Disclosure of Invention
In view of the above technical problems, a first object of the present invention is to provide a method for preparing a human excrement hydrothermal carbon-based coated urea fertilizer, and a second object of the present invention is to provide a human excrement hydrothermal carbon-based coated urea fertilizer obtained thereby. The high-strength chromium-contaminated soil remediation agent has high compressive strength and good wear resistance, improves the utilization rate of the fertilizer, and can realize remediation of chromium-contaminated soil.
In order to achieve the first purpose, the invention provides a preparation method of a carbon-based coated urea fertilizer prepared from human excrement and water, which is characterized by comprising the following steps:
1) preparing hydrothermal carbon, namely taking the excrement slag at the bottom of the first tank of the three-grid septic tank, naturally drying, crushing and sieving, then adding into a hydrothermal reaction kettle, setting the heating rate to be 8-12 ℃/min, carrying out hydrothermal reaction, pouring out supernatant after the reaction is finished, washing the mixture to be neutral by using deionized water, carrying out freeze drying, and grinding to obtain the hydrothermal carbon;
2)Fe3O4hydrothermal carbon preparation, dispersing the prepared hydrothermal carbon in ethylene glycol, and then adding FeCl3·6H2Dissolving O, adding anhydrous sodium acetate, stirring to mix thoroughly, ultrasonic dispersing, transferring to a reaction kettle, sealing for reaction, taking out, cooling, and magnetically separating out Fe3O4Hydrothermal charcoal, washing, freeze drying, grinding to obtain Fe3O4Hydrothermal charcoal, Fe3O4The mass fraction of (A) is 10% -25%;
3) preparing a hydrothermal carbon-based urea fertilizer: weighing r-polyglutamic acid, dissolving into glacial acetic acid water solution to obtain binder, pulverizing urea, sieving, weighing urea, placing into a granulator, starting the granulator, spraying binder during rotation, and slowly spraying Fe3O4And/or hydrothermal carbon, taking out after the particles are formed, drying to constant weight, and cooling to obtain the product.
In the step 1), the reaction is respectively kept at 140 ℃, 180 ℃ and 220 ℃ for 30-40min during the reaction.
In the step 1), the ratio of the human excrement slag to water added into the hydrothermal reaction kettle is 15-20g of the human excrement slag added into each 100mL of water.
In the step 2), the reaction temperature is 200-250 ℃.
In the scheme, the mass concentration of the r-polyglutamic acid solution is 0.1-0.3%.
In the above scheme, the volume concentration of glacial acetic acid in the glacial acetic acid aqueous solution is 1%.
In the above scheme, Fe3O4The mass ratio of the hydrothermal carbon to the urea is 0.2-0.3: 1.
In the scheme, the excrement residue and the urea are crushed and then are sieved by a 50-100-mesh sieve.
The second object of the present invention is achieved by: the human excrement hydrothermal carbon-based coated urea fertilizer is prepared by the preparation method of the human excrement hydrothermal carbon-based coated urea fertilizer.
The invention takes gamma-polyglutamic acid as a binder and Fe3O4The modified hydrothermal carbon-based urea fertilizer is prepared by using hydrothermal carbon as a carrier. Gamma-PGA (Gamma-PGA) has super-strong hydrophilicity, and water molecules can form a film on the surface of the Gamma-PGA to slow down the direct contact of the Gamma-PGA with the outside. Fe3O4The nano particles have paramagnetism, high specific surface area and active surface anchoring and adsorbing functional molecules, and change the characteristics of unstable granulation structure, poor water resistance and instant dispersion when meeting water of single hydrothermal carbon coated urea. The invention takes gamma-polyglutamic acid as a binder to construct Fe3O4The hydrothermal carbon-based urea fertilizer fully utilizes the characteristics of hydrophilicity, spatial structure and the like of r-polyglutamic acid to improve the efficient absorption of nutrients by crops, and simultaneously skillfully utilizes the advantages of high specific surface area, magnetic separation and the like of the modified hydrothermal carbon to achieve a good slow release effect, so that the yield of the crops can be improved by more than 25 percent compared with the common urea. Meanwhile, hexavalent chromium in the chromium-polluted soil can be converted into trivalent chromium with lower toxicity, and the chromium-polluted soil can be repaired.
