Patent Application
20240091739
This patent application claims the benefit and priority of Chinese Patent Application No. 202211100599.7 filed with the China National Intellectual Property Administration on Sep. 8, 2022, the disclosure of which is incorporated by reference herein in its entirety as part of the present application.
The present disclosure belongs to the technical field of soil pollution remediation, and relates to a mercapto group-loaded layered double hydroxide (LDH)-based magnetic composite particle, and a preparation method and use thereof.
Cadmium pollution in farmland soil has become one of the global soil environmental problems and then attracted widespread attention from governments and the public. Cadmium pollution in soil can cause excessive cadmium in rice, wheat and other food crops, threatening human and organism health and food safety production. Therefore, remediating cadmium-contaminated farmland soils and providing guarantee for the safe production of food crops are the current research hotspots and difficulties in the field of soil and environment remediation.
Cadmium is one of the most toxic heavy metals with teratogenic, carcinogenic, and mutagenic effects. Currently, there are two main strategies for the remediation of cadmium-contaminated soils. One is to remove heavy metals in the soil; the other is to immobilize heavy metals in the soil and reduce their environmental risks. For a long time, the remediation of cadmium polluted soil has been mainly based on the chemical stabilization of adding stabilizers to the soil. In this technology, lime, phosphate, humus, biochar or various organic/inorganic composite porous materials are used as stabilizers to adsorb and immobilize heavy metals, for example, bioavailable cadmium in the soil, thereby reducing the biotoxicity of heavy metals in the soil. However, this technology does not reduce the cadmium content in the soil, and the change of soil environment may cause the risk of releasing of immobilized cadmium. In terms of reductive removal of cadmium from the soil, phytoextraction technology is relatively emerging. But it has a long remediation period and is easily affected by biological and climatic conditions. Chemical leaching using chelating agents and the like can effectively reduce the cadmium content in the soil, but generally leads to deterioration of soil quality and health, thereby seriously affecting the agricultural production of remediated soil. Some researchers remove soil heavy metals by using waste textiles loaded with layered double hydroxides as adsorbents, which can remove heavy metals by separating the waste textiles from soil. However, the netted waste textiles may not be in sufficient contact with the soil, and it is difficult to manipulate for large areas of cadmium-contaminated farmland soil. Therefore, it is of great practical significance to seek a new economical and efficient method to remove cadmium from contaminated soil to ensure soil ecological security and food security.
Technical problems to be solved: Aiming at the shortcomings and deficiencies of existing methods for removing cadmium from contaminated farmland soil, the present disclosure provides for the first time a mercapto group-loaded layered double hydroxide (LDH)-based magnetic composite particle (hereafter referred to as magnetic composite particles), and a preparation method and use thereof. The magnetic particle reacts with cadmium in the soil, and then the magnetic particle that adsorbs the cadmium in the soil is separated by a magnet, thereby fundamentally reducing the total content of cadmium in the soil.
Technical solutions: The present disclosure provides a method for preparing a mercapto group-loaded LDH-based magnetic composite particle, including the following steps:
a mass ratio of the product to the water is in a range of 1:(8.3-18.3), a volume ratio of the ethanol to the water is 1:10.4, and a volume ratio of the KH-580 to the ethanol is in a range of 1:(7.9-8.3);
S7) leaving the magnetic bead obtained in S6 to harden in the calcium chloride solution, and then washing a hardened magnetic bead with water and drying, to obtain the mercapto group-loaded LDH-based magnetic composite particle.
In some embodiments, the water-soluble divalent metal salt is a magnesium salt selected from the group consisting of magnesium nitrate and magnesium chloride; and the water-soluble trivalent metal salt is an aluminum salt selected from the group consisting of aluminum nitrate and aluminum chloride; and a mass ratio of the magnesium salt to the aluminum salt is in a range of 1:(0.49-0.73), and the mixed salt solution has a total mixed salt mass concentration of from 20 g/L to 40 g/L.
In some embodiments, in S2), a volume ratio of the ammonia water to the mixed salt solution is in a range of 1:(2-2.5), and the ammonia water has a concentration of 6 mol/L to 7 mol/L; and the reaction I in S2 is conducted at a temperature of 50° C. to 100° C. for 10 to 20 hours.
In some embodiments, in S5), the ferroferric oxide and the sodium alginate each have a mass concentration of 9 g/L to 10 g/L in the homogeneous mixed solution; a mass ratio of the mercapto group-loaded LDH to the ferroferric oxide is 3:2; a mass ratio of the mercapto group-loaded LDH to the sodium alginate is 3:2; the stirring in S5) is performed at a rate of 2,000 rpm to 5,000 rpm for 2 h to 6 h to obtain the homogeneous mixed solution; and the homogeneous mixed solution is subjected to an ultrasonic treatment for 15 min to 60 min before pumping into the calcium chloride solution.
In some embodiments, in S6), the calcium chloride solution has a mass concentration of 2% to 4%.
In some embodiments, in S7), the magnetic bead is left to harden in the calcium chloride solution for 10 h to 24 h, and the drying is conducted at a temperature of 50° C. to 110° C.
The present disclosure further provides a mercapto group-loaded LDH-based magnetic composite particle prepared by the method as described in above technical solutions.
The present disclosure further provides use of the mercapto group-loaded LDH-based magnetic composite particle as described in above technical solutions for the removal of cadmium from soil.
In some embodiments, the use includes
In some embodiments, the use further includes
the recovered mercapto group-loaded LDH-based magnetic composite particle is regenerated for 0.5 h to 4 h.
Beneficial effects:by the method of preparing the mercapto group-loaded LDH-based magnetic composite particle according to the present disclosure, the magnetic beads are obtained by a one-step method that is easy to implement under mild conditions, thus greatly reducing the harsh experimental conditions such as heating, reflux, and calcination in the existing loading or modification methods. The LDHs used have a three-dimensional pore structure and a large specific surface area, which can enhence the adsorption of cadmium ions in the soil; meanwhile, the selective adsorption of cadmium in soil can be enhanced by loaded mercapto functional groups. The mercapto group-loaded LDH-based magnetic composite particle has magnetic properties, and has a particle size of 0.8 mm to 1.9 mm (average particle size of 1.4 mm), which is different from that of soil clay and silt particles. This can greatly improve the separation efficiency of the magnetic particles in flooded soils and reduce the difficulty of their separation. Moreover, in the mercapto group-loaded LDH-based magnetic composite particle, LDH functions as an adsorption component, which enhances the structural strength of sodium alginate, and is beneficial for applications in soil. The mercapto group-loaded LDH-based magnetic composite particle is easy to regenerate and recycle, and has the advantages of low cost, and applicability to different scales of remediation in cadmium-contaminated farmland soil. In this way, the cadmium content in the soil could be fundamentally reduced, thereby reducing secondary pollution.
The present disclosure will be described in further detail below with reference to examples and accompanying drawings, but examples of the present disclosure are not limited thereto.
The experimental methods in the following examples, unless otherwise specified, are conventional methods. The chemical reagents used in each example, unless otherwise specified, are commercially available conventional products, and can be obtained through commercial purchase.
Step I: Preparation of mercapto group-loaded LDH-based magnetic composite particle
S1) 92.28 g of Mg(NO3)2·6H2O and 45.0 g of Al(NO3)3·9H2O were dissolved in 300 mL of deionized water, and stirred evenly in a 2.0 L beaker on a heated magnetic stirrer at 60° C., obtaining a mixed salt solution.
S2) 600 mL of 50% (v/v) ammonia water was slowly pumped into the mixed salt solution obtained in S1 for the co-precipitation reaction with continuous stirring; while a pH value of the resulting reaction system was monitored to be 9.65 during the co-precipitation. After the ammonia water was completely added, 80.0 mL of concentrated ammonia water was further pumped into the reaction system such that the pH value of the resulting reaction system was stabilized at 9.75. The resulting mixture was left to stand at 60° C. and aged for 12 h (overnight).
S3) A mixture obtained in S2 was divided into a 200 mL centrifuge bottle, centrifuged at 3,000 rpm for 10 min on a centrifuge, and taken out. A supernatant obtained after centrifugation was discarded. Deionized water was added to a resulting residue and they were mixed evenly, an obtained mixture was then centrifuged again and a resulting supernatant was discarded. Washing was conducted in this way and repeated 4 to 5 times, and an obtained washed substance was centrifuged to obtain a product.
S4) 38.4 mL of absolute ethanol, 4.8 mL of KH-580, and 400 mL of deionized water were added to the product obtained in S3 to form a mixed solution, and the mixed solution was stirred mechanically at room temperature for 2.5 h to obtain mercapto group-loaded LDH, wherein a volume ratio of the absolute ethanol to the deionized water was 1:10.4, and a volume ratio of the KH-580 to the absolute ethanol was 1:8.0.
S5) The mercapto group-loaded LDH obtained in S4 was mixed with 20.0 g of a ferroferric oxide powder (or iron powder) and 20.0 g of sodium alginate. 1,600 mL of deionized water was further added thereto. The resulting mixture was stirred at 4,000 rpm for 5 h in a stirrer to obtain a homogeneous mixed solution.
S6) The homogeneous mixed solution obtained in S5 was subjected to ultrasonic treatment in an ultrasonic cleaner for 30 min to remove air bubbles in the mixed solution, and then added dropwise to a calcium chloride solution through a pump to form magnetic beads with a particle size of 2 mm to 4 mm.
S7) The magnetic beads obtained in S6 were left to harden in the calcium chloride solution for 14 h (overnight), and then washed 5 times with tap water. The washed magnetic beads were evenly distributed on a tray, and dried at 100° C. for 5 h to obtain the mercapto group-loaded LDH-based magnetic composite particle.
Step II: Removal of cadmium in the contaminated farmland soil
A typical cadmium-contaminated farmland soil collected from Taicang City, Jiangsu Province, China was selected, with a soil type of Anthrosols. The soil total cadmium content and cadmium content extracted with 0.43 mol/L nitric acid are shown in Table 1.
S8) 2.0 g of the mercapto group-loaded LDH-based magnetic composite particle obtained in S7 was mixed with 10.0 g of the cadmium-contaminated farmland soil and 20 mL of water. The resulting mixture was mixed evenly in a shaker at room temperature to allow a full reaction. Alternatively, 2.0 g of the mercapto group-loaded LDH-based magnetic composite particle obtained in S7 was added to 10.0 g of flooded cadmium-contaminated farmland soil.
S9) After stirring and mixing evenly, the mercapto group-loaded LDH-based magnetic composite particle interacted with the soil for 15 h.
Step III: Recovery of mercapto group-loaded LDH-based magnetic composite particle
S10) A bar-shaped magnet with a magnetic field strength of 300 mT was inserted into the flooded soil after the reaction in S9, and a stirring was performed. After the mercapto group-loaded LDH-based magnetic composite particle was attracted by the magnet, the magnet was taken out. The mercapto group-loaded LDH-based magnetic composite particles attracted on a surface of the magnetic bar were removed. The magnetic bar was inserted again into the flooded soil after the reaction to check whether the mercapto group-loaded LDH-based magnetic composite particle was fully recovered.
S11) The mercapto group-loaded LDH-based magnetic composite particles recovered in S10 were washed 5 times with tap water and dried at 100° C. The weight of recovered mercapto group-loaded LDH-based magnetic composite particle was 1.97 g±0.01 g, and the recovery rate of mercapto group-loaded LDH-based magnetic composite particle was 98.3%.
The original soil and the soil obtained after recovering mercapto group-loaded LDH-based magnetic composite particle were naturally air-dried, ground, and sieved with a 10-mesh sieve, obtaining those passing through the 10-mesh sieve. 2.00 g of soil passing through the 10-mesh sieve was put into a centrifuge tube, and 20.0 mL of 0.43 mol/L nitric acid was added thereto. The centrifuge tubes were shaken at 25° C. for 4 h, and centrifuged. A resulting supernatant was passed through a 0.45 μm filter membrane, and cadmium concentration in the supernatant was determined by inductively coupled plasma-mass spectrometry (ICP-MS). A cadmium removal rate was calculated as follows:
As shown in
Step IV: Regeneration and reuse of mercapto group-loaded LDH-based magnetic composite particles
S12) The recovered mercapto group-loaded LDH-based magnetic composite particles obtained in S11 were added to 20 mL of 0.10 mol/L MgCl2 solution, and stirred or shaken to allow reaction for 1.00 h.
S13) The mercapto group-loaded LDH-based magnetic composite particle obtained in S12 was withdrawn, washed with tap water, and dried at 100° C. to obtain a regenerated mercapto group-loaded LDH-based magnetic composite particle.
Step I: Preparation of mercapto group-loaded LDH-based magnetic composite particle
S1) 15.38 g of Mg(NO3)2·6H2O and 7.50 g of Al(NO3)3·9H2O were dissolved in 50 mL of deionized water, and stirred evenly in a 1.0 L beaker on a heated magnetic stirrer at 60° C., obtaining a mixed salt solution.
S2) 100 mL of 50% (v/v) ammonia water was slowly pumped into the mixed salt solution obtained in S1 for the co-precipitation reaction with continuous stirring; while a pH value of the resulting reaction system was monitored to be 9.6 during the co-precipitation. After adding the ammonia water, 80.0 mL of concentrated ammonia water was further pumped into the reaction system such that the pH value of the resulting reaction system was stabilized at 9.75. The resulting mixture was left to stand at 60° C. and aged for 12 h.
S3) A mixture obtained in S2 was centrifuged at 3,000 rpm for 10 min on a centrifuge, and taken out. A supernatant obtained after centrifugation was discarded. Deionized water was added to a resulting residue and they were mixed evenly, an obtained mixture was then centrifuged again and a resulting supernatant was discarded. Washing was conducted in this way and repeated 5 times, and an obtained washed substance was centrifuged to obtain a product.
S4) 6.4 mL of absolute ethanol, 0.81 mL of KH-580, and 66.7 mL of deionized water were added to the product obtained in S3 to form a mixed solution, and the mixed solution was stirred mechanically at room temperature for 2.5 h to obtain mercapto group-loaded LDH, wherein a volume ratio of the absolute ethanol to the deionized water was 1:10.4, and a volume ratio of the KH-580 to the absolute ethanol was 1:7.9.
S5) The mercapto group-loaded LDH obtained in S4 was mixed with 3.33 g of a ferroferric oxide powder (or iron powder) and 3.33 g of sodium alginate. 266.7 mL of deionized water was further added thereto. The resulting mixture was stirred at 4,000 rpm for 4.0 h in a stirrer to obtain a homogeneous mixed solution.
S6) The homogeneous mixed solution obtained in S5 was subjected to ultrasonic treatment in an ultrasonic cleaner for 30 min to remove air bubbles in the mixed solution, and then added dropwise to a calcium chloride solution through a pump to form magnetic beads with a particle size of 2 mm to 4 mm.
S7) The magnetic beads obtained in S6 were left to harden in the calcium chloride solution for 12 h (overnight), and then washed 5 times with tap water. The washed magnetic beads were evenly distributed on a tray, and dried at 100° C. for 5 h to obtain the mercapto group-loaded LDH-based magnetic composite particle.
The particle size of the mercapto group-loaded LDH-based magnetic composite particle obtained in Example 2 is shown in
Step II: Removal of Cadmium in Farmland Soil
A typical cadmium-contaminated farmland soil collected from Baiyin City, Gansu Province, China was selected, with a soil type of Aridisols. The soil total cadmium content and cadmium content extracted with 0.43 mol/L HNO3 are shown in Table 2.
S8) 2.0 g of the mercapto group-loaded LDH-based magnetic composite particle obtained in S7 was mixed with 10.0 g of the cadmium-contaminated farmland soil and 20 mL of water. The resulting mixture was mixed evenly in a shaker at room temperature to allow a full reaction.
Alternatively, 2.0 g of the mercapto group-loaded LDH-based magnetic composite particle obtained in S7 was added to 10.0 g of flooded cadmium-contaminated farmland soil.
S9) After stirring and mixing evenly, the mercapto group-loaded LDH-based magnetic composite particle interacted with the soil for 5 h.
Step III: Recovery of mercapto group-loaded LDH-based magnetic composite particles
S10) A bar-shaped magnet with a magnetic field strength of 300 mT was inserted into the flooded soil after the reaction in S9, and a stirring was performed. After the mercapto group-loaded LDH-based magnetic composite particle was attracted by the magnet, the magnet was taken out. The mercapto group-loaded LDH-based magnetic composite particles attracted on a surface of the magnetic bar were removed. The magnetic bar was inserted again into the flooded soil after the reaction to check whether the mercapto group-loaded LDH-based magnetic composite particle was fully recovered.
S11) The mercapto group-loaded LDH-based magnetic composite particles recovered in S10 were washed 5 times with tap water and dried at 100° C. The weight of recovered mercapto group-loaded LDH-based magnetic composite particles was 1.98 g, and the recovery rate of mercapto group-loaded LDH-based magnetic composite particle was 98.8%.
The original soil and the soil obtained after recovering mercapto group-loaded LDH-based magnetic composite particle were naturally air-dried, ground, and sieved with a 10-mesh sieve, obtaining those passing through the 10-mesh sieve. 2.00 g of soil passing through the 10-mesh sieve was put into a centrifuge tube, and 20.0 mL of 0.43 mol/L nitric acid was added thereto. The centrifuge tubes were shaken at 25° C. for 4 h, and centrifuged. A resulting supernatant was passed through a 0.4511m filter membrane, and cadmium concentration in the supernatant was determined by inductively coupled plasma-mass spectrometry (ICP-MS).
A cadmium removal rate was calculated according to Equation (1). As shown in
Step IV: Regeneration and reuse of mercapto group-loaded LDH-based magnetic composite particles
S12) The recovered mercapto group-loaded LDH-based magnetic composite particles obtained in S11 were added to 15 mL of 0.10 mol/L MgCl2 solution, and stirred or shaken to allow reaction for 1.00 h.
S13) The mercapto group-loaded LDH-based magnetic composite particles obtained in S12 were withdrawn, washed with tap water, and dried at 100° C. to obtain regenerated mercapto group-loaded LDH-based magnetic composite particles.
Step I: Preparation of mercapto group-loaded LDH-based magnetic composite particle
S1) 92.28 g of Mg(NO3)2·6H2O and 45.0 g of Al(NO3)3·9H2O were dissolved in 300 mL of deionized water, and stirred evenly in a 2.0 L beaker on a heated magnetic stirrer at 60° C., obtaining a mixed salt solution.
S2) 600 mL of 50% (v/v) ammonia water was slowly pumped into the mixed salt solution obtained in S1 for the co-precipitation reaction with continuous stirring, while a pH value of the resulting reaction system was monitored to be 9.75. After the ammonia water was completely added, 80.0 mL of concentrated ammonia water was further pumped into the reaction system such that the pH value of the resulting reaction system was stabilized at 9.75. The resulting mixture was left to stand at 60° C. and aged for 15 h (i.e., overnight).
S3) The mixture obtained in S2 was divided into a 250 mL centrifuge bottles, centrifuged at 4,000 rpm for 8 min, and the supernatant obtained after centrifugation was discarded. Deionized water was added to a resulting residue again, and they were mixed evenly. An obtained mixture was then centrifuged again and the supernatant was discarded. Washing was conducted in this way and repeated 4 to 5 times, and an obtained washed substance was centrifuged to obtain a product.
S4) 38.4 mL of absolute ethanol, 4.8 mL of KH-580, and 400 mL of deionized water were added to the product obtained in S3 to form a mixed solution, and the mixed solution was stirred mechanically at room temperature for 2.5 h to obtain mercapto group-loaded LDH, wherein a volume ratio of the absolute ethanol to the deionized water was 1:10.4, and a volume ratio of the KH-580 to the absolute ethanol was 1:8.0.
S5) The mercapto group-loaded LDH obtained in S4 was mixed with 20.0 g of a ferroferric oxide powder (or iron powder) and 20.0 g of sodium alginate. 1,600 mL of deionized water was further added thereto. The resulting mixture was stirred at 4,000 rpm for 4 h in a stirrer to obtain a homogeneous mixed solution.
S6) The homogeneous mixed solution obtained in S5 was subjected to ultrasonic treatment in an ultrasonic cleaner for 30 min to remove air bubbles in the mixed solution, and then added dropwise to a calcium chloride solution through a pump to form magnetic beads with a particle size of 2 mm to 4 mm.
S7) The magnetic beads obtained in S6 were left to harden in the calcium chloride solution for 14 h (overnight), and then washed 5 times with tap water afterward. The washed magnetic beads were evenly distributed on a tray, and dried at 100° C. for 5 h to obtain the mercapto group-loaded LDH-based magnetic composite particle.
Step II: Removal of Cadmium in Farmland Soil
3 types of typical cadmium-contaminated farmland soil were selected. The available cadmium (extracted by diethylenetriaminepentaacetic acid (DTPA) and triethylamine solution (TEA) according to NY/T 890-2004, China) in soils are shown in Table 3.
S8) 3.0 g of the mercapto group-loaded LDH-based magnetic composite particles obtained in S7 were mixed with 15.0 g of the cadmium-contaminated farmland soil and 30 mL of water. The resulting mixture was mixed evenly in a shaker at room temperature to allow a full reaction. Alternatively, 3.0 g of the mercapto group-loaded LDH-based magnetic composite particles obtained in S7 were added to 15.0 g of flooded cadmium-contaminated farmland soil.
S9) After stirring and mixing evenly, the mercapto group-loaded LDH-based magnetic composite particle interacted with the soil for 5 h.
Step III: Recovery of Mercapto Group-Loaded LDH-Based Magnetic Composite Particle
S10) A bar-shaped magnet with a magnetic field strength of 300 mT was inserted into the flooded soil after the reaction in S9, and a stirring was performed. After the mercapto group-loaded LDH-based magnetic composite particle was attracted by the magnet, the magnet was taken out. The mercapto group-loaded LDH-based magnetic composite particles attracted on a surface of the magnetic bar were removed. The magnetic bar was inserted again into the flooded soil after the reaction to check whether the mercapto group-loaded LDH-based magnetic composite particle was fully recovered.
S11) The mercapto group-loaded LDH-based magnetic composite particles recovered in S10 were washed 5 times with tap water and dried at 100° C. The weights of recovered mercapto group-loaded LDH-based magnetic composite particles recovered after treating solis from Xiangtan City in Hunan Province of China; Taizhou City in Zhejiang Province of China, and Baiyin City in Gansu Province of China were 3.00, 3.01, and 3.01 g, respectively, indicating that the recovery rate of mercapto group-loaded LDH-based magnetic composite particle was 100%.
The original soil and the soil obtained after recovering mercapto group-loaded LDH-based magnetic composite particle were naturally air-dried, ground, and sieved with a 10-mesh sieve, obtaining those passing through a 10-mesh sieve. 5.00 g of soil passing through the 10-mesh sieve was put into a centrifuge tube, and 10.0 mL of a DTPA extraction agent (0.005 mol/L diethylenetriaminepentaacetic acid (DTPA), 0.01 mol/L CaCl 2, and 0.1 mol/L triethylamine (TEA)) was added thereto. The resulting mixture was shaken at 25° C. for 2 h, and centrifuged. A resulting supernatant was passed through a 0.45 μm filter membrane, and cadmium concentration in the supernatant was determined by inductively coupled plasma-mass spectrometry (ICP-MS).
Cadmium removal rate was calculated according to Equation (1). As shown in
Step I: Preparation of mercapto group-loaded LDH-based magnetic composite particle
S1) 92.28 g of Mg(NO3)2·6H2O and 45.0 g of Al(NO3)3·9H2O were dissolved in 300 mL of deionized water, and stirred evenly in a 2.0 L beaker on a heated magnetic stirrer at 60° C., obtaining a mixed salt solution.
S2) 600 mL of 50% (v/v) ammonia water was slowly pumped into the mixed salt solution obtained in S1 for the co-precipitation reaction with constantly stirring; while a pH value of the resulting reaction system was monitored to be 9.75 during the co-precipitation. After the ammonia water was completely added, 80.0 mL of concentrated ammonia water was further added dropwise into the reaction system such that the pH value of the resulting reaction system was stabilized at 9.75. The resulting mixture was left to stand at 60° C. and aged for 12 h. A resulting mixed solution had a pH value of 9.73.
S3) A mixture obtained in S2 was divided into a 200 mL centrifuge bottle, centrifuged at 4,000 rpm for 8 min on a centrifuge, and withdrawn. A supernatant obtained after centrifugation was discarded. Deionized water was added to a resulting residue, and they were mixed evenly, an obtained mixture was then centrifuged again and a resulting supernatant was discarded. Washing was conducted in this way and repeated 5 times, and an obtained washed substance was centrifuged to obtain a product.
S4) 38.4 mL of absolute ethanol, 4.8 mL of KH-580, and 400 mL of deionized water were added to the product obtained in S3 to form a mixed solution, and the mixed solution was stirred mechanically at room temperature for 3.0 h to obtain mercapto group-loaded LDH, wherein a volume ratio of the ethanol to the deionized water was 1:10.4, and a volume ratio of the KH-580 to the absolute ethanol was 1:8.0.
S5) The mercapto group-loaded LDH obtained in S4 were mixed with 20.0 g of a ferroferric oxide powder (or iron powder) and 20.0 g of sodium alginate. 1,600 mL of deionized water was further added thereto. The resulting mixture was stirred at 4,000 rpm for 5 h in a stirrer to obtain a homogeneous mixed solution.
S6) The homogeneous mixed solution obtained in S5 was subjected to ultrasonic treatment in an ultrasonic cleaner for 30 min to remove air bubbles in the mixed solution, and then added dropwise to a calcium chloride solution with a mass fraction of 2.5% through a pump to form magnetic beads with a particle size of 2 mm to 4 mm.
S7) The magnetic beads obtained in S6 were left to harden in the calcium chloride solution for 12 h, and then washed 5 times with tap water. The washed magnetic beads were evenly distributed on a tray, and dried at 100° C. for 5 h to obtain the mercapto group-loaded LDH-based magnetic composite particle.
Step II: Removal of Cadmium in Farmland Soil
A typical cadmium-contaminated farmland soil collected from Taicang City, Jiangsu Province, China was selected, with a soil type of Anthrosols. The soil total cadmium content and cadmium content extracted with 0.43 mol/L nitric acid are shown in Table 4.
S8) 1.5 g of the mercapto group-loaded LDH-based magnetic composite particle obtained in S7 was mixed with 15.0 g of the cadmium-contaminated farmland soil and 30 mL of water. The resulting mixture was mixed evenly in a shaker at room temperature to allow a full reaction. Alternatively, 1.5 g of the mercapto group-loaded LDH-based magnetic composite particle obtained in S7 was added to 15.0 g of flooded cadmium-contaminated farmland soil.
S9) After stirring and mixing evenly, the mercapto group-loaded LDH-based magnetic composite particle interacted with the soil for 5 h.
Step III: Recovery of mercapto group-loaded LDH-based magnetic composite particle
S10) A bar-shaped magnet with a magnetic field strength of 300 mT was inserted into the flooded soil after the reaction in S9, and a stirring was performed. After the mercapto group-loaded LDH-based magnetic composite particle was attracted by the magnet, the magnet was taken out. The mercapto group-loaded LDH-based magnetic composite particles attracted on a surface of the magnetic bar were removed. The magnetic bar was inserted again into the flooded soil after the reaction to check whether the mercapto group-loaded LDH-based magnetic composite particle was fully recovered.
S11) The mercapto group-loaded LDH-based magnetic composite particle recovered in S10 was washed 5 times with tap water and dried at 100° C. The weight of recovered mercapto group-loaded LDH-based magnetic composite particle was weighed.
The original soil and the soil obtained after recovering mercapto group-loaded LDH-based magnetic composite particle were naturally air-dried, ground, and sieved with a 10-mesh sieve, obtaining those passing through the 10-mesh sieve. 2.00 g of soil passing through the 10-mesh sieve was put into a centrifuge tube, and 20.0 mL of 0.43 mol/L nitric acid was added thereto. The resulting mixture was shaken at 25° C. for 4 h, and centrifuged. A resulting supernatant was passed through a 0.45 μm filter membrane, and a cadmium concentration in the supernatant was determined by inductively coupled plasma-mass spectrometry (ICP-MS).
Step IV: Regeneration and reuse of mercapto group-loaded LDH-based magnetic composite particles
S12) The recovered mercapto group-loaded LDH-based magnetic composite particles obtained in S11 were added to 30 mL of 0.10 mol/L MgCl2 solution, and stirred or shaken to allow reaction for 1.00 h. Alternatively, the recovered mercapto group-loaded LDH-based magnetic composite particle was added to 30 mL of 0.01 mol/L Na2S2O3 solution, and stirred or shaken to allow reaction for 1.00 h.
S13) The mercapto group-loaded LDH-based magnetic composite particle obtained in S12 was taken out, washed with tap water, and dried at 100° C. to obtain a regenerated mercapto group-loaded LDH-based magnetic composite particle.
S14) 1.5 g of the regenerated mercapto group-loaded LDH-based magnetic composite particle obtained in S13 was mixed with 15.0 g of original contaminated soil in Taicang City, Jiangsu Province, China and 30 mL of water. The resulting mixture was mixed evenly in a shaker at room temperature to allow a full reaction. Alternatively, the regenerated mercapto group-loaded LDH-based magnetic composite particle obtained in S13 was added to 15.0 g of flooded cadmium-contaminated farmland soil.
S15) After stirring and mixing evenly, the mercapto group-loaded LDH-based magnetic composite particle interacted with the soil for 5 h.
Steps S10 to S15 were repeated sequentially, to obtain the recovery rate of 2nd utilization (i.e., treating with one regenerated after the first utilization) and 3rd utilization (i.e., treating with one regenerated after the second utilization) of the mercapto group-loaded LDH-based magnetic composite particle and the removal rate of cadmium in the original cadmium-contaminated farmland soil.
A cadmium removal rate was calculated according to Equation (1), and a cadmium removal rate in soil was obtained.
As shown in
The above embodiments are merely preferred solutions of the present disclosure and are not intended to limit the present disclosure in any form, and other variations and modifications may be made without departing from the technical solutions of the present disclosure as set forth in the appended claims.
| Number | Date | Country | Kind |
|---|---|---|---|
| 202211100599.7 | Sep 2022 | CN | national |
