulating trace elements. The compound fertilizer is composed of more than 4 wt% of organic matter, 15-40 wt% of nitrogen fertilizer solution, 10-20 wt% of phosphate solution, 7-15 wt% of potash fertilizer, 4-8 wt% of medium and trace amount. Element, and appropriate amount of additives. The medium amount elements include Ca, Mg and S; the trace elements include Fe, Zn, Mo, Cl, B and Cu; and the additive is a disinfectant. The complex may have different nutrients and concentrations to meet plant growth requirements and may also be used by mixing other fertilizers. However, the production of fertilizers in the form of pellets or granules as time-release capsules is desirable to allow nutrients to flow out over time rather than the manner in which nutrients such as the liquid fertilizer in CN 1690020 A are filled with plants.

WO 2001000011 A1 discloses a process for producing pure organic fertilizer pellets. Organic materials such as composite waste or materials considered to be organic standards are collected and converted into bio-stabilized complexes having known amounts of nitrogen, phosphorus, potassium and water. This composite is further sieved to provide fine particles having a size of 150 microns or less. The fines are compressed and pelletized to reduce premature dissolution and maximize plant nutrient retention to promote plant growth.

Another method, for example, DE 102004017876 A1, discloses a process for preparing solid fertilizers by mixing vinasse with organic and/or inorganic solids and by subsequent agglomeration. Solid fertilizers can be produced in the form of granules or pellets. However, in the two cited prior art, such as WO 2001000011 A1 and DE 102004017876 A1, there is a lack of fertilizer in the fertilizer to assist the nutrient cycle and Controlling the presence of beneficial microorganisms of plants or crop pathogens.

Thus, it appears in the prior art that there is a need to provide a method of combining organic matter, plant nutrients, and injecting microorganisms to produce a bio-stabilized pathogen-free fertilizer to promote plant growth and crop yield.

The object of the present invention is to provide fertilizer pellets from composite waste.

It is also an object of the present invention to provide a method of producing a fertilizer pellet by converting the waste into a microparticle of a bio-anhydrous complex.

Another object of the present invention is to provide a mixture of organic matter, plant nutrients, and injected microorganisms and subject to a pelletizing process to provide a pelletized biochemical fertilizer.

Accordingly, such objectives can be achieved by the following teachings of the present invention. The present invention relates to a bio-stabilized fertilizer characterized by comprising organic waste; a microbial inoculant; wherein the microbial inoculum comprises Azotobacter vinelandii , Azotobacter chroococcum , Azospirillum lipoferum ), Pseudomonas fluorescens , Pseudomonas putida , Bacillus subtilis , Bacillus megaterium , Bacillus firmus , or a combination thereof; And inorganic compounds. The invention also provides a method for producing a bio-stabilized fertilizer, characterized by the steps of: drying organic waste; decomposing organic waste to form a composite; and inoculating the microbial inoculum; and inoculating the composite with the inorganic compound Forming a powder mixture; pulverizing the powder mixture and pelletizing the pulverized powder mixture to form a fertilizer pellet; and cooling the fertilizer pellet.

The features of the present invention will become more apparent from the following detailed description when read in conjunction with the accompanying drawings. A chart of experimental results of growing corn.

The detailed description of the present invention is set forth in the claims of the claims. Therefore, the details of specific structures and functions disclosed herein are not to be construed as a limitation. It is to be understood that the invention is not intended to be in the And alternatives. As used throughout this application, the term "may" is used in a permissible sense (ie, having a potential meaning) rather than a forced meaning (ie, meaning necessary). Similarly, the words "include," "include" and "include" are meant to include but not limiting. Also, "a" or "an" means "at least one" and "the plural" means one or more unless otherwise indicated. Where abbreviations or technical terms are used, these denote the commonly accepted meanings as are known in the art. The invention will now be described with reference to Figure 1.

The present invention relates to a bio-stabilized fertilizer characterized by comprising: organic waste; microbial inoculum; wherein the microbial inoculum comprises Azotobacter vinelandii , Azotobacter chroococcum , and Azospirillum. Lipoferum ), Pseudomonas fluorescens , Pseudomonas putida , Bacillus subtilis , Bacillus megaterium , Bacillus firmus , or any a composition; and an inorganic compound.

In a preferred embodiment of the bio-stabilized fertilizer, the organic waste comprises a cocoa shell, a coffee grounds, a decanter cake, a bleaching earth, a palm kernel extract, an organic plant. An extract, an empty fruit bunch, a palm oil mill effluent, a rice bran, a rice husk, or a combination thereof.

A preferred embodiment of this bio-stabilized fertilizer is a ratio of 1-20% (v/w).

A preferred embodiment of this bio-stabilized fertilizer is in the range of 1 x 10 ² to 1 x 10 ¹² CFU ml ^-1 .

In a preferred embodiment of the bio-stabilized fertilizer, the inorganic compound comprises urea, ammonium chloride, ammonium sulfate, diammonium phosphate, ammonium nitrate phosphate, rock phosphate, potassium chloride ( Muriate of potash), sulphate of potash, borax, magnesia, kieserite, dolomite, zeolite, or combinations thereof.

The invention also provides a method for producing a bio-stabilized fertilizer, characterized by comprising the steps of: air drying organic waste; decomposing organic waste to form a composite; and inoculating the composite with a microbial inoculum; The inoculated complex is mixed with an inorganic compound to form a powder mixture; the powder mixture is crushed and the crushed powder mixture is pelletized to form a fertilizer pellet; and the fertilizer pellet is cooled.

In a preferred embodiment of the method for pelletizing a biologically stabilized fertilizer, the organic waste is subjected to aerobic decomposition in a solid state fermentation at a flow rate of 10-25 m ³ min ^-1 and a rotational speed of 30-100 rpm.

The following are examples of bio-stabilized fertilizer pellets and methods of producing the same, whereby the advantages of the present invention are more readily understood. It is to be understood that the following examples are merely illustrative and are not to be construed as limiting the invention in any way.

Example

A bio-stabilized fertilizer comprising organic waste, microbial inoculants, and chemical compounds. The bio-stabilized fertilizer is preferably in the form of pellets, granules, troches, or powders.

In a preferred embodiment, organic waste is provided and air dried in a greenhouse. The organic waste is preferably organic waste derived from plants, including cocoa shell, coffee grounds, pomace, clay, palm kernel extract, organic plant extract, empty fruit bunch, palm oil grinding waste, rice bran, rice husk, Or a composition thereof. The organic waste was then sieved using a 3-10 mesh vibrating screen.

In a preferred embodiment, the organic waste is then premixed with other organic waste at the following concentrations. For example, a mixture of organic wastes comprises an exemplary concentration of 0-95% (w/w) of cocoa shell, an exemplary concentration of 0-95% (w/w) coffee grounds, and a simulated concentration of 0-99.5% (w/w). Slag, demonstration clay with 0-50% (w/w) concentration, palm kernel extract with a concentration of 0-95% (w/w), organic plant extract with a concentration of 0-95% (w/w), Demonstration concentration 0-75% (w/w) of empty fruit bunches, demonstration concentration 0-95% (w/w) palm oil ground waste, 0-95% (w/w) rice bran, and 0-95% (w/w) rice husk. In a preferred embodiment, the organic waste is then incubated at ambient temperature for 1 to 4 weeks.

This organic waste is then transferred to the solid fermentation zone. The organic waste is decomposed in solid state fermentation for 7 to 45 days to form a stable pathogen-free complex. This solid state fermentation zone is equipped with a blower and a top rotator. Preferably, 9 to 40 blowers evenly distribute the entire solid state fermentation zone. The aeration amount of the decomposition process is preferably in the range of 10-25 m ³ min ^-1 . The organic waste in the solid state fermentation zone was continuously and thoroughly mixed using a top rotator at a rotational speed of 30-100 rpm.

In a preferred embodiment, the solid state fermentation zone comprises from 8 to 15 fermentation lines. This top rotator takes about one hour to complete the mixing in a fermentation line and then moves to the next fermentation line. The completion of this decomposition process is indicated by the temperature of the composite. Preferably, the complex at a temperature below 40 °C is removed from the solid state fermentation zone and used in a microbial inoculation process. This complex is collected and inoculated with a microbial inoculum, preferably in a 1-20% (v/w) ratio. This complex acts as a carrier and as a source of nutrients for microbial inoculants. In addition, this complex is also used to promote water and nutrients to stay in the soil.

In a preferred embodiment, the microbial inoculum is sprayed onto the composite using an automatic sprayer. The microbial inoculum comprises Azotobacter vinelandii , Azotobacter chroococcum , Azospirillum lipoferum , Pseudomonas fluorescens , Pseudomonas Putida ), Bacillus subtilis , Bacillus megaterium , Bacillus firmus , or a combination thereof. Each strain of the microbial inoculum has an amount of 1 x 10 ² to 1 x 10 ¹² CFU ml ^-1 . Table 1 shows colony-forming units (CFU) of each strain of the microbial inoculum and is a specific example exemplified in the present invention.

This inoculated complex is then mixed with an inorganic compound using a spiral mixer to form a powder mixture. The inorganic compound comprises urea, ammonium chloride, ammonium sulfate, diammonium phosphate, ammonium phosphate phosphate, phosphate rock, potassium chloride, potassium sulfate, borax, magnesium oxide, magnesium sulphate, dolomite, zeolite, or a combination thereof . Table 2 shows the inorganic compounds of the specific examples exemplified in the present invention and their functions.

