CN111592678A - Preparation method and application of porous magnetic ion exchange resin - Google Patents

Preparation method and application of porous magnetic ion exchange resin Download PDF

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Publication number
CN111592678A
CN111592678A CN202010334071.0A CN202010334071A CN111592678A CN 111592678 A CN111592678 A CN 111592678A CN 202010334071 A CN202010334071 A CN 202010334071A CN 111592678 A CN111592678 A CN 111592678A
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ion exchange
exchange resin
magnetic ion
porous magnetic
ferroferric oxide
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杨滨
钟杰
应光国
冯勇
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South China Normal University
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South China Normal University
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    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08JWORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
    • C08J9/00Working-up of macromolecular substances to porous or cellular articles or materials; After-treatment thereof
    • C08J9/28Working-up of macromolecular substances to porous or cellular articles or materials; After-treatment thereof by elimination of a liquid phase from a macromolecular composition or article, e.g. drying of coagulum
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/42Treatment of water, waste water, or sewage by ion-exchange
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08FMACROMOLECULAR COMPOUNDS OBTAINED BY REACTIONS ONLY INVOLVING CARBON-TO-CARBON UNSATURATED BONDS
    • C08F212/00Copolymers of compounds having one or more unsaturated aliphatic radicals, each having only one carbon-to-carbon double bond, and at least one being terminated by an aromatic carbocyclic ring
    • C08F212/02Monomers containing only one unsaturated aliphatic radical
    • C08F212/04Monomers containing only one unsaturated aliphatic radical containing one ring
    • C08F212/14Monomers containing only one unsaturated aliphatic radical containing one ring substituted by heteroatoms or groups containing heteroatoms
    • C08F212/16Halogens
    • C08F212/18Chlorine
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08KUse of inorganic or non-macromolecular organic substances as compounding ingredients
    • C08K3/00Use of inorganic substances as compounding ingredients
    • C08K3/18Oxygen-containing compounds, e.g. metal carbonyls
    • C08K3/20Oxides; Hydroxides
    • C08K3/22Oxides; Hydroxides of metals
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08KUse of inorganic or non-macromolecular organic substances as compounding ingredients
    • C08K9/00Use of pretreated ingredients
    • C08K9/04Ingredients treated with organic substances
    • C08K9/06Ingredients treated with organic substances with silicon-containing compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08JWORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
    • C08J2325/00Characterised by the use of homopolymers or copolymers of compounds having one or more unsaturated aliphatic radicals, each having only one carbon-to-carbon double bond, and at least one being terminated by an aromatic carbocyclic ring; Derivatives of such polymers
    • C08J2325/18Homopolymers or copolymers of aromatic monomers containing elements other than carbon and hydrogen
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08KUse of inorganic or non-macromolecular organic substances as compounding ingredients
    • C08K3/00Use of inorganic substances as compounding ingredients
    • C08K3/18Oxygen-containing compounds, e.g. metal carbonyls
    • C08K3/20Oxides; Hydroxides
    • C08K3/22Oxides; Hydroxides of metals
    • C08K2003/2265Oxides; Hydroxides of metals of iron
    • C08K2003/2275Ferroso-ferric oxide (Fe3O4)

Abstract

The invention discloses a preparation method and application of porous magnetic ion exchange resin, relating to the synthesis technology of environment functional materials, and the method comprises the following steps: preparing ferroferric oxide by using a coprecipitation method under an anaerobic condition and using weak base to adjust the pH value; modifying ferroferric oxide by using a silane coupling agent to activate chemical bonds of the ferroferric oxide; taking p-chlorostyrene as a monomer and benzoyl peroxide as an initiator, adding a proper amount of a cross-linking agent and a pore-forming agent, and ultrasonically dispersing modified ferroferric oxide in a solution to obtain an oil phase A; adding a certain amount of composite dispersant and stabilizer into deionized water to serve as a water phase B; and transferring the oil phase A and the water phase B into a reactor to prepare the magnetic ion exchange resin. The ion exchange resin prepared by the method has a core-shell structure coated with magnetic substances, has a plurality of exchangeable ion channels, is easy for magnetic separation, has low cost, and has good application prospect in removing organic matters in industrial wastewater.