Detailed Description
The invention is further illustrated by the following examples:
example 1
A preparation method of a human excrement hydrothermal carbon-based coated urea fertilizer comprises the following steps:
1) preparing hydrothermal carbon, taking the excrement residue at the bottom of the first tank of the three-grid septic tank, naturally drying, crushing, sieving by a 50-100 mesh sieve, and then adding into a hydrothermal reaction kettle, wherein 15g of human excrement residue is added into every 100mL of water. Setting the heating rate to be 8 ℃/min, carrying out hydrothermal reaction, respectively staying at 140 ℃, 180 ℃ and 220 ℃ for 30min, pouring out supernatant after the reaction is finished, washing the mixture to be neutral by deionized water, freezing and drying the mixture, and grinding the mixture to obtain the hydrothermal carbon.
2)Fe3O4Hydrothermal charcoal preparation, dispersing 10g of the prepared hydrothermal charcoal in 30mL of ethylene glycol, and then adding FeCl3·6H2Dissolving O, adding 5mL of anhydrous sodium acetate, stirring to fully mix, ultrasonically dispersing for 20min, transferring to a reaction kettle, sealing and reacting at 250 ℃ for 2h at 200-3O4Hydrothermal charcoal, washing, freeze drying, grinding to obtain Fe3O4Hydrothermal charcoal, Fe3O4Is 25 percent.
3) Preparing a hydrothermal carbon-based urea fertilizer: weighing 1g r-polyglutamic acid, dissolving to 1% (V/V) glacial acetic acid water solution to obtain adhesive, wherein the mass concentration of r-polyglutamic acid solution is 0.1%, pulverizing urea by a pulverizer, sieving with a 50-100 mesh sieve, weighing urea, placing in a granulator, starting the granulator, setting the rotation speed at 40r/min, spraying binder during rotation, and slowly spraying Fe3O4Hydrothermal charcoal, Fe3O4The mass ratio of the hydrothermal carbon to the urea is 0.2:1, the granules are taken out after being formed, dried to constant weight at 40 ℃, and cooled to obtain the product.
Example 2
A preparation method of a human excrement hydrothermal carbon-based coated urea fertilizer comprises the following steps:
1) preparing the hydrothermal carbon, taking the excrement residue at the bottom of the first tank of the three-grid septic tank, naturally drying, crushing, sieving by a 50-100 mesh sieve, and then adding into a hydrothermal reaction kettle, wherein 18g of human excrement residue is added into every 100mL of water. Setting the heating rate at 10 ℃/min, carrying out hydrothermal reaction, respectively standing at 140 ℃, 180 ℃ and 220 ℃ for 30min, pouring out the supernatant after the reaction is finished, washing with deionized water to be neutral, freeze-drying, and grinding to obtain the hydrothermal carbon.
2)Fe3O4Hydrothermal charcoal preparation, dispersing 10g of the prepared hydrothermal charcoal in 30mL of ethylene glycol, and then adding FeCl3·6H2Dissolving O, adding 5mL of anhydrous sodium acetate, stirring to fully mix, ultrasonically dispersing for 20min, transferring to a reaction kettle, sealing and reacting at 250 ℃ for 2h at 200-3O4Hydrothermal charcoal, washing, freeze drying, grinding to obtain Fe3O4Hydrothermal charcoal, Fe3O4Is 15 percent.
3) Preparing a hydrothermal carbon-based urea fertilizer: weighing 1g r-polyglutamic acid, dissolving to 1% (V/V) glacial acetic acid water solution to obtain adhesive, wherein the mass concentration of r-polyglutamic acid solution is 0.2%, pulverizing urea by a pulverizer, sieving with a 50-100 mesh sieve, weighing urea, placing in a granulator, starting the granulator, setting the rotation speed at 40r/min, spraying binder during rotation, and slowly spraying Fe3O4Hydrothermal charcoal, Fe3O4The mass ratio of the hydrothermal carbon to the urea is 0.2:1, the granules are taken out after being formed, dried to constant weight at 40 ℃, and cooled to obtain the product.