The powder mixture was crushed using a hammer mill at a rate of 1-10 rpm, followed by sieving using a vibrating or rotating screen with 3-10 mesh. This powder mixture is then subjected to a pelletizing process to form fertilizer pellets. In a preferred embodiment, the screened powder mixture is pelletized at a rate of from 1.5 to 10 metric tons per hour using a ring die granulator having a plurality of orifices having a diameter in the range of from 0.5 mm to 10 mm. The resulting fertilizer pellets are then cooled to a final temperature of 30 ° C to 40 ° C prior to packaging in a cooling chamber at 4 ° C to 15 ° C. In a preferred embodiment, the fertilizer pellets preferably have a length of from 5 mm to 20 mm and a diameter of from 2 mm to 7.5 mm.

In a preferred embodiment, the resulting bio-stabilized fertilizer is formulated into different ratios of nitrogen, phosphorus, and potassium oxide (NPK) and different concentrations of microbial inoculum are added to promote plant growth. Table 3 presents the experimental design used to grow corn.

Referring to Table 3, five treatment zones, namely A, B, C, D, E, and F, are provided for this experiment. Corn crops are available in all districts. Zone A served as a control group and corn was not treated; Zone B was treated with the preferred ratio of commercially available NPK fertilizers listed in Table 3. Zone E is treated only with urea. The bio-stabilized fertilizer of the present invention was tested on corn in the C, D and F zones. In a preferred embodiment, the bio-stabilized fertilizer is formulated to a preferred NPK ratio of 5:5:5, 11:11:11, and 8:8:20. In the D and F areas, bio-solidified fertilizers for corn processing are formulated as microbial inoculants with high concentrations of nitrogen fixation, such as Azotobacter vinelandii and Azotobacter chroococcum .

In a preferred embodiment, the treatment zones have 5 treatments applied to the corn. Treatments applied to each zone were continuously treated with corn at predetermined intervals of application as indicated in Table 3.

Table 4 presents exemplary compositions of bio-stabilized fertilizers which were formulated at preferred NPK ratios of 5:5:5, 11:11:11, and 12:12:17, respectively. The microbial inoculum contained in the bio-stabilized fertilizer comprises Azotobacter vinelandii , Azotobacter chroococcum , Azospirillum lipoferum , Pseudomonas fluorescens , and odor Pseudomonas putida , Bacillus subtilis , Bacillus megaterium , and Bacillus firmus .

Experimental result

Referring to Figure 1, the D zone treatment yielded the highest grain yield and biomass yield of 8775.1 kg ha ^-1 and 21776.71 kg ha ^-1 , respectively, compared to the A, B and E zones. In conclusion, the treatment of the bio-stabilized fertilizer (refer to Tables C, D and F) of the present invention showed an increase in biomass and glutinous grain yield compared to the treatment of zones A, B and E.

Although the present invention has been described with reference to the specific embodiments thereof, it is apparent to those skilled in the art that many variations and modifications can be made in the scope of the present invention as defined in the specification and the scope of the following claims.

Claims (7)

A bio-stabilized fertilizer characterized by comprising: organic waste; a microbial inoculant; wherein the microbial inoculum comprises Azotobacter vinelandii , Azotobacter chroococcum , Azospirillum lipoferum , Pseudomonas fluorescens , Pseudomonas putida , Bacillus subtilis , Bacillus megaterium , Bacillus firmus , or combinations thereof; Compound. The bio-stabilized fertilizer of claim 1, wherein the organic waste comprises cocoa shell, coffee grounds, pomace, clay, palm kernel extract, organic plant extract, empty fruit bunch, palm oil grinding waste, rice bran, rice husk, Or a composition thereof. The bio-stabilized fertilizer of claim 1, wherein the ratio of the microbial inoculum is 1-20% (v/w). The bio-stabilized fertilizer of claim 1, wherein the microbial inoculant is in the range of 1 x 10 ² to 1 x 10 ¹² CFU ml ^-1 . The bio-stabilized fertilizer of claim 1, wherein the inorganic compound comprises urea, ammonium chloride, ammonium sulfate, diammonium phosphate, ammonium nitrate phosphate, rock phosphate, and muriate of Potash), sulphate of potash, borax, magnesia, kieserite, dolomite, zeolite, or combinations thereof. A method for producing a bio-stabilized fertilizer according to claim 1, characterized by comprising the steps of: air drying the organic waste; decomposing the organic waste to form a composite; inoculating the composite with a microbial inoculum; mixing the inoculated complex with The inorganic compound is formed to form a powder mixture; the powder mixture is crushed and the crushed powder mixture is pelletized to form a fertilizer pellet; and the fertilizer pellet is cooled. A method of pelletizing a bio-stabilized fertilizer according to claim 6, wherein the organic waste is decomposed by aerobic in a solid-state fermentation having a range of aeration of 10-25 m ³ min ^-1 and a rotational speed of 30-100 rpm.