Description

Preparation method and application of porous magnetic ion exchange resin
Technical Field
The invention relates to an environment functional material synthesis technology, in particular to a preparation method and application of porous magnetic ion exchange resin.
Background
Currently, adsorption technology is considered to be one of the most efficient and economical methods in industrial wastewater treatment. The method for removing the pollutants from the water environment by utilizing the adsorption reaction between the adsorbent and the pollutants is simple to operate, safe in process and good in pollutant removal effect. The efficiency of the sorbent to remove the contaminants is determined by the structure of the sorbent and the nature of the contaminants.
The activated carbon has large porosity and specific surface area and rich surface chemical groups, can remove pollutants through double actions of chemical adsorption and physical adsorption, and is an important adsorption material in the wastewater treatment process. Conventionally, activated carbon has a certain adsorption effect on most pollutants, but the stability is poor, most of the activated carbon is adsorbed on the surface of small molecular ions or groups, and the activated carbon is easy to fall off and causes secondary pollution easily in the using process. Activated carbon also lacks selective adsorption of contaminants and has difficulties in the application of specific adsorption techniques due to the complex functional groups on the surface of biomass.
Ion exchange resin is a new material with a good application prospect which is developed recently, and is a high molecular adsorbent. The ion on the resin can exchange with the ion in the water in equal quantity, and can effectively remove the organic pollutant in the wastewater. Compared with activated carbon, the resin has the advantages of small general surface area and low effective active functional group, but has the advantages of stable chemical property, strong unit adsorption capacity, high selectivity, easy regeneration and the like. Just because of the difference of the resin structure, the resin can be modified and designed according to the application field to prepare the selective high-efficiency adsorbent.
Disclosure of Invention
The invention aims at the problems and provides a preparation method and application of porous magnetic ion exchange resin.
According to an aspect of the present invention, there is provided a method for preparing a porous magnetic ion exchange resin, comprising the steps of:
step 1, weighing a certain amount of ferrous chloride and ferric chloride, dispersing the ferrous chloride and the ferric chloride in deionized water, heating and stirring the mixture under an oxygen-free condition, dropwise adding weak base into the mixture to adjust the pH value, crystallizing the mixture at a constant temperature, and performing coprecipitation to obtain ferroferric oxide;
step 2, dispersing the prepared magnetic particles in absolute ethyl alcohol, adding a certain amount of silane coupling agent, and heating and stirring for reaction;
step 3, taking p-chlorostyrene as a monomer and benzoyl peroxide as an initiator, adding a proper amount of a cross-linking agent and a pore-forming agent, and ultrasonically dispersing modified ferroferric oxide particles in a solution to obtain an oil phase A;
step 4, adding a certain amount of polyvinyl alcohol/polyvinylpyrrolidone dispersing agent and sodium chloride stabilizing agent into deionized water to obtain a water phase B;
and 5, simultaneously transferring the oil phase A and the water phase B obtained in the step into a reactor, and fully polymerizing the mixed solution under the condition of heating and stirring to obtain the magnetic ion exchange resin.
Further, in the step 1, the mass ratio of the ferrous chloride to the ferric chloride is 1: (0-2); adjusting the pH value to 8-12; the reaction temperature is 40-80 ℃; the reaction time is 1-5 h.
Further, in the step 2, the silane coupling agent is one or a combination of vinyltrimethoxysilane, vinyltrioxysilane and vinylmethyldimethoxysilane; the concentration of the silane coupling agent is 1-5% (w/w); the reaction temperature is 40-80 ℃; the reaction time is 1-5 h.
Further, in the step 3, the crosslinking agent is one of divinylbenzene, triallyl isocyanurate and ethanedioic acid diacrylate or a combination thereof; the pore-forming agent is one or the combination of normal heptane, toluene and xylene; the mass ratio of the monomer, the initiator, the cross-linking agent, the pore-forming agent and the modified ferroferric oxide is 10: (0-0.5): (0-2): (0-5): (0-2).
Furthermore, in the step 4, the mass ratio of the polyvinyl alcohol to the polyvinylpyrrolidone is 1: (0-2); the mass ratio of the deionized water to the dispersant to the stabilizer is 100: (0-2): (0-5).
Furthermore, in the step 5, the mass ratio of the oil phase to the water phase is 1 (5-20); the polymerization reaction temperature is 60-95 ℃; the reaction time is 1-5 h.
Furthermore, in all the steps, the oxygen-free condition is one or more of nitrogen, argon and helium.
According to another aspect of the invention, the porous magnetic ion exchange resin prepared by the preparation method of the porous magnetic ion exchange resin is applied to removal of one or more organic matters in industrial wastewater.
The invention has the advantages that:
according to the preparation method of the porous magnetic ion exchange resin, the inorganic magnetic substance is grafted and coated on the surface of the resin by using a unique silane coupling agent in a suspension polymerization mode to obtain a magnetic function, and agglomeration or depression of the resin in the polymerization process is limited under the assistance of auxiliary agents such as a cross-linking agent, a dispersing agent, a pore-forming agent and the like, so that a cross-linked stable net-shaped structure is formed. The resin has a porous core-shell structure, has strong adsorption capacity and is easy for magnetic separation, and can be applied to treatment of organic pollutants in industrial wastewater.
The method and the process are optimized, the prepared ion exchange resin has a core-shell structure coated with magnetic substances, and the resin has a plurality of exchangeable ion channels, is easy for magnetic separation, has low cost and has good application prospect in removing organic matters in industrial wastewater.
In addition to the objects, features and advantages described above, other objects, features and advantages of the present invention are also provided. The present invention will be described in further detail below with reference to the drawings.
Drawings
The accompanying drawings, which are incorporated in and constitute a part of this application, illustrate embodiments of the invention and, together with the description, serve to explain the invention and not to limit the invention.
FIG. 1 is a scanning electron micrograph of a magnetic ion exchange resin according to example 1 of the present invention;
FIG. 2 is an X-ray diffraction pattern of a magnetic ion exchange resin according to example 1 of the present invention;
FIG. 3 is a hysteresis loop diagram of the magnetic ion exchange resin of example 1 of the present invention.
FIG. 4 is a graph showing the adsorption behavior of the magnetic ion exchange resin of example 1 in the presence of reactive bright red dye.
Detailed Description
In order to make the objects, technical solutions and advantages of the present invention more apparent, the present invention is described in further detail below with reference to the accompanying drawings and embodiments. It should be understood that the specific embodiments described herein are merely illustrative of the invention and are not intended to limit the invention.
A preparation method of porous magnetic ion exchange resin comprises the following steps:
step 1, weighing a certain amount of ferrous chloride and ferric chloride, dispersing the ferrous chloride and the ferric chloride in deionized water, heating and stirring the mixture under an oxygen-free condition, dropwise adding weak base into the mixture to adjust the pH value, crystallizing the mixture at a constant temperature, and performing coprecipitation to obtain ferroferric oxide;
step 2, dispersing the prepared magnetic particles in absolute ethyl alcohol, adding a certain amount of silane coupling agent, and heating and stirring for reaction;
step 3, taking p-chlorostyrene as a monomer and benzoyl peroxide as an initiator, adding a proper amount of a cross-linking agent and a pore-forming agent, and ultrasonically dispersing modified ferroferric oxide particles in a solution to obtain an oil phase A;
step 4, adding a certain amount of polyvinyl alcohol/polyvinylpyrrolidone dispersing agent and sodium chloride stabilizing agent into deionized water to obtain a water phase B;
and 5, simultaneously transferring the oil phase A and the water phase B obtained in the step into a reactor, and fully polymerizing the mixed solution under the condition of heating and stirring to obtain the magnetic ion exchange resin.
In the step 1, the mass ratio of the ferrous chloride to the ferric chloride is 1: (0-2); adjusting the pH value to 8-12; the reaction temperature is 40-80 ℃; the reaction time is 1-5 h.
In the step 2, the silane coupling agent is one or the combination of vinyltrimethoxysilane, vinyltrioxysilane and vinylmethyldimethoxysilane; the concentration of the silane coupling agent is 1-5% (w/w); the reaction temperature is 40-80 ℃; the reaction time is 1-5 h.