Example 3
A preparation method of a human excrement hydrothermal carbon-based coated urea fertilizer comprises the following steps:
1) preparing the hydrothermal carbon, taking the excrement residue at the bottom of the first tank of the three-grid septic tank, naturally drying, crushing, sieving by a 50-100 mesh sieve, and then adding into a hydrothermal reaction kettle, wherein 20g of human excrement residue is added into every 100mL of water. Setting the heating rate at 12 ℃/min, carrying out hydrothermal reaction, respectively standing at 140 ℃, 180 ℃ and 220 ℃ for 35min, pouring out supernatant after the reaction is finished, washing with deionized water to be neutral, freeze-drying, and grinding to obtain the hydrothermal carbon.
2)Fe3O4Hydrothermal charcoal preparation, dispersing 10g of the prepared hydrothermal charcoal in 30mL of ethylene glycol, and then adding FeCl3·6H2Dissolving O, adding 5mL of anhydrous sodium acetate, stirring to fully mix, ultrasonically dispersing for 20min, transferring to a reaction kettle, sealing and reacting at 250 ℃ for 2h at 200-3O4Hydrothermal charcoal, washing, freeze drying, grinding to obtain Fe3O4Hydrothermal charcoal, Fe3O4Is 10 percent.
3) Preparing a hydrothermal carbon-based urea fertilizer: weighing 1g r-polyglutamic acid, dissolving to 1% (V/V) glacial acetic acid water solution to obtain adhesive, wherein the mass concentration of r-polyglutamic acid solution is 0.3%, pulverizing urea by a pulverizer, sieving with a 50-100 mesh sieve, weighing urea, placing in a granulator, starting the granulator, setting the rotation speed at 40r/min, spraying binder during rotation, and slowly spraying Fe3O4Hydrothermal charcoal, Fe3O4The mass ratio of the hydrothermal carbon to the urea is 0.3:1, the granules are taken out after being formed, dried to constant weight at 40 ℃, and cooled to obtain the product.
And the physicochemical property of the slow release fertilizer is detected by referring to the slow release characteristic detection standard (GB/T23348-2009).
(1) Compressive strength and wear resistance
Compressive strength: and randomly taking out 20 prepared hydrothermal carbon-based urea fertilizers, measuring the pressure resistance value of each fertilizer by using a texture analyzer, repeating for 5 times, and calculating the average value and the standard deviation of the fertilizers.
Wear resistance: and (4) measuring the wear resistance of the carbon-based urea fertilizer through the balance weight ratio. Weighing 3.00g to 50mL of prepared carbon-based urea fertilizer in a conical flask, mixing 8 steel beads into the fertilizer, sealing the opening of the conical flask, transferring the conical flask into a vibration incubator, oscillating the conical flask for 30min at a speed of 300r/min, taking out the conical flask, passing through a 0.4mm filter screen, weighing the mass of the residual fertilizer particles, calculating the residual weight ratio according to the ratio of the mass of the residual particles to the initial mass of the particles, and determining the wear resistance of the carbon-based fertilizer.
Remarking: in the table above, the hydrothermal carbon-based fertilizer is prepared from hydrothermal carbon according to the step 3). The modified hydrothermal carbon-based fertilizer prepared in example 2 was used in the modified hydrothermal carbon-based fertilizer of the present invention (the modified hydrothermal carbon-based fertilizer prepared in example 2 was also used in the following tests, and the test data of examples 1 and 3 were similar to those of example 2 and are not repeated here)
From the above table, it can be seen that the hydrothermal carbon has a relatively abundant pore structure, so that the adhesion during the coating process is insufficient, the average compressive capacity of the hydrothermal carbon-based urea fertilizer is 36.6N and is higher than 12N (critical value for measuring relatively high hardness), and the residual weight ratio homogeneity is higher than 97%. Compared with the hydrothermal carbon-based fertilizer, the compression resistance and the residual weight ratio of the modified hydrothermal carbon-based fertilizer are further improved, and the modified hydrothermal carbon-based fertilizer is convenient for the processes of collection, storage and transportation.
(2) Water absorption rate and water resistance
Generally, the lower the water absorption rate of the carbon-based fertilizer, the better the slow release effect. Testing the water absorbability of different carbon-based fertilizers according to a method of the national standard (GB/T23348-2009) of the slow-release fertilizer, and calculating the water absorption multiplying power of the water-absorbing carbon-based fertilizer in the process of achieving water absorption balance. The specific method comprises the following steps: taking 5.0g of fertilizer, filling the fertilizer into a nylon gauze bag with the aperture of 0.1-0.15mm, sealing, transferring the bag into a 250mL beaker, adding 150mL of deionized water, covering and sealing, and transferring the bag into a constant-temperature biochemical incubator at 25 ℃.
Carbon-based urea fertilizer slow-release water absorption rate
| Time of Water absorption (h) | Urea | Water-heating carbon-based fertilizer | The invention relates to a modified water-heating carbon-based fertilizer |
| 6 | 2.15±0.08 | 1.31±0.04 | 1.63±0.02 |
| 12 | 2.61±0.03 | 1.53±0.06 | 1.87±0.04 |
| 18 | 3.24±0.02 | 1.74±0.01 | 2.01±0.05 |
| 24 | 3.52±0.05 | 1.89±0.05 | 2.11±0.03 |
| 30 | 3.54±0.05 | 1.92±0.03 | 2.14±0.04 |
| 36 | 3.55±0.07 | 1.94±0.02 | 2.14±0.01 |
From the above table, it can be seen that the water absorption rate of the hydrothermal carbon-based coated urea fertilizer is significantly reduced compared with urea, mainly because the hydrothermal carbon has a rich pore structure and a surface functional group structure, resulting in a stronger adsorption performance of the hydrothermal carbon. Meanwhile, the super-strong water absorbability of the r-polyglutamic acid has certain contribution to the water absorption rate of the slow release fertilizer. The water absorption rate of the modified hydrothermal carbon-based coated slow-release fertilizer is slightly improved (P is less than 0.05) because of Fe3O4The introduction of the carbon-based fertilizer increases the particle size of the carbon-based fertilizer and reduces the integral specific surface area and porosity.
Water resistance refers to the ability of a material to resist water damage. The longer the particles remain in the water, the greater the water resistance. 5.0g of fertilizer was weighed into a 250mL beaker, 150mL of deionized water was added, and the resulting mixture was placed in a constant temperature biochemical incubator at 25 ℃ to closely observe the dissolution of the granules. The result shows that urea is completely dissolved in deionized water within 2h, the hydrothermal carbon-based urea fertilizer is gradually flocculent on the surface of the particle from the 8 th day, and the dissolution is basically completed when the particle reaches 12 th day. Fe3O4The modified hydrothermal carbon-based urea fertilizer starts to dissolve at 13d until 20d is substantially completely dissolved. The water resistance of the modified hydrothermal carbon-based urea fertilizer is enhanced mainly in that r-polyglutamic acid forms a smooth coating on the surface of particles, so that the particles are not easily soaked by water molecules, and the retention time in water is long. Fe3O4The water resistance of the modified hydrothermal carbon-based urea fertilizer is further increased by Fe in the granules2+The increase of the concentration further increases the water resistance of the surface coating.
(3) Nitrogen release characteristics of carbon-based fertilizer
And performing an earth pillar intermittent leaching experiment by referring to a slow release characteristic detection standard GB/T23349-2009 to evaluate the slow release characteristic of the slow release fertilizer. The inner diameter of the leaching column is 4cm, the column height is 25cm, the tube bottom is tightly banded and sealed by two layers of non-woven fabrics, and the leaching column is provided with a constant flow pump. Before rinsing begins, the quartz sand is washed by distilled water until the rinsing liquid is clear, the quartz sand passes through a 40-mesh screen after being dried, and then a mixed layer (6cm) → quartz sand (5cm) → two layers of non-woven fabrics from top to bottom according to the quartz sand (5cm) → carbon-based fertilizer (5.0g) + soil (20 g), and the content of Cr (VI) being 5.24 mg/kg. Simulating natural precipitation and precipitation every 24 hours, uniformly spraying 100mL of distilled water by using a constant flow pump, collecting leacheate by using a 250mL beaker, and measuring the concentration of urea in the leacheate by adopting a dimethylaminobenzaldehyde color development spectrophotometry method. And (3) when the leaching is finished, determining the content of Cr (VI) in the soil and the leacheate by using an alkali solution extraction-flame atomic absorption spectrophotometry (HJ 1082-2019).
As can be seen from fig. 4, the modified hydrothermal carbon-based urea fertilizer has the best slow release performance, the hydrothermal carbon-based urea fertilizer has the next highest slow release rate, and the initial nutrient dissolution rates of the modified hydrothermal carbon-based urea fertilizer, the hydrothermal carbon-based urea fertilizer and the urea are 5.7%, 7.5% and 21.2%, respectively. Complete release of the contained nitrogen at 45d, 35d and 20d, respectively. The dissolution rate of the initial nutrients shows that the carbon-based fertilizer is complete in coating and contains rich pore structures, so that the rapid release of the nutrients is inhibited.
Capability of carbon-based urea fertilizer in removing Cr (VI)
| Type of fertiliser | Content (mg/kg) of Cr (VI) in soil | Cr (VI) concentration (mg/L) in leacheate |
| Urea | 4.65 | 0.025 |
| Water-heating carbon-based fertilizer | 3.26 | 0.017 |
| The invention relates to a modified water-heating carbon-based fertilizer | 2.57 | 0.011 |
As can be seen from the table, the addition of the hydrothermal carbon and the modified hydrothermal carbon based urea fertilizer reduces the content of Cr (VI) in the whole reaction system. This is because the hydrothermal carbon surface contains abundant oxygen-containing functional groups, which can increase the coulomb attraction with Cr (VI) and simultaneously perform redox reaction, thereby realizing the removal of Cr (VI). Fe2+/Fe3+As the electronic shuttle, the capability of removing Cr (VI) is further enhanced. The r-polyglutamic acid is used as a good flocculating agent and also contributes to the removal of Cr (VI).
(4) Recoverability and stability of modified hydrothermal carbon-based urea fertilizer
Based on the recycling concept, the recovery performance of the modified hydrothermal carbon-based material is explored. As shown in the figure, the saturation magnetization of the hydrothermal carbon-based urea fertilizer is about 0emu/g, while the magnetization of the modified hydrothermal carbon-based urea fertilizer can reach 21.26emu/g, so that the modified hydrothermal carbon-based urea fertilizer has strong magnetic recovery performance and is easy to recover from soil. After being washed and dried, the urea fertilizer is repeatedly used for 6 times with the urea fertilizer for preparing the modified hydrothermal carbon-based urea fertilizer, and the complete dissolution time of nutrients can be maintained to be more than 35 days.
(5) Experiment of potted lettuce
Lettuce is taken as a research object, the actual effect of the carbon-based urea fertilizer is measured through the crop yield and the nitrogen fertilizer utilization rate, and the experimental scheme is as follows:
| kind of fertilizer | Fertilizer quality (g/basin) | Potassium chloride (g/basin) | Perphosphoric acid quality (g/basin) |
| Urea | 0.5 | 1.34 | 0.33 |
| Water-heating carbon-based fertilizer | 2.0 | 1.34 | 0.33 |
| Modified water-heating carbon-based fertilizer | 2.0 | 1.34 | 0.33 |
After the fertilizer and 2.0kg of soil are fully mixed, 2 lettuce plants are planted in each pot for 3 groups of parallel experiments, and the yield of the lettuce is observed after 45 days, as shown in the table
| Kind of fertilizer | Yield g/granule | Increase in yield/%) |
| Urea | 91.04±0.32 | - |
| Water-heating carbon-based fertilizer | 114.25±0.27 | 20.31 |
| The invention relates to a modified water-heating carbon-based fertilizer | 125.68±0.14 | 27.56 |
Compared with the traditional urea, the yield of the lettuce under the condition of the hydrothermal carbon-based fertilizer is increased by 20.31 percent, and the yield of the lettuce under the condition of the modified hydrothermal carbon-based fertilizer is increased by 27.56 percent.
The present invention is not limited to the above-described embodiments, and those skilled in the art will understand that: various changes, modifications, substitutions and alterations can be made to the embodiments without departing from the principles and spirit of the invention, the scope of which is defined by the claims and their equivalents.