CN116554888B - Soil restoration agent suitable for heavy metal pollution of soil - Google Patents

Soil restoration agent suitable for heavy metal pollution of soil Download PDF

Info

Publication number
CN116554888B
CN116554888B CN202310841559.6A CN202310841559A CN116554888B CN 116554888 B CN116554888 B CN 116554888B CN 202310841559 A CN202310841559 A CN 202310841559A CN 116554888 B CN116554888 B CN 116554888B
Authority
CN
China
Prior art keywords
parts
bentonite
hydroxyapatite
soil
stirring
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
CN202310841559.6A
Other languages
Chinese (zh)
Other versions
CN116554888A (en
Inventor
蒋奇晋
张留全
吕书记
曾河山
凌志锋
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.)
Guangdong Wanshan Environmental Technology Co ltd
Original Assignee
Guangdong Wanshan Environmental Technology 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 Guangdong Wanshan Environmental Technology Co ltd filed Critical Guangdong Wanshan Environmental Technology Co ltd
Priority to CN202310841559.6A priority Critical patent/CN116554888B/en
Publication of CN116554888A publication Critical patent/CN116554888A/en
Application granted granted Critical
Publication of CN116554888B publication Critical patent/CN116554888B/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
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C1/00Reclamation of contaminated soil
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C1/00Reclamation of contaminated soil
    • B09C1/08Reclamation of contaminated soil chemically

Abstract

The invention discloses a soil restoration agent suitable for soil heavy metal pollution, which comprises the following raw materials in parts by weight: 40-45 parts of bentonite regulating slurry, 15-25 parts of biomass charcoal, 5-10 parts of calcium hydroxy phosphate, 2-5 parts of humic acid, 3-6 parts of hydroxyapatite blending rice hull ash agent and 1-3 parts of calcium oxide. According to the invention, biomass charcoal, calcium hydroxy phosphate, humic acid and hydroxyapatite are blended with rice hull ash and calcium oxide raw materials to be compounded and prepared, through coordination among various raw materials, bentonite adjustment slurry is used as matrix liquid to carry out coating modification, through coordination among bentonite adjustment slurry and the hydroxyapatite blending rice hull ash, the raw materials are synergistic, the heavy metal adsorption efficiency of the product is enhanced, sustainable adsorption can be realized, and meanwhile, the product has stable performance under the acid corrosion condition.

Description

Soil restoration agent suitable for heavy metal pollution of soil
Technical Field
The invention relates to the technical field of soil remediation, in particular to a soil remediation agent suitable for soil heavy metal pollution.
Background
Soil is one of the main natural resources that humans depend on to survive, and is also an important component of the human ecological environment. However, with the increase of industrial and urban pollution and the increase of the types and the quantity of agricultural chemical substances, the heavy metal pollution of soil is increasingly serious. Therefore, in order to protect natural resources and maintain good ecological environment, the soil polluted by heavy metals is repaired into unprecedented matters.
The existing soil repairing agent is easy to saturate in heavy metal adsorption, long-acting repairing efficiency is difficult to realize, meanwhile, the repairing agent is difficult to store under the acid corrosion condition, the adsorption effect is easy to influence after long-term storage, and the invention further improves the problem.
Disclosure of Invention
Aiming at the defects of the prior art, the invention aims to provide a soil restoration agent suitable for soil heavy metal pollution so as to solve the problems in the prior art.
The invention solves the technical problems by adopting the following technical scheme:
the invention provides a soil restoration agent suitable for soil heavy metal pollution, which comprises the following raw materials in parts by weight:
40-45 parts of bentonite regulating slurry, 15-25 parts of biomass charcoal, 5-10 parts of calcium hydroxy phosphate, 2-5 parts of humic acid, 3-6 parts of hydroxyapatite blending rice hull ash agent and 1-3 parts of calcium oxide;
the preparation method of the repairing agent comprises the following steps: and (3) mixing biomass charcoal, calcium hydroxy phosphate, humic acid and hydroxyapatite with the rice hull ash agent, uniformly stirring and mixing the mixture, and then adding the mixture into bentonite-regulated slurry for continuous mixing to obtain the repairing agent.
Preferably, the soil restoration agent comprises the following raw materials in parts by weight:
42.5 parts of bentonite regulating slurry, 20 parts of biomass charcoal, 7.5 parts of calcium hydroxy phosphate, 3.5 parts of humic acid, 4.5 parts of hydroxyapatite blending rice hull ash agent and 2 parts of calcium oxide.
Preferably, the preparation method of the bentonite conditioning slurry comprises the following steps:
s01: feeding bentonite into 130-140 deg.C, heat treating for 10-15min, cooling to 45-55 deg.C at 1-3 deg.C/min, and maintaining for 5-10min;
s02: placing the S01 product into hydrochloric acid solution with the total amount of 3-5 times of the S01 product, then adding sodium dodecyl sulfate with the total amount of 2-5% of the S01 product and yttrium nitrate solution with the total amount of 1-5% of the S01 product, and then carrying out primary stirring and pre-modification;
s03: then adding a silane coupling agent KH560 accounting for 2-5% of the total amount of the S01 product and a Tris buffer solution accounting for 1-3% of the total amount of the S01 product into the S02, carrying out secondary stirring for pre-modification, stirring fully, washing with water, and drying to obtain pre-modified bentonite;
s04: adding the pre-modified bentonite into 3-5 times of the regulating composite liquid, and uniformly stirring to obtain bentonite regulating slurry.
Preferably, the mass fraction of the hydrochloric acid solution is 1-3%; the mass fraction of the yttrium nitrate solution is 2-5%.
Preferably, the rotational speed of the primary stirring pre-modification is 350-450r/min, the stirring temperature is 40-45 ℃, and the stirring time is 30-40min; the rotational speed of the secondary stirring pre-modification is 800-1000r/min, the stirring temperature is 46-48 ℃, and the stirring time is 20-30min.
Preferably, the Tris buffer is 12-15g/L, pH value 8.5-9.0, wherein the concentration of dopamine is 2-3mg/ml.
Preferably, the regulating compound liquid comprises the following raw materials in parts by weight:
3-6 parts of chitosan aqueous solution with the mass fraction of 5%, 1-3 parts of sodium alginate aqueous solution with the mass fraction of 2%, 5-10 parts of ethanol solvent, 1-4 parts of N, N-dimethylamide and 2-5 parts of nano magnesium oxide.
Preferably, the preparation method of the hydroxyapatite blended rice hull ash agent comprises the following steps:
s11: mixing a hydrogen peroxide solution with the mass fraction of 6% and a hydrochloric acid solution with the mass fraction of 2% according to the weight ratio of 1:3 to obtain a hydrochloric acid-hydrogen peroxide solution;
s12: delivering the rice hull ash into 3-5 times hydrochloric acid-hydrogen peroxide solution for ultrasonic dispersion for 10-20min, ending ultrasonic treatment, washing with water, and drying to obtain modified rice hull ash;
s13: adding hydroxyapatite into a lanthanum nitrate solution according to a weight ratio of 1:5, then adding glycol amine accounting for 5-10% of the total amount of the hydroxyapatite, and uniformly stirring to obtain a hydroxyapatite solution;
adding the modified rice hull ash into the hydroxyapatite liquid according to the weight ratio of 1:5, stirring fully, washing with water, and drying to obtain the hydroxyapatite blended rice hull ash agent.
Preferably, the lanthanum nitrate solution has a mass fraction of 5-10%.
Preferably, the ultrasonic power is 300-400W.
Compared with the prior art, the invention has the following beneficial effects:
according to the invention, biomass charcoal, calcium hydroxy phosphate, humic acid and hydroxyapatite are blended with rice hull ash and calcium oxide raw materials to be compounded and prepared, through coordination among various raw materials, bentonite adjustment slurry is used as matrix liquid to carry out coating modification, through coordination among bentonite adjustment slurry and the hydroxyapatite blending rice hull ash, the raw materials are synergistic, the heavy metal adsorption efficiency of the product is enhanced, sustainable adsorption can be realized, and meanwhile, the product has stable performance under the acid corrosion condition.
Detailed Description
The following description of the embodiments of the present invention will be made clearly and fully with reference to the accompanying drawings, in which it is evident that the embodiments described are only some, but not all embodiments of the invention. All other embodiments, which can be made by those skilled in the art based on the embodiments of the invention without making any inventive effort, are intended to be within the scope of the invention.
The soil remediation agent suitable for soil heavy metal pollution comprises the following raw materials in parts by weight:
40-45 parts of bentonite regulating slurry, 15-25 parts of biomass charcoal, 5-10 parts of calcium hydroxy phosphate, 2-5 parts of humic acid, 3-6 parts of hydroxyapatite blending rice hull ash agent and 1-3 parts of calcium oxide;
the preparation method of the repairing agent comprises the following steps: and (3) mixing biomass charcoal, calcium hydroxy phosphate, humic acid and hydroxyapatite with the rice hull ash agent, uniformly stirring and mixing the mixture, and then adding the mixture into bentonite-regulated slurry for continuous mixing to obtain the repairing agent.
The soil restoration agent of the embodiment comprises the following raw materials in parts by weight:
42.5 parts of bentonite regulating slurry, 20 parts of biomass charcoal, 7.5 parts of calcium hydroxy phosphate, 3.5 parts of humic acid, 4.5 parts of hydroxyapatite blending rice hull ash agent and 2 parts of calcium oxide.
The preparation method of the bentonite conditioning slurry of the embodiment comprises the following steps:
s01: feeding bentonite into 130-140 deg.C, heat treating for 10-15min, cooling to 45-55 deg.C at 1-3 deg.C/min, and maintaining for 5-10min;
s02: placing the S01 product into hydrochloric acid solution with the total amount of 3-5 times of the S01 product, then adding sodium dodecyl sulfate with the total amount of 2-5% of the S01 product and yttrium nitrate solution with the total amount of 1-5% of the S01 product, and then carrying out primary stirring and pre-modification;
s03: then adding a silane coupling agent KH560 accounting for 2-5% of the total amount of the S01 product and a Tris buffer solution accounting for 1-3% of the total amount of the S01 product into the S02, carrying out secondary stirring for pre-modification, stirring fully, washing with water, and drying to obtain pre-modified bentonite;
s04: adding the pre-modified bentonite into 3-5 times of the regulating composite liquid, and uniformly stirring to obtain bentonite regulating slurry.
The mass fraction of the hydrochloric acid solution in the embodiment is 1-3%; the mass fraction of the yttrium nitrate solution is 2-5%.
The rotational speed of the primary stirring pre-modification is 350-450r/min, the stirring temperature is 40-45 ℃, and the stirring time is 30-40min; the rotational speed of the secondary stirring pre-modification is 800-1000r/min, the stirring temperature is 46-48 ℃, and the stirring time is 20-30min.
The Tris buffer of this example has a value of 12-15g/L, pH of 8.5-9.0, wherein the concentration of dopamine is 2-3mg/ml.
The adjusting composite liquid of the embodiment comprises the following raw materials in parts by weight:
3-6 parts of chitosan aqueous solution with the mass fraction of 5%, 1-3 parts of sodium alginate aqueous solution with the mass fraction of 2%, 5-10 parts of ethanol solvent, 1-4 parts of N, N-dimethylamide and 2-5 parts of nano magnesium oxide.
The preparation method of the hydroxyapatite blended rice hull ash agent in the embodiment comprises the following steps:
s11: mixing a hydrogen peroxide solution with the mass fraction of 6% and a hydrochloric acid solution with the mass fraction of 2% according to the weight ratio of 1:3 to obtain a hydrochloric acid-hydrogen peroxide solution;
s12: delivering the rice hull ash into 3-5 times hydrochloric acid-hydrogen peroxide solution for ultrasonic dispersion for 10-20min, ending ultrasonic treatment, washing with water, and drying to obtain modified rice hull ash;
s13: adding hydroxyapatite into a lanthanum nitrate solution according to a weight ratio of 1:5, then adding glycol amine accounting for 5-10% of the total amount of the hydroxyapatite, and uniformly stirring to obtain a hydroxyapatite solution;
adding the modified rice hull ash into the hydroxyapatite liquid according to the weight ratio of 1:5, stirring fully, washing with water, and drying to obtain the hydroxyapatite blended rice hull ash agent.
The mass fraction of the lanthanum nitrate solution in the embodiment is 5-10%.
The ultrasonic power of this embodiment is 300-400W.
Example 1.
The soil remediation agent suitable for soil heavy metal pollution comprises the following raw materials in parts by weight:
40 parts of bentonite regulating slurry, 15 parts of biomass charcoal, 5 parts of calcium hydroxy phosphate, 2 parts of humic acid, 3 parts of hydroxyapatite blending rice hull ash agent and 1 part of calcium oxide;
the preparation method of the repairing agent comprises the following steps: and (3) mixing biomass charcoal, calcium hydroxy phosphate, humic acid and hydroxyapatite with the rice hull ash agent, uniformly stirring and mixing the mixture, and then adding the mixture into bentonite-regulated slurry for continuous mixing to obtain the repairing agent.
The preparation method of the bentonite conditioning slurry of the embodiment comprises the following steps:
s01: feeding bentonite into a reactor for heat treatment at 130 ℃ for 10min, cooling to 45 ℃ at a speed of 1 ℃/min, and preserving heat for 5min;
s02: placing the S01 product into hydrochloric acid solution with the total amount being 3 times that of the S01 product, then adding sodium dodecyl sulfate with the total amount being 2% of the S01 product and yttrium nitrate solution with the total amount being 1% of the S01 product, and then carrying out primary stirring and pre-modification;
s03: then adding a silane coupling agent KH560 accounting for 2-5% of the total amount of the S01 product and a Tris buffer solution accounting for 1% of the total amount of the S01 product into the S02, carrying out secondary stirring for pre-modification, stirring fully, washing with water, and drying to obtain pre-modified bentonite;
s04: adding the pre-modified bentonite into 3 times of the regulating composite liquid, and uniformly stirring to obtain bentonite regulating slurry.
The mass fraction of the hydrochloric acid solution of this example was 1%; the mass fraction of the yttrium nitrate solution is 2%.
The rotational speed of the primary stirring pre-modification is 350r/min, the stirring temperature is 40 ℃, and the stirring time is 30min; the rotational speed of the secondary stirring pre-modification is 800r/min, the stirring temperature is 46 ℃, and the stirring time is 20min.
The Tris buffer of this example had a 12g/L, pH value of 8.5, with a dopamine concentration of 2mg/ml.
The adjusting composite liquid of the embodiment comprises the following raw materials in parts by weight:
3 parts of chitosan aqueous solution with the mass fraction of 5%, 1 part of sodium alginate aqueous solution with the mass fraction of 2%, 5 parts of ethanol solvent, 1 part of N, N-dimethylamide and 2 parts of nano magnesium oxide.
The preparation method of the hydroxyapatite blended rice hull ash agent in the embodiment comprises the following steps:
s11: mixing a hydrogen peroxide solution with the mass fraction of 6% and a hydrochloric acid solution with the mass fraction of 2% according to the weight ratio of 1:3 to obtain a hydrochloric acid-hydrogen peroxide solution;
s12: sending the rice hull ash into 3 times hydrochloric acid-hydrogen peroxide solution for ultrasonic dispersion for 10min, ending ultrasonic treatment, washing with water, and drying to obtain modified rice hull ash;
s13: adding hydroxyapatite into a lanthanum nitrate solution according to a weight ratio of 1:5, then adding glycol amine accounting for 5% of the total amount of the hydroxyapatite, and uniformly stirring to obtain a hydroxyapatite solution;
adding the modified rice hull ash into the hydroxyapatite liquid according to the weight ratio of 1:5, stirring fully, washing with water, and drying to obtain the hydroxyapatite blended rice hull ash agent.
The lanthanum nitrate solution of this example was 5% by mass.
The ultrasonic power of this example was 300W.
Example 2.
The soil remediation agent suitable for soil heavy metal pollution comprises the following raw materials in parts by weight:
45 parts of bentonite regulating slurry, 25 parts of biomass charcoal, 10 parts of calcium hydroxy phosphate, 5 parts of humic acid, 6 parts of hydroxyapatite blending rice hull ash agent and 3 parts of calcium oxide;
the preparation method of the repairing agent comprises the following steps: and (3) mixing biomass charcoal, calcium hydroxy phosphate, humic acid and hydroxyapatite with the rice hull ash agent, uniformly stirring and mixing the mixture, and then adding the mixture into bentonite-regulated slurry for continuous mixing to obtain the repairing agent.
The preparation method of the bentonite conditioning slurry of the embodiment comprises the following steps:
s01: feeding bentonite into a reactor at 140 ℃ for heat treatment for 15min, cooling to 55 ℃ at a speed of 3 ℃/min, and preserving heat for 10min;
s02: placing the S01 product into a hydrochloric acid solution which is 5 times of the total amount of the S01 product, then adding sodium dodecyl sulfate which is 5% of the total amount of the S01 product and yttrium nitrate solution which is 5% of the total amount of the S01 product, and then carrying out primary stirring and pre-modification;
s03: then adding a silane coupling agent KH560 accounting for 5 percent of the total amount of the S01 product and a Tris buffer solution accounting for 3 percent of the total amount of the S01 product into the S02, carrying out secondary stirring for pre-modification, stirring fully, washing with water, and drying to obtain pre-modified bentonite;
s04: adding the pre-modified bentonite into 5 times of the regulating composite liquid, and uniformly stirring to obtain bentonite regulating slurry.
The mass fraction of the hydrochloric acid solution of this example was 3%; the mass fraction of the yttrium nitrate solution is 5%.
The rotational speed of the primary stirring pre-modification is 450r/min, the stirring temperature is 45 ℃, and the stirring time is 40min; the rotational speed of the secondary stirring pre-modification is 1000r/min, the stirring temperature is 48 ℃, and the stirring time is 30min.
The Tris buffer of this example had a 15/L, pH value of 9.0, where the concentration of dopamine was 3mg/ml.
The adjusting composite liquid of the embodiment comprises the following raw materials in parts by weight:
6 parts of chitosan aqueous solution with the mass fraction of 5%, 3 parts of sodium alginate aqueous solution with the mass fraction of 2%, 10 parts of ethanol solvent, 4 parts of N, N-dimethylamide and 5 parts of nano magnesium oxide.
The preparation method of the hydroxyapatite blended rice hull ash agent in the embodiment comprises the following steps:
s11: mixing a hydrogen peroxide solution with the mass fraction of 6% and a hydrochloric acid solution with the mass fraction of 2% according to the weight ratio of 1:3 to obtain a hydrochloric acid-hydrogen peroxide solution;
s12: sending the rice hull ash into 5 times hydrochloric acid-hydrogen peroxide solution for ultrasonic dispersion for 20min, ending ultrasonic treatment, washing with water, and drying to obtain modified rice hull ash;
s13: adding hydroxyapatite into a lanthanum nitrate solution according to a weight ratio of 1:5, then adding glycol amine accounting for 10% of the total amount of the hydroxyapatite, and uniformly stirring to obtain a hydroxyapatite solution;
adding the modified rice hull ash into the hydroxyapatite liquid according to the weight ratio of 1:5, stirring fully, washing with water, and drying to obtain the hydroxyapatite blended rice hull ash agent.
The lanthanum nitrate solution of this example has a mass fraction of 10%.
The ultrasonic power of this example was 400W.
Example 3.
The soil remediation agent suitable for soil heavy metal pollution comprises the following raw materials in parts by weight: 42.5 parts of bentonite regulating slurry, 20 parts of biomass charcoal, 7.5 parts of calcium hydroxy phosphate, 3.5 parts of humic acid, 4.5 parts of hydroxyapatite blending rice hull ash agent and 2 parts of calcium oxide.
The preparation method of the repairing agent comprises the following steps: and (3) mixing biomass charcoal, calcium hydroxy phosphate, humic acid and hydroxyapatite with the rice hull ash agent, uniformly stirring and mixing the mixture, and then adding the mixture into bentonite-regulated slurry for continuous mixing to obtain the repairing agent.
The preparation method of the bentonite conditioning slurry of the embodiment comprises the following steps:
s01: feeding bentonite into a reactor for heat treatment at 135 ℃ for 12min, cooling to 50 ℃ at a speed of 2 ℃/min, and preserving heat for 7.5min;
s02: placing the S01 product into a hydrochloric acid solution with the total amount of 4 times of the S01 product, then adding sodium dodecyl sulfate with the total amount of 3.5% of the S01 product and yttrium nitrate with the total amount of 3% of the S01 product, and then carrying out primary stirring and pre-modification;
s03: then adding a silane coupling agent KH560 accounting for 3.5 percent of the total amount of the S01 product and a Tris buffer solution accounting for 2 percent of the total amount of the S01 product into the S02, carrying out secondary stirring for pre-modification, stirring fully, washing with water, and drying to obtain pre-modified bentonite;
s04: adding the pre-modified bentonite into 4 times of the regulating composite liquid, and uniformly stirring to obtain bentonite regulating slurry.
The mass fraction of the hydrochloric acid solution in this example was 2%; the mass fraction of the yttrium nitrate solution is 3.5%.
The rotational speed of the primary stirring pre-modification is 400r/min, the stirring temperature is 42 ℃, and the stirring time is 35min; the rotational speed of the secondary stirring pre-modification is 900r/min, the stirring temperature is 47 ℃, and the stirring time is 25min.
The Tris buffer of this example had a value of 13.5g/L, pH of 8.8, with a dopamine concentration of 2.5mg/ml.
The adjusting composite liquid of the embodiment comprises the following raw materials in parts by weight:
4.5 parts of chitosan aqueous solution with the mass fraction of 5%, 2 parts of sodium alginate aqueous solution with the mass fraction of 2%, 7.5 parts of ethanol solvent, 2.5 parts of N, N-dimethylamide and 3.5 parts of nano magnesium oxide.
The preparation method of the hydroxyapatite blended rice hull ash agent in the embodiment comprises the following steps:
s11: mixing a hydrogen peroxide solution with the mass fraction of 6% and a hydrochloric acid solution with the mass fraction of 2% according to the weight ratio of 1:3 to obtain a hydrochloric acid-hydrogen peroxide solution;
s12: sending the rice hull ash into 4 times hydrochloric acid-hydrogen peroxide solution for ultrasonic dispersion for 15min, ending ultrasonic treatment, washing with water, and drying to obtain modified rice hull ash;
s13: adding hydroxyapatite into a lanthanum nitrate solution according to a weight ratio of 1:5, then adding glycol amine accounting for 7.5% of the total amount of the hydroxyapatite, and uniformly stirring to obtain a hydroxyapatite solution;
adding the modified rice hull ash into the hydroxyapatite liquid according to the weight ratio of 1:5, stirring fully, washing with water, and drying to obtain the hydroxyapatite blended rice hull ash agent.
The lanthanum nitrate solution of this example has a mass fraction of 7.5%.
The ultrasonic power of this example was 350W.
Comparative example 1.
The difference from example 3 is that no bentonite conditioning slurry was added.
Comparative example 2.
The difference from example 3 is that the bentonite material used for the pre-modification in the preparation of bentonite conditioning slurry is replaced by bentonite.
Comparative example 3.
The modification process for the pre-modified bentonite differs from example 3:
putting bentonite into hydrochloric acid solution with the total amount of 4 times of bentonite, adding sodium dodecyl sulfate with the total amount of 3.5% of bentonite and yttrium nitrate solution with the total amount of 3% of bentonite, adding silane coupling agent KH560 with the total amount of 3.5% of bentonite and Tris buffer solution with the total amount of 2% of bentonite into the bentonite, stirring for pre-modification, wherein the stirring speed of the stirring for pre-modification is 900r/min, the stirring temperature is 47 ℃, the stirring time is 35min, stirring is full, and then washing and drying are carried out to obtain the pre-modified bentonite.
Comparative example 4.
The difference from example 3 is that the bentonite conditioning slurry is prepared by replacing the conditioning composite liquid with a chitosan aqueous solution with a mass fraction of 5%.
Comparative example 5.
Unlike example 3, no hydroxyapatite was added to blend the rice hull ash.
Comparative example 6.
Unlike example 3, the hydroxyapatite blended rice hull ash agent was prepared without adding modified rice hull ash.
The products of examples 1-3 and comparative examples 1-6 were tested for performance as follows:
from examples 1-3 and comparative examples 1-6, the adsorption rate of heavy metals in the embodiment 3 of the invention is excellent from 1h to 48h, and the product has excellent adsorption performance stability under the acid corrosion condition;
the product is not added with bentonite adjustment slurry or one of hydroxyapatite and rice hull ash agent, the performance of the product is obviously deteriorated, meanwhile, the stability of acid corrosion is obviously deteriorated, only the bentonite adjustment slurry and the hydroxyapatite are adopted for blending, the synergistic effect is obvious, the pre-modified bentonite in the preparation of the bentonite adjustment slurry is replaced by bentonite raw materials, the modification method of the pre-modified bentonite is different, the adjustment composite liquid in the preparation of the bentonite adjustment slurry is replaced by chitosan aqueous solution with the mass fraction of 5%, the performance of the product is in a deterioration trend, and only the bentonite adjustment slurry and the hydroxyapatite and rice hull ash agent prepared by the method have the most obvious synergistic effect.
It will be evident to those skilled in the art that the invention is not limited to the details of the foregoing illustrative embodiments, and that the present invention may be embodied in other specific forms without departing from the spirit or essential characteristics thereof. The present embodiments are, therefore, to be considered in all respects as illustrative and not restrictive, the scope of the invention being indicated by the appended claims rather than by the foregoing description, and all changes which come within the meaning and range of equivalency of the claims are therefore intended to be embraced therein.
Furthermore, it should be understood that although the present disclosure describes embodiments, not every embodiment is provided with a separate embodiment, and that this description is provided for clarity only, and that the disclosure is not limited to the embodiments described in detail below, and that the embodiments described in the examples may be combined as appropriate to form other embodiments that will be apparent to those skilled in the art.

Claims (7)

1. The soil restoration agent suitable for heavy metal pollution of soil is characterized by comprising the following raw materials in parts by weight:
40-45 parts of bentonite regulating slurry, 15-25 parts of biomass charcoal, 5-10 parts of calcium hydroxy phosphate, 2-5 parts of humic acid, 3-6 parts of hydroxyapatite blending rice hull ash agent and 1-3 parts of calcium oxide;
the preparation method of the repairing agent comprises the following steps: mixing biomass charcoal, calcium hydroxy phosphate, humic acid and hydroxyapatite to prepare rice hull ash agent and calcium oxide, stirring and mixing uniformly, adding into bentonite-regulated slurry, and continuing to mix thoroughly to obtain a repairing agent; the preparation method of the bentonite adjustment slurry comprises the following steps:
s01: feeding bentonite into 130-140 deg.C, heat treating for 10-15min, cooling to 45-55 deg.C at 1-3 deg.C/min, and maintaining for 5-10min;
s02: placing the S01 product into hydrochloric acid solution with the total amount of 3-5 times of the S01 product, then adding sodium dodecyl sulfate with the total amount of 2-5% of the S01 product and yttrium nitrate solution with the total amount of 1-5% of the S01 product, and then carrying out primary stirring and pre-modification;
s03: then adding a silane coupling agent KH560 accounting for 2-5% of the total amount of the S01 product and a Tris buffer solution accounting for 1-3% of the total amount of the S01 product into the S02, carrying out secondary stirring for pre-modification, stirring fully, washing with water, and drying to obtain pre-modified bentonite;
s04: adding the pre-modified bentonite into 3-5 times of the regulating composite liquid, and uniformly stirring to obtain bentonite regulating slurry;
the preparation method of the hydroxyapatite blended rice hull ash agent comprises the following steps:
s11: mixing a hydrogen peroxide solution with the mass fraction of 6% and a hydrochloric acid solution with the mass fraction of 2% according to the weight ratio of 1:3 to obtain a hydrochloric acid-hydrogen peroxide solution;
s12: delivering the rice hull ash into 3-5 times hydrochloric acid-hydrogen peroxide solution for ultrasonic dispersion for 10-20min, ending ultrasonic treatment, washing with water, and drying to obtain modified rice hull ash;
s13: adding hydroxyapatite into a lanthanum nitrate solution according to a weight ratio of 1:5, then adding glycol amine accounting for 5-10% of the total amount of the hydroxyapatite, and uniformly stirring to obtain a hydroxyapatite solution;
adding the modified rice hull ash into the hydroxyapatite liquid according to the weight ratio of 1:5, stirring fully, washing with water, and drying to obtain a hydroxyapatite blended rice hull ash agent; the adjusting composite liquid comprises the following raw materials in parts by weight:
3-6 parts of chitosan aqueous solution with the mass fraction of 5%, 1-3 parts of sodium alginate aqueous solution with the mass fraction of 2%, 5-10 parts of ethanol solvent, 1-4 parts of N, N-dimethylamide and 2-5 parts of nano magnesium oxide.
2. The soil restoration agent suitable for heavy metal pollution of soil according to claim 1, wherein the soil restoration agent is prepared from the following raw materials in parts by weight:
42.5 parts of bentonite regulating slurry, 20 parts of biomass charcoal, 7.5 parts of calcium hydroxy phosphate, 3.5 parts of humic acid, 4.5 parts of hydroxyapatite blending rice hull ash agent and 2 parts of calcium oxide.
3. The soil restoration agent suitable for heavy metal pollution of soil according to claim 1, wherein the mass fraction of the hydrochloric acid solution is 1-3%; the mass fraction of the yttrium nitrate solution is 2-5%.
4. The soil remediation agent suitable for heavy metal pollution of soil according to claim 1, wherein the primary stirring pre-modification speed is 350-450r/min, the stirring temperature is 40-45 ℃, and the stirring time is 30-40min; the rotational speed of the secondary stirring pre-modification is 800-1000r/min, the stirring temperature is 46-48 ℃, and the stirring time is 20-30min.
5. A soil restoration agent for soil heavy metal pollution according to claim 1, wherein said Tris buffer solution has a concentration of 12-15g/L, pH value of 8.5-9.0, and wherein the concentration of dopamine is 2-3mg/ml.
6. The soil restoration agent for soil heavy metal pollution according to claim 1, wherein the lanthanum nitrate solution has a mass fraction of 5-10%.
7. A soil restoration agent suitable for soil heavy metal pollution according to claim 1, wherein the power of said ultrasound is 300-400W.
CN202310841559.6A 2023-07-11 2023-07-11 Soil restoration agent suitable for heavy metal pollution of soil Active CN116554888B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202310841559.6A CN116554888B (en) 2023-07-11 2023-07-11 Soil restoration agent suitable for heavy metal pollution of soil

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202310841559.6A CN116554888B (en) 2023-07-11 2023-07-11 Soil restoration agent suitable for heavy metal pollution of soil

Publications (2)

Publication Number Publication Date
CN116554888A CN116554888A (en) 2023-08-08
CN116554888B true CN116554888B (en) 2023-10-31

Family

ID=87491917

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202310841559.6A Active CN116554888B (en) 2023-07-11 2023-07-11 Soil restoration agent suitable for heavy metal pollution of soil

Country Status (1)

Country Link
CN (1) CN116554888B (en)

Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002309254A (en) * 2001-04-11 2002-10-23 Konica Corp Soil conditioner and method for producing the same
JP2011236411A (en) * 2010-04-13 2011-11-24 Kokyo Sangyo Kk Method of manufacturing soil conditioner
CN102329620A (en) * 2011-10-13 2012-01-25 武汉凯迪工程技术研究总院有限公司 Heavy-metal-polluted acidic soil repairing material as well as preparation method and application thereof
CN103788960A (en) * 2014-03-05 2014-05-14 中国科学院合肥物质科学研究院 Functional fertilizer and repair agents for repairing soil heavy metal
CN105149336A (en) * 2015-09-29 2015-12-16 沈阳化工研究院有限公司 Method and device for remediating soil
CN105419807A (en) * 2015-12-17 2016-03-23 东南大学 Curing agent for heavy metal and organic matter combined polluted soil, and preparation and application methods for curing agent
CN107629798A (en) * 2017-08-11 2018-01-26 湖南省土壤肥料研究所 Acidic soil conditioner and application
CN107746711A (en) * 2017-10-18 2018-03-02 河北大学 A kind of soil heavy metal cadmium passivator and preparation method and application
CN108435782A (en) * 2018-03-23 2018-08-24 河南科技大学 A kind of restorative procedure of heavy metal pollution of soil
CN113234445A (en) * 2021-04-01 2021-08-10 农业农村部环境保护科研监测所 Regulating agent suitable for alkaline soil heavy metal cadmium pollution remediation, preparation method and application
CN116332705A (en) * 2023-06-01 2023-06-27 水利部牧区水利科学研究所 Method for applying organic and inorganic fertilizer by using biochar and improving salinized soil by using biochar

Patent Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002309254A (en) * 2001-04-11 2002-10-23 Konica Corp Soil conditioner and method for producing the same
JP2011236411A (en) * 2010-04-13 2011-11-24 Kokyo Sangyo Kk Method of manufacturing soil conditioner
CN102329620A (en) * 2011-10-13 2012-01-25 武汉凯迪工程技术研究总院有限公司 Heavy-metal-polluted acidic soil repairing material as well as preparation method and application thereof
CN103788960A (en) * 2014-03-05 2014-05-14 中国科学院合肥物质科学研究院 Functional fertilizer and repair agents for repairing soil heavy metal
CN105149336A (en) * 2015-09-29 2015-12-16 沈阳化工研究院有限公司 Method and device for remediating soil
CN105419807A (en) * 2015-12-17 2016-03-23 东南大学 Curing agent for heavy metal and organic matter combined polluted soil, and preparation and application methods for curing agent
CN107629798A (en) * 2017-08-11 2018-01-26 湖南省土壤肥料研究所 Acidic soil conditioner and application
CN107746711A (en) * 2017-10-18 2018-03-02 河北大学 A kind of soil heavy metal cadmium passivator and preparation method and application
CN108435782A (en) * 2018-03-23 2018-08-24 河南科技大学 A kind of restorative procedure of heavy metal pollution of soil
CN113234445A (en) * 2021-04-01 2021-08-10 农业农村部环境保护科研监测所 Regulating agent suitable for alkaline soil heavy metal cadmium pollution remediation, preparation method and application
CN116332705A (en) * 2023-06-01 2023-06-27 水利部牧区水利科学研究所 Method for applying organic and inorganic fertilizer by using biochar and improving salinized soil by using biochar

Also Published As

Publication number Publication date
CN116554888A (en) 2023-08-08

Similar Documents

Publication Publication Date Title
CN111349421B (en) Environment-friendly dust suppressant and preparation method thereof
CN109609134B (en) Stable curing agent for arsenic-polluted soil and slag and preparation method thereof
CN104496251A (en) Liquid hexavalent chromium reducing agent and preparation method thereof, cement and preparation method thereof
CN115226731B (en) Environment-friendly slow-release archival anti-corrosion insect-resistant bacteriostatic agent and preparation method thereof
CN106317518B (en) Warm-mixed asphalt warm-mixing agent and its application process
CN116554888B (en) Soil restoration agent suitable for heavy metal pollution of soil
CN102815853A (en) Harmless mud processing method for sewage treatment plant
CN105665969B (en) A kind of production method of corrosion-resisting steel welding welding rod special for special
CN106010572A (en) Alkali-affected soil restoration preparation and preparation method thereof
CN114230227B (en) Anti-mud concrete glue reducing agent and preparation method and application thereof
CN108752127A (en) A kind of biomass castoff soil conditioner in improvement salt-soda soil
CN111518531A (en) Composite cross-linking agent and preparation method thereof, and delayed cross-linking profile control agent and preparation method thereof
CN111676020B (en) Composite soil remediation agent and preparation method and application thereof
CN110272228A (en) The low peculiar smell rubber-asphalt mixture of road engineering
CN116586043A (en) Preparation method and application of alginic acid composite gel
CN111320983A (en) Soil remediation agent, preparation method thereof and soil remediation method
CN113136087A (en) High-viscosity-reduction warm mixing agent for warm-mixed asphalt
JP4216061B2 (en) Rheology modifier kit
CN111793501A (en) Soil conditioner and preparation method thereof
CN112125752A (en) High-nutrition soil remediation regulator and preparation method thereof
CN114507532A (en) Preparation and application of dolomite attapulgite soil improvement material
CN101481470B (en) Oxidized graphite / rare earth stabiliser for PVC and preparation thereof
CN114307030A (en) Fly ash heavy metal curing agent, preparation method thereof and fly ash treatment method
CN112480931A (en) Passivating agent for treating cadmium and arsenic combined pollution of paddy field and preparation method and application thereof
CN108517211A (en) A kind of soil conditioner and preparation method thereof with height suspension stability

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