In the step 3, the cross-linking agent is one or a combination of divinylbenzene, triallyl isocyanurate and ethanedioic acid diacrylate; the pore-forming agent is one or the combination of normal heptane, toluene and xylene; the mass ratio of the monomer, the initiator, the cross-linking agent, the pore-forming agent and the modified ferroferric oxide is 10: (0-0.5): (0-2): (0-5): (0-2).
In the step 4, the mass ratio of the polyvinyl alcohol to the polyvinylpyrrolidone is 1: (0-2); the mass ratio of the deionized water to the dispersant to the stabilizer is 100: (0-2): (0-5).
In the step 5, the mass ratio of the oil phase to the water phase is 1 (5-20); the polymerization reaction temperature is 60-95 ℃; the reaction time is 1-5 h.
In all the steps, the adopted oxygen-free condition is one or more of nitrogen, argon and helium.
According to another aspect of the invention, the porous magnetic ion exchange resin prepared by the preparation method of the porous magnetic ion exchange resin is applied to removal of one or more organic matters in industrial wastewater.
According to the preparation method of the porous magnetic ion exchange resin, the inorganic magnetic substance is grafted and coated on the surface of the resin by using a unique silane coupling agent in a suspension polymerization mode to obtain a magnetic function, and agglomeration or depression of the resin in the polymerization process is limited under the assistance of auxiliary agents such as a cross-linking agent, a dispersing agent, a pore-forming agent and the like, so that a cross-linked stable net-shaped structure is formed. The resin has a porous core-shell structure, has strong adsorption capacity and is easy for magnetic separation, and can be applied to treatment of organic pollutants in industrial wastewater.
The method and the process are optimized, the prepared ion exchange resin has a core-shell structure coated with magnetic substances, the resin has a porous structure, the specific surface area is large, the particle size distribution is small and uniform, a plurality of exchangeable ion channels are provided, the magnetic separation is easy, the cost is low, and the application prospect for removing organic matters in industrial wastewater is good.
Example 1 (the main variable in this example is the dispersant)
Weighing a certain amount of ferrous chloride and ferric chloride, dispersing in deionized water, and adding into the deionized water2Heating to 60 ℃ under protection, stirring, dropwise adding weak base to adjust the pH to be =10, and crystallizing at constant temperature for 1 h to obtain ferroferric oxide; dispersing magnetic particles in absolute ethyl alcohol, adding 1 wt% of vinyl methyl dimethoxy silane coupling agent, and reacting in N2Stirring and reacting for 2 hours at 40 ℃ under protection to obtain the modified ferroferric oxide.
Taking 10 g of p-chlorostyrene, 0.2 g of benzoyl peroxide, 2.0 g of triallyl isocyanurate and 6.0 g of n-heptane, and then ultrasonically dispersing 2.0 g of modified ferroferric oxide particles in the solution to obtain an oil phase A; 0.8 g of polyvinyl alcohol/0.8 g of polyvinylpyrrolidone and 4.0 g of sodium chloride were added to 100 mL of deionized water, and dissolved by heating to obtain an aqueous phase B.
And simultaneously transferring the oil phase A and the water phase B into a reactor, heating to 80 ℃ under stirring for reaction for 2 h, and then heating to 90 ℃ for reaction for 2 h to obtain the magnetic ion exchange resin.
FIG. 1 is a scanning electron microscope image of the porous magnetic ion exchange resin of the present invention, the resin has no obvious pits, the particle size is 40-50 μm, and the surface has large sizeMeasuring micropores, and exchanging ion channels are more. FIG. 2 is an X-ray diffraction pattern of the magnetic ion exchange resin, and the crystallinity of ferroferric oxide in the obtained resin is good, which is consistent with the result of its standard card (No. 19-0029), and a broad peak package appears at 20 degrees, corresponding to the diffraction peak of the polymer. FIG. 3 is a hysteresis chart of a magnetic ion exchange resin showing ferromagnetism and having a saturation magnetization of 11.6 emu g-1. FIG. 4 shows that magnetic ion exchange resin is used for adsorption in the aqueous solution of reactive bright red dye, and after 24 hours, the adsorption amount reaches 177.6 mg/mg, and about 89% of the reactive bright red dye is removed.
Example 2 (the main variable in this example is the crosslinker)
Weighing a certain amount of ferrous chloride and ferric chloride, dispersing in deionized water, and adding into the deionized water2Heating to 60 ℃ under protection, stirring, dropwise adding weak base to adjust the pH to be =10, and crystallizing at constant temperature for 1 h to obtain ferroferric oxide; dispersing magnetic particles in absolute ethyl alcohol, adding 1 wt% of vinyl methyl dimethoxy silane coupling agent, and reacting in N2Stirring and reacting for 2 hours at 40 ℃ under protection to obtain the modified ferroferric oxide.
Taking 10 g of p-chlorostyrene, 0.2 g of benzoyl peroxide, 2.0 g of divinylbenzene and 6.0 g of n-heptane, and then ultrasonically dispersing 2.0 g of modified ferroferric oxide particles in the solution to obtain an oil phase A; 0.8 g of polyvinyl alcohol/0.8 g of polyvinylpyrrolidone and 4.0 g of sodium chloride were added to 100 mL of deionized water, and dissolved by heating to obtain an aqueous phase B.
And simultaneously transferring the oil phase A and the water phase B into a reactor, heating to 80 ℃ under stirring for reaction for 2 h, and then heating to 90 ℃ for reaction for 2 h to obtain the magnetic ion exchange resin.
Example 3 (the main variable in this example is the pore former)
Weighing a certain amount of ferrous chloride and ferric chloride, dispersing in deionized water, and adding into the deionized water2Heating to 60 ℃ under protection, stirring, dropwise adding weak base to adjust the pH to be =10, and crystallizing at constant temperature for 1 h to obtain ferroferric oxide; dispersing magnetic particles in absolute ethyl alcohol, adding 1 wt% of vinyl methyl dimethoxy silane coupling agent, and reacting in N2Stirring and reacting for 2 h at 40 ℃ under protection to obtain the modified materialNeutral ferroferric oxide.
Taking 10 g of p-chlorostyrene, 0.2 g of benzoyl peroxide, 2.0 g of triallyl isocyanurate and 6.0 g of xylene, and then ultrasonically dispersing 2.0 g of modified ferroferric oxide particles in the solution to obtain an oil phase A; 0.4 g of polyvinyl alcohol/0.4 g of polyvinylpyrrolidone and 4.0 g of sodium chloride were added to 100 mL of deionized water, and dissolved by heating to obtain an aqueous phase B.
And simultaneously transferring the oil phase A and the water phase B into a reactor, heating to 80 ℃ under stirring for reaction for 2 h, and then heating to 90 ℃ for reaction for 2 h to obtain the magnetic ion exchange resin.
Example 4 (the main variable in this example is the silane coupling agent)
Weighing a certain amount of ferrous chloride and ferric chloride, dispersing in deionized water, and adding into the deionized water2Heating to 60 ℃ under protection, stirring, dropwise adding weak base to adjust the pH to be =10, and crystallizing at constant temperature for 1 h to obtain ferroferric oxide; dispersing magnetic particles in absolute ethanol, adding 1 wt% of vinyl trimethoxy silane coupling agent in N2Stirring and reacting for 2 hours at 40 ℃ under protection to obtain the modified ferroferric oxide.
Taking 10 g of p-chlorostyrene, 0.2 g of benzoyl peroxide, 2.0 g of triallyl isocyanurate and 6.0 g of n-heptane, and then ultrasonically dispersing 2.0 g of modified ferroferric oxide particles in the solution to obtain an oil phase A; 0.4 g of polyvinyl alcohol/0.4 g of polyvinylpyrrolidone and 4.0 g of sodium chloride were added to 100 mL of deionized water, and dissolved by heating to obtain an aqueous phase B.
And simultaneously transferring the oil phase A and the water phase B into a reactor, heating to 80 ℃ under stirring for reaction for 2 h, and then heating to 90 ℃ for reaction for 2 h to obtain the magnetic ion exchange resin.
Example 5 (the main variables in this example are coupling time and inert gas)
Weighing a certain amount of ferrous chloride and ferric chloride, dispersing in deionized water, heating to 60 ℃ under the protection of argon gas, stirring, dropwise adding weak base to adjust the pH to be =10, and crystallizing at constant temperature for 1 h to obtain ferroferric oxide; dispersing the magnetic particles in absolute ethyl alcohol, adding 1 wt% of vinyl methyl dimethoxy silane coupling agent, and stirring and reacting for 1 h at 40 ℃ under the protection of argon to obtain the modified ferroferric oxide.
Taking 10 g of p-chlorostyrene, 0.2 g of benzoyl peroxide, 2.0 g of triallyl isocyanurate and 6.0 g of n-heptane, and then ultrasonically dispersing 2.0 g of modified ferroferric oxide particles in the solution to obtain an oil phase A; 0.4 g of polyvinyl alcohol/0.4 g of polyvinylpyrrolidone and 4.0 g of sodium chloride were added to 100 mL of deionized water, and dissolved by heating to obtain an aqueous phase B.
And simultaneously transferring the oil phase A and the water phase B into a reactor, heating to 80 ℃ under stirring for reaction for 2 h, and then heating to 90 ℃ for reaction for 2 h to obtain the magnetic ion exchange resin.
Example 6 (the main variables in this example are the polymerization temperature and time)
Weighing a certain amount of ferrous chloride and ferric chloride, dispersing in deionized water, and adding into the deionized water2Heating to 60 ℃ under protection, stirring, dropwise adding weak base to adjust the pH to be =10, and crystallizing at constant temperature for 1 h to obtain ferroferric oxide; dispersing magnetic particles in absolute ethyl alcohol, adding 1 wt% of vinyl methyl dimethoxy silane coupling agent, and reacting in N2Stirring and reacting for 2 hours at 40 ℃ under protection to obtain the modified ferroferric oxide.
Taking 10 g of p-chlorostyrene, 0.2 g of benzoyl peroxide, 2.0 g of triallyl isocyanurate and 6.0 g of n-heptane, and then ultrasonically dispersing 2.0 g of modified ferroferric oxide particles in the solution to obtain an oil phase A; 0.4 g of polyvinyl alcohol/0.4 g of polyvinylpyrrolidone and 4.0 g of sodium chloride were added to 100 mL of deionized water, and dissolved by heating to obtain an aqueous phase B.
Transferring the oil phase A and the water phase B into a reactor simultaneously, heating to 80 ℃ under stirring for reaction for 2 h, then heating to 90 ℃ for reaction for 2 h, and finally heating to 95 ℃ for reaction for 0.5 h to obtain the magnetic ion exchange resin.
In conclusion, the ion exchange resin obtained by the preparation method of the embodiment of the invention has the magnetic function of a core-shell structure, and the research and optimization of the polymerization process, the magnetic ion exchange resin has a stable cross-linked network structure, large specific surface area, small and uniform particle size distribution and strong adsorption capacity, so that the ion exchange resin can be applied to the treatment of organic pollutants in industrial wastewater.
The above description is only for the purpose of illustrating the preferred embodiments of the present invention and is not to be construed as limiting the invention, and any modifications, equivalents, improvements and the like that fall within the spirit and principle of the present invention are intended to be included therein.

Claims (8)

1. The preparation method of the porous magnetic ion exchange resin is characterized by comprising the following steps
The method comprises the following steps:
step 1, weighing a certain amount of ferrous chloride and ferric chloride, dispersing the ferrous chloride and the ferric chloride in deionized water, heating and stirring the mixture under an oxygen-free condition, dropwise adding weak base into the mixture to adjust the pH value, crystallizing the mixture at a constant temperature, and performing coprecipitation to obtain ferroferric oxide;
step 2, dispersing the prepared magnetic particles in absolute ethyl alcohol, adding a certain amount of silane coupling agent, and heating and stirring for reaction;
step 3, taking p-chlorostyrene as a monomer and benzoyl peroxide as an initiator, adding a proper amount of a cross-linking agent and a pore-forming agent, and ultrasonically dispersing modified ferroferric oxide particles in a solution to obtain an oil phase A;
step 4, adding a certain amount of polyvinