CN114656973B - Ecological active agent with water storage regulating function and preparation method thereof - Google Patents

Ecological active agent with water storage regulating function and preparation method thereof Download PDF

Info

Publication number
CN114656973B
CN114656973B CN202210390307.1A CN202210390307A CN114656973B CN 114656973 B CN114656973 B CN 114656973B CN 202210390307 A CN202210390307 A CN 202210390307A CN 114656973 B CN114656973 B CN 114656973B
Authority
CN
China
Prior art keywords
parts
soil
active agent
water storage
water
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN202210390307.1A
Other languages
Chinese (zh)
Other versions
CN114656973A (en
Inventor
郭光光
武艳芳
徐自恒
王慧
胡传伟
王晶
赵珊珊
陈娜娟
张俊强
陈开荣
高红升
崔光昊
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Palm Eco Town Development Co ltd
Original Assignee
Palm Eco Town Development Co ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Palm Eco Town Development Co ltd filed Critical Palm Eco Town Development Co ltd
Priority to CN202210390307.1A priority Critical patent/CN114656973B/en
Publication of CN114656973A publication Critical patent/CN114656973A/en
Application granted granted Critical
Publication of CN114656973B publication Critical patent/CN114656973B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C09DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
    • C09KMATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
    • C09K17/00Soil-conditioning materials or soil-stabilising materials
    • C09K17/40Soil-conditioning materials or soil-stabilising materials containing mixtures of inorganic and organic compounds
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05BPHOSPHATIC FERTILISERS
    • C05B17/00Other phosphatic fertilisers, e.g. soft rock phosphates, bone meal
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05GMIXTURES OF FERTILISERS COVERED INDIVIDUALLY BY DIFFERENT SUBCLASSES OF CLASS C05; MIXTURES OF ONE OR MORE FERTILISERS WITH MATERIALS NOT HAVING A SPECIFIC FERTILISING ACTIVITY, e.g. PESTICIDES, SOIL-CONDITIONERS, WETTING AGENTS; FERTILISERS CHARACTERISED BY THEIR FORM
    • C05G3/00Mixtures of one or more fertilisers with additives not having a specially fertilising activity
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05GMIXTURES OF FERTILISERS COVERED INDIVIDUALLY BY DIFFERENT SUBCLASSES OF CLASS C05; MIXTURES OF ONE OR MORE FERTILISERS WITH MATERIALS NOT HAVING A SPECIFIC FERTILISING ACTIVITY, e.g. PESTICIDES, SOIL-CONDITIONERS, WETTING AGENTS; FERTILISERS CHARACTERISED BY THEIR FORM
    • C05G3/00Mixtures of one or more fertilisers with additives not having a specially fertilising activity
    • C05G3/80Soil conditioners
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05GMIXTURES OF FERTILISERS COVERED INDIVIDUALLY BY DIFFERENT SUBCLASSES OF CLASS C05; MIXTURES OF ONE OR MORE FERTILISERS WITH MATERIALS NOT HAVING A SPECIFIC FERTILISING ACTIVITY, e.g. PESTICIDES, SOIL-CONDITIONERS, WETTING AGENTS; FERTILISERS CHARACTERISED BY THEIR FORM
    • C05G5/00Fertilisers characterised by their form
    • C05G5/10Solid or semi-solid fertilisers, e.g. powders
    • C05G5/12Granules or flakes
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05GMIXTURES OF FERTILISERS COVERED INDIVIDUALLY BY DIFFERENT SUBCLASSES OF CLASS C05; MIXTURES OF ONE OR MORE FERTILISERS WITH MATERIALS NOT HAVING A SPECIFIC FERTILISING ACTIVITY, e.g. PESTICIDES, SOIL-CONDITIONERS, WETTING AGENTS; FERTILISERS CHARACTERISED BY THEIR FORM
    • C05G5/00Fertilisers characterised by their form
    • C05G5/30Layered or coated, e.g. dust-preventing coatings
    • CCHEMISTRY; METALLURGY
    • C09DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
    • C09KMATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
    • C09K2101/00Agricultural use

Landscapes

  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Organic Chemistry (AREA)
  • Pest Control & Pesticides (AREA)
  • Soil Sciences (AREA)
  • Inorganic Chemistry (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Fertilizers (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The invention discloses an ecological active agent with a water storage regulation function, which comprises the following components in parts by weight: 4 to 6 parts of construction waste, 2.1 to 4.3 parts of attapulgite powder, 2 to 3 parts of phosphate rock powder, 1 to 2 parts of potassium feldspar, 0.5 to 0.8 part of water, 1 to 3 parts of polyacrylamide, 0.2 to 1 part of plant activator, 2 to 5 parts of garden waste composting product, 0.5 to 1 part of thickener, 2 to 4 parts of oxidized starch, 0.1 to 0.2 part of adhesive and 4 to 8 parts of microorganism strain. The invention also provides a preparation method of the ecological active agent with the water storage regulating function. The ecological active agent with the water storage regulation function can effectively improve the soil structure, passivate the heavy metals in the soil, strengthen the soil fertilizer and water retention capacity, has wide application range and high applicability, is simple in preparation process, and is suitable for large-scale production.

Description

Ecological active agent with water storage regulating function and preparation method thereof
Technical Field
The invention belongs to the technical field of ecological restoration, and particularly relates to an ecological active agent with a water storage regulation function and a preparation method thereof.
Background
The soil is located in the exchange zone of the atmosphere ring, the water ring, the rock ring and the biosphere and is a junction connecting the inorganic world and the organic world, so the soil has extremely important function. With the development of economy, human activities are frequent, so that the soil environment is greatly changed, various soil problems are accompanied, and the ecological damage problem is caused. At present, relatively more soil problems mainly comprise soil hardening, soil acidification and water and soil loss, and a plurality of technologies and products for preventing and treating the soil hardening, the soil acidification and the water and soil loss are developed and applied, and good results are obtained.
However, the existing soil conditioner is mainly a soil restoration modifier, and the soil acidification restoration effect cannot be durable due to the formula and the process problems, the water storage and retention capacity is poor, and the soil improvement effect is weak; the partial soil restoration modifier also has the characteristics of improving the physical and chemical properties of soil and fertility improvement, but takes effect slowly. The existing soil remediation modifier has low soil improvement efficiency, can influence the physicochemical properties of soil in the improvement process, damages the soil structure, and can also introduce heavy metals to cause heavy metal pollution of the soil.
The prior art has the defects of low applicability, difficulty in achieving the persistent solution of soil hardening and acidification, and poor soil fertilizer and water retention capacity after product improvement, thereby causing resource waste. The main manifestations are:
1. in the conditioner, most organic matters are mainly organic matters, especially organic fertilizers prepared from animal and plant residues, animal excreta and the like are mainly prepared into repairing products, and the products are single in functionality and short in improvement duration;
2. the soil conditioner mainly containing microorganisms is characterized in that the microorganisms are not strictly screened, the selected strains are random, antagonism and synergistic effects among composite strains are not fully considered, the effect of a single strain is still good, but the combined effects of a plurality of strains are poor;
3. most products simply mix materials, and the reaction between the materials is not fully considered, so that the effect of 1+1 & gt2 is not achieved, and the effect is single and not obvious;
4. most modifiers want to achieve corresponding effects, the application amount is large, and the obvious improvement effect can be achieved only 3-4 years;
5. some conditioning agents can effectively improve the soil structure and have a certain fertility effect, but the fertility releasing effect is weak, the plant growth capacity is weak after soil improvement, and the soil fixing, soil holding and water and fertilizer retaining capacity cannot be achieved through the synergistic effect of plants and microorganisms.
The present invention has been made based on the above-described circumstances.
Disclosure of Invention
The invention aims at: aiming at the defects of the prior art, an ecological active agent with a water storage adjusting function is developed, and the invention also provides a preparation method of the ecological active agent with the water storage adjusting function. The ecological active agent can effectively improve soil structure, passivate soil heavy metals, enhance soil fertilizer and water retention capacity, has wide application range and high applicability, is simple in preparation process, and is suitable for large-scale production.
In order to achieve the above purpose, the present invention adopts the following technical scheme:
an ecological active agent with a water storage regulating function comprises the following components in parts by weight:
in the invention, the construction waste is one or a mixture of more of concrete, mortar, brickwork and waste wood. When the construction waste contains waste wood, the proportion of the waste wood should not exceed 10% of the total mass of the construction waste.
In the invention, the plant activator is mixed paste or powder, and the plant activator is mainly one or more of Kang Zhuangsu (hypersensitive protein), benzothiadiazole (BTH) and humic acid.
In the invention, the garden waste is powdery or flocculent after long-time decomposition of roots, stems, fallen leaves (including but not limited to broadleaf trees and shrubs), hay and the like, and the particle size of the garden waste is less than or equal to 0.3mm.
In the invention, the thickener is mainly bentonite added with one or more materials of alginic acid, gelatin, agar and pectin, and the bentonite accounts for 65-80%.
In the invention, the binder is carboxymethyl cellulose.
In the invention, the microbial bacillus is prepared by matching bacillus subtilis, bacillus mucilaginosus and bacillus megatherium according to the weight ratio of 2-4:1-2:1-2.
In the invention, the attapulgite powder is natural water-containing magnesium aluminosilicate, has a unique three-dimensional chain structure and a special needle-bar crystal structure, thus having unusual colloid and adsorption performance, and has the main functions of binding various materials and providing reliable structural stability for the preparation of subsequent products.
The phosphate rock powder is prepared by directly mechanically pulverizing and grinding phosphate rock, is generally gray or yellow brown powder, and contains tricalcium phosphate Ca as main ingredient 3 (PO 4 ) 2 It can gradually become absorbable by plants in an acidic environment.
The potassium feldspar is a potassium-containing ore and is one of main raw materials for preparing the potassium fertilizer. The potassium ore adopted here is potassium ore powder, needs to be ground into a powdery structure, and has the functions of being matched with the subsequent microorganism strain, and providing stable potassium element supply for plants by combining the water retention and water release characteristics of the product.
The polyacrylamide is a linear high molecular polymer, and the invention uses powdery polyacrylamide products. The material has good thermal stability, can be dissolved in water according to any proportion, and the aqueous solution is uniform and transparent liquid. In the product, the function of the product is mainly to absorb and release water, and the product has the functions of adhesion and thickening in an acidic environment, so that the product is beneficial to the form stability.
The oxidized starch is modified starch obtained by oxidizing starch by the action of the starch with an oxidant in acid, alkali and neutral medium. The oxidized starch reduces the gelatinization temperature of the starch, reduces the viscosity of the hot paste and increases the thermal stability, and the product has white color, transparent paste, good film forming property and good freeze thawing resistance, is a thickener with low viscosity and high concentration, and is widely applied to the industries of textile, papermaking, food and fine chemical industry.
The invention also provides a preparation method of the ecological active agent with the water storage regulation function, which comprises the following specific steps:
a. carrying out multistage crushing on the construction waste, pouring the construction waste which is sieved by a sieve with 4-6 mm into organic weak acid, soaking for 3.5-4.5 h, filtering and air-drying;
b. mixing the construction waste treated in the step a, 1-2 parts of attapulgite powder, phosphate rock powder, potassium feldspar and water, stirring for 20-40 min at normal temperature, rolling, crushing and granulating under the conditions that the humidity is 65-85% and the pressure is 130-150 MPa, and sieving the mixture with the particle size of 2-5 mm;
c. adding polyacrylamide, a plant activator and 0.1-0.3 part of attapulgite powder into the mixture prepared in the step b, granulating by adopting a rotary drum granulating method, and screening out particles A with the particle size of 3-8 mm, wherein no water is added in the process;
d. c, adjusting the temperature to 35-40 ℃ and the humidity to 40-60%, adding a garden waste composting product, the rest attapulgite powder and a thickener into the particles A obtained in the step c, performing disc granulation, and screening out particles B with the particle size of 5-16 mm, wherein no water is added in the process;
e. c, adding oxidized starch into the particles B obtained in the step c for coating, taking out after 20-40 min, and air-drying at room temperature, wherein the coating effect is that the particles B are just covered;
f. then adding adhesive and microbial strain, granulating at room temperature by adopting a rotary drum granulating method, and screening the product with the particle size of 5-18 mm.
In the step a, the organic weak acid is any one of acetic acid, oxalic acid and citric acid, and the concentration of the organic weak acid is 0.5-1%.
A large amount of construction waste is produced every year in China, and some construction waste has compact structural characteristics, and the construction waste is treated to have excellent water retention and water release properties, fully develops the characteristics and is prepared into a soil conditioner, so that the construction waste has extremely wide application prospect.
The invention mainly uses construction waste, attapulgite powder, garden waste composting products, phosphate rock powder, bacillus mucilaginosus, bacillus subtilis, bacillus megaterium, potassium feldspar, oxidized starch, polyacrylamide and plant activators as raw materials. The preparation technology fully considers the interaction among soil, microorganisms and plants, conditions and restores the soil while ensuring ecological balance, adopts a hot-sticking cold-swelling process, and utilizes a modern multilayer cold-coating technology to prepare and produce the high-performance ecological active agent.
Compared with the prior art, the invention has the beneficial effects that:
1. the preparation is simple, and the required equipment is less; the raw materials are easy to obtain, and the production process is pollution-free; the heating treatment is less, and the energy consumption is low;
2. the ecological active agent with the water storage regulation function can effectively improve the physicochemical property of soil, improve the water retention of the soil and prolong the effect duration; after the product is applied into soil, the microbial layer is eluted by water and is firstly shed and developed, oxidized starch can provide short-term growth raw material requirements for the microbial layer, and after the garden waste layer is shed into the soil, the microbial layer is decomposed for a period of time to form soil organic matters, so that the soil can be effectively improved; the middle layer of the product is wetted by water to form a granular structure with more surface pores, has strong water and fertilizer retention, can continuously supplement water and nutrients for soil, has stable internal structure, can effectively supplement soil nutrients by inorganic phosphorus and potassium contained in the product, and has good water storage and retention functions and fertility improvement capability;
3. the added garden waste composting product contains more functional groups, has strong bond-bridge combined effect, can effectively solidify heavy metals in soil, and has certain heavy metal passivation capability.
Detailed Description
The invention is further illustrated, but not limited, by the following examples.
The invention provides 3 examples and 3 comparative examples, 6 different ecological active agents are prepared by adjusting the types, the content, the preparation conditions or the preparation steps of raw materials, and the specific operation is as follows:
example 1
The preparation method of the ecological active agent with the water storage adjusting function in the embodiment comprises the following specific steps:
a. crushing the construction waste, sieving with a 4mm sieve, soaking the crushed construction waste in 0.5% acetic acid-citric acid mixed solution for 4.5 hours, and filtering and air-drying the crushed construction waste;
b. taking 6 parts of the construction waste treated in the step a, 2 parts of attapulgite powder, 3 parts of rock phosphate powder and 2 parts of dolomite, adding water and stirring for 40min at normal temperature, rolling, crushing and granulating under the conditions that the humidity is 65% and the pressure is 130MPa, and screening the mixture with the particle size of 2-5 mm.
c. And b, adding 1 part of polyacrylamide, 1 part of plant activator and 0.3 part of attapulgite powder into the mixture prepared in the step b, granulating by adopting a drum granulation method, and sieving the granules A with the particle size of 3-8 mm without adding water.
d. C, adjusting the temperature to 35 ℃ and the humidity to 50%, adding 5 parts of garden waste composting products, 2 parts of attapulgite powder and 1 part of thickener into the particles A obtained in the step c, carrying out disc granulation, and sieving the particles B with the particle size of 5-16 mm without adding water in the process.
e. And c, adding 4 parts of oxidized starch into the granules B obtained in the step c at the temperature of 80-95 ℃, coating, taking out after 30min, and airing at room temperature.
f. Then adding 0.2 part of adhesive, 4 parts of bacillus subtilis, 2 parts of bacillus mucilaginosus and 2 parts of bacillus megaterium into the mixture, granulating the mixture at room temperature by adopting a rotary drum granulating method, and screening the product with the particle size of 5-18 mm as a final product.
Example 2
a. Crushing the construction waste, sieving with a 4mm sieve, soaking in 0.5% oxalic acid for 4 hours, filtering and air-drying;
b. taking 5 parts of the construction waste treated in the step a, 2 parts of attapulgite powder, 2 parts of rock phosphate powder and 1 part of dolomite, adding water and stirring for 20min at normal temperature, carrying out rolling crushing granulation under the pressure of 140MPa with the humidity of 70%, and screening the mixture with the particle size of 2-5 mm.
c. And b, adding 2 parts of polyacrylamide, 0.5 part of plant activator and 0.2 part of attapulgite powder into the mixture prepared in the step b, granulating by adopting a drum granulation method, and sieving the granules A with the particle size of 3-8 mm without adding water.
d. C, adjusting the temperature to 35 ℃ and the humidity to 50%, adding 3 parts of garden waste composting products, 2 parts of attapulgite powder and 1 part of thickener into the particles A obtained in the step c, carrying out disc granulation, and sieving the particles B with the particle size of 5-16 mm, wherein no water is added in the process.
e. And c, adding 3 parts of oxidized starch into the granules B obtained in the step c at the temperature of 80-95 ℃, coating, taking out after 30min, and airing at room temperature.
f. Then adding 0.2 part of adhesive, 2 parts of bacillus subtilis, 1 part of bacillus mucilaginosus and 1 part of bacillus megaterium into the mixture, granulating the mixture at room temperature by adopting a rotary drum granulating method, and screening the product with the particle size of 5-18 mm as a final product.
Example 3
a. Crushing the construction waste, sieving with a 4mm sieve, soaking the crushed construction waste in 1% oxalic acid-citric acid mixed solution for 3.5 hours, and filtering and air-drying the crushed construction waste;
b. and d, taking 4 parts of the construction waste treated in the step a, 4 parts of attapulgite powder, 4 parts of rock phosphate powder and 1 part of dolomite, adding water, stirring for 30min at normal temperature, carrying out rolling crushing granulation under the pressure of 140MPa with the humidity of 70%, and screening the mixture with the particle size of 2-5 mm.
c. And b, adding 3 parts of polyacrylamide, 1 part of plant activator and 0.3 part of attapulgite powder into the mixture prepared in the step b, granulating by adopting a drum granulation method, and sieving particles A with the particle size of 3-8 mm without adding water.
d. C, adjusting the temperature to 35 ℃ and the humidity to 50%, adding 2 parts of garden waste composting products, 1 part of attapulgite powder and 0.5 part of thickener into the particles A obtained in the step c, carrying out disc granulation, and sieving the particles B with the particle size of 5-16 mm without adding water in the process.
e. And c, adding 2 parts of oxidized starch into the particles B obtained in the step c at the temperature of 80-95 ℃, coating, taking out after 30min, and airing at room temperature.
f. Then adding 0.1 part of adhesive, 2 parts of bacillus subtilis, 1 part of bacillus mucilaginosus and 1 part of bacillus megaterium into the mixture, granulating the mixture at room temperature by adopting a rotary drum granulating method, and screening the product with the particle size of 5-18 mm as a final product.
Comparative example 1
a. Crushing the construction waste, sieving with a 4mm sieve, soaking the crushed construction waste in 0.5% acetic acid-citric acid mixed solution for 4.5 hours, and filtering and air-drying the crushed construction waste;
b. taking 4 parts of the construction waste treated in the step a, 2 parts of attapulgite powder, 3 parts of rock phosphate powder and 2 parts of dolomite, adding water and stirring for 40min under normal temperature, carrying out rolling crushing granulation under the pressure of 130MPa, and screening particles with the particle size of 2-5 mm;
c. b, adjusting the temperature to 35 ℃ and the humidity to 50%, adding 5 parts of garden waste composting products, 2 parts of attapulgite powder and 1 part of thickening agent into the particles prepared in the step b, carrying out disc granulation, and sieving the particles with the particle size of 5-16 mm, wherein no water is added in the process;
d. c, adding 1 part of polyacrylamide, 1 part of plant activator and 0.3 part of attapulgite powder into the particles prepared in the step c, granulating by adopting a drum granulation method, and sieving to obtain particles with the particle size of 3-8 mm, wherein no water is added in the process;
e. adding 4 parts of oxidized starch into the particles obtained in the step c at the temperature of 80-95 ℃, coating, taking out after 30min, and airing at room temperature;
f. then adding 0.2 part of adhesive, 4 parts of bacillus subtilis, 2 parts of bacillus mucilaginosus and 2 parts of bacillus megaterium into the mixture, granulating the mixture at room temperature by adopting a rotary drum granulating method, and screening the product with the particle size of 5-18 mm as a final product.
Comparative example 1 differs from example 1 in that: the order of preparation of step b and step c in comparative example 1 was exchanged with the order of preparation of steps b, c in example 1.
Comparative example 2
Comparative example 2 differs from example 1 in that no polyacrylamide was added in step c of comparative example 2, and the remaining preparation steps and materials were the same as in example 1.
Comparative example 3
Comparative example 3 differs from example 1 in that comparative example 3 was added with water during the preparation of step c and step d, and the remaining preparation steps and materials were the same as example 1.
Application example
Taking 6 flowerpots with water leakage openings at bottoms with outer diameters of 20cm and heights of 15cm, and placing flowerpots with the bottoms of more than 314cm 2 Weighing 3kg of dried soil, respectively placing the dried soil at the bottoms of 6 flowerpots, slightly compacting the dried soil, and respectively marking the dried soil as S1, S2, S3, D1, D2 and D3. Weighing 6 groups of 1kg of dried soil respectively, uniformly mixing with 1kg of the 6 groups of products prepared in examples 1-3 and comparative examples 1-3 respectively, adding 2kg of the mixture into 6 flowerpots filled with 3kg of soil S1, S2, S3, D1, D2 and D3 respectively; for example, 1kg of the product prepared in example 1 and 1kg of the baked soil were uniformly mixed and then covered in a flowerpot labeled S1. 2kg of dried soil is weighed and covered on all flowerpots filled with soil and products, and the total mass of the soil and the products in each flowerpot is 7kg. And setting a flowerpot without adding a product and only adding the dried soil as a blank control, and marking the flowerpot as CK.
Repeating the above experiment for 3 times, namely, performing 3 parallel experiments, and taking the average value of the 3 experiments as the experimental result.
1. Detecting the water storage capacity of soil
7 flowerpots are watered thoroughly (water seepage occurs at the bottom), and then weighed, and the mass is taken as the initial mass of the treatment. The flowerpots were placed in cool and ventilated places and weighed at 0, 1, 2, 3, 5, 7, 10, 15, 20, 30, 50, 80, 120, 180, 240 days, respectively. The change in soil weight average in the pot for various days of treatment is shown in table 1.
Table 1 soil weight change on different days of treatment
As can be seen from the data in table 1, the weight of the flowerpot marked CK was lower than that of other flowerpots on day 0, and the weight of the flowerpot marked CK was almost identical to the weight of the soil itself from day 30 until 240 days, indicating that the soil moisture of the flowerpot had completely disappeared around day 30; the pot marked D1 became 7.01kg on day 50 and no significant change was followed, indicating that no soil weight below 7kg was present under this treatment; the weight change rule of the flowerpot marked as D2 is consistent with CK, but the weight loss amount is larger than CK within 7 days, which indicates that in D2, the soil porosity is changed to a certain extent, so that the water loss speed is increased, and the weight of D2 is slightly lower than 7kg at 30 days, which is related to the consumption of part of garden waste by microorganisms; the flowerpot marked as D3 has the weight higher than D2 and 7kg before 50 days, which indicates that the water storage capacity of D3 is higher than CK within 50 days, and has a certain water storage effect.
The weight change rule of the soil of the flowerpots marked as S1, S2 and S3 is the same, and the weight change is almost the same as that of the soil in other flowerpots before the 5 th day, but the quality of the soil is reduced far less than that of the soil in other flowerpots from the 5 th day to the 80 th day, and the quality of the soil is still higher than that of the soil in other flowerpots from the 80 th day to the 180 th day, which indicates that the water storage capacity of the soil is obviously improved under the treatment condition. On day 240, the quality is almost the same as that of CK, and the fact that microorganisms degrade garden waste and cause weak quality degradation is considered, which means that the soil still contains a small amount of water.
The experimental data prove that the products prepared by the embodiment have the capability of obviously improving the water storage and retention capacity of soil.
2. Determination of soil alkaline hydrolysis nitrogen, available phosphorus and quick-acting potassium content
After 240 days, the soil in 7 flowerpots was taken out, air-dried and ground, and the contents of alkaline hydrolysis nitrogen, available phosphorus and quick-acting potassium in the soil were measured by the method and instrument shown in table 2. The content changes of each sample in the soil are shown in Table 3.
TABLE 2 method and instrument for determining alkaline hydrolysis nitrogen, available phosphorus and quick-acting potassium content of soil
TABLE 3 variation of nutrient and heavy metal element content in different treated soils
As can be seen from the data in Table 1, the alkaline hydrolysis nitrogen, available phosphorus and quick-acting potassium contents of the soil in the CK flowerpot are 86.3mg/kg, 10.7mg/kg and 53.4mg/kg respectively, and the soil nutrient level is on the whole in a medium bias.
The alkaline hydrolysis nitrogen content, the effective phosphorus content and the quick-acting potassium content of the soil in the flowerpot marked as D1 are improved compared with CK, but the improvement range is less, namely 18%, 30% and 17%; the conditions of the soil in the flowerpots marked as D2 and D3 are basically the same, and the contents of alkaline hydrolysis nitrogen, available phosphorus and quick-acting potassium are respectively improved by 67% -83%, 140% -147% and 79% -83% relative to CK.
The alkaline hydrolysis nitrogen, the available phosphorus and the quick-acting potassium of the soil in the flowerpots marked as S1, S2 and S3 are respectively improved by 115% -133%, 222% -238% and 136% -155% compared with CK. The improvement effect of the product prepared by the additive example on soil nutrients is obviously better than that of the product prepared by the additive comparative example.
In conclusion, the ecological active agent prepared by the embodiment of the invention can effectively improve the physicochemical property of soil, improve the water retention of the soil and prolong the effect duration; the ecological active agent with the water storage regulation function has the advantages of good water storage and retention functions and capability of improving fertility.

Claims (6)

1.An ecological active agent with water storage regulating function is characterized by comprising the following components in parts by weight
4-6 parts of construction waste
2.1 to 4.3 portions of attapulgite powder
2-3 parts of ground phosphate rock
1 to 2 parts of potassium feldspar
0.5 to 0.8 part of water
1 to 3 parts of polyacrylamide
0.2 to 1 part of plant activator
2-5 parts of garden waste composting product
0.5 to 1 part of thickener
Oxidized starch 2-4 parts
0.1 to 0.2 part of adhesive
4-8 parts of microorganism strain;
the ecological active agent with the water storage regulation function is prepared by the following steps:
a. multistage crushing is carried out on the construction waste, the construction waste after 4-6 mm screening is poured into organic weak acid to be soaked for 3.5-4.5 h, and filtration and air drying are carried out;
b. mixing the construction waste treated in the step a, 1-2 parts of attapulgite powder, phosphate rock powder, potassium feldspar and water, stirring for 20-40 min at normal temperature, rolling, crushing and granulating under the conditions that the humidity is 65-85% and the pressure is 130-150 MPa, and screening out a mixture with the particle size of 2-5 mm;
c. adding polyacrylamide, a plant activator and 0.1-0.3 part of attapulgite powder into the mixture prepared in the step b, granulating by adopting a rotary drum granulating method, and screening out particles A with the particle size of 3-8 mm, wherein no water is added in the process;
d. c, adjusting the temperature to 35-40 ℃ and the humidity to 40-60%, adding a garden waste composting product, the rest attapulgite powder and a thickener into the particles A obtained in the step c, performing disc granulation, and screening out particles B with the particle size of 5-16 mm, wherein no water is added in the process;
e. adding oxidized starch into the particles B obtained in the step d for coating, taking out after 20-40 min, and air-drying at room temperature, wherein the coating effect is that the particles B are just covered;
f. adding an adhesive and microbial strains into the mixture, granulating the mixture at room temperature by adopting a rotary drum granulating method, and screening the product with the particle size of 5-18 mm;
the microbial strain is prepared by matching bacillus subtilis, bacillus mucilaginosus and bacillus megatherium according to the weight ratio of 2-4:1-2:1-2.
2. An ecological active agent with water storage regulating function according to claim 1, wherein: the construction waste is one or a mixture of more of concrete, mortar, brickwork and waste wood.
3. An ecological active agent with water storage regulating function according to claim 2, wherein: when the construction waste contains waste wood, the proportion of the waste wood should not exceed 10% of the total mass of the construction waste.
4. An ecological active agent with water storage regulating function according to claim 1, wherein: the plant activator is mixed paste or powder, and the plant activator is one or more of Kang Zhuangsu, benzothiadiazole and humic acid.
5. An ecological active agent with water storage regulating function according to claim 1, wherein: the garden waste is a powdery or flocculent product formed by decomposing tree roots, stems, fallen leaves and dried grass for a long time, and the grain size of the garden waste is less than or equal to 0.3 and mm.
6. An ecological active agent with water storage regulating function according to claim 1, wherein: the binder is carboxymethyl cellulose.
CN202210390307.1A 2022-04-14 2022-04-14 Ecological active agent with water storage regulating function and preparation method thereof Active CN114656973B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202210390307.1A CN114656973B (en) 2022-04-14 2022-04-14 Ecological active agent with water storage regulating function and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202210390307.1A CN114656973B (en) 2022-04-14 2022-04-14 Ecological active agent with water storage regulating function and preparation method thereof

Publications (2)

Publication Number Publication Date
CN114656973A CN114656973A (en) 2022-06-24
CN114656973B true CN114656973B (en) 2024-04-12

Family

ID=82035691

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202210390307.1A Active CN114656973B (en) 2022-04-14 2022-04-14 Ecological active agent with water storage regulating function and preparation method thereof

Country Status (1)

Country Link
CN (1) CN114656973B (en)

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104109038A (en) * 2014-08-12 2014-10-22 许盛英 Method for producing construction waste compressed nutrient soil
CN105669308A (en) * 2016-01-18 2016-06-15 李巍 Bioorganic fertilizer and method for improving soil by accurate application of bioorganic fertilizer
CN106187530A (en) * 2016-07-25 2016-12-07 南京信息工程大学 A kind of compound organic fertilizer and preparation method thereof
CN107417374A (en) * 2017-06-22 2017-12-01 兰溪市奥而特农业科技有限公司 Multifunction soil improver and preparation method thereof
CN108797612A (en) * 2018-06-19 2018-11-13 江苏东珠景观股份有限公司 A kind of high stability side slope vertical planting ecological restoring method
CN113860950A (en) * 2021-10-11 2021-12-31 浙江省农业科学院 Medium and low yield farmland plough layer soil reservoir expansion and storage improving agent and preparation method thereof

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104109038A (en) * 2014-08-12 2014-10-22 许盛英 Method for producing construction waste compressed nutrient soil
CN105669308A (en) * 2016-01-18 2016-06-15 李巍 Bioorganic fertilizer and method for improving soil by accurate application of bioorganic fertilizer
CN106187530A (en) * 2016-07-25 2016-12-07 南京信息工程大学 A kind of compound organic fertilizer and preparation method thereof
CN107417374A (en) * 2017-06-22 2017-12-01 兰溪市奥而特农业科技有限公司 Multifunction soil improver and preparation method thereof
CN108797612A (en) * 2018-06-19 2018-11-13 江苏东珠景观股份有限公司 A kind of high stability side slope vertical planting ecological restoring method
CN113860950A (en) * 2021-10-11 2021-12-31 浙江省农业科学院 Medium and low yield farmland plough layer soil reservoir expansion and storage improving agent and preparation method thereof

Also Published As

Publication number Publication date
CN114656973A (en) 2022-06-24

Similar Documents

Publication Publication Date Title
CN101723766B (en) Organic compound soil modifier and preparation thereof
CN104086313B (en) A kind of preparation method of inorganic-organic nutritive soil modifier
CN110066662B (en) Functional soil conditioner and preparation method thereof
CN106381150A (en) An acidic charcoal modifier for modifying saline-alkali soil and a preparing method thereof
CN104860753A (en) Membrane-coated microbial slow-release fertilizer and production method thereof
CN104860779A (en) Soil improvement type fertilizer and preparation method thereof
CN103011973A (en) Manufacture method of synergic type nitrogen-phosphorus-potassium mixed fertilizer with slow release and loss control effect
CN113336593A (en) Organic-inorganic compound fertilizer for leafy vegetables and preparation method thereof
CN113481011A (en) Preparation method and application of activated phosphate rock powder-biochar composite soil conditioner
CN114656973B (en) Ecological active agent with water storage regulating function and preparation method thereof
CN108314521A (en) A kind of special compound base manure of eucalyptus of high phosphorus element release rate
CN107903117A (en) Concave convex rod saline land greening tree planting soil conditioner
CN107903136A (en) Ardealite saline land greening tree planting soil conditioner
CN110028358B (en) Coastal saline-alkali soil salt-control alkali-reduction soil improvement method based on dominant compatibility of controlled release fertilizer, plant immunity inducer and organic fertilizer
CN104671981A (en) Full nutritional functional type polymer coated type strawberry fertilizer and preparation method thereof
CN107162862A (en) A kind of raising rice seedlings moisturizing getting fat block and preparation method
CN103011972A (en) Manufacture method of synergic type nitrogenous fertilizer with slow release and loss control effect
CN116076189A (en) Method for promoting improvement of red mud soil formation and vegetation recovery by sintering process
CN108821878A (en) One kind containing active humic acid composite microbe fertilizer and preparation method thereof
CN107129373A (en) A kind of nursery stock organic fertilizer and preparation method thereof
CN111362752A (en) Prepolymerization liquid for preparing water-retaining coated urea and method for preparing water-retaining coated urea by using prepolymerization liquid
CN111747708A (en) Rock slope vegetation concrete capable of promoting plant growth and preparation method thereof
CN111978121A (en) Humic acid plant nutrition powder and preparation method thereof
CN104987163A (en) Stalk mesophyll embedded microbial fertilizer and preparation method thereof
AU2021100149A4 (en) Greenhouse Soil Amendment and Application Method Thereof

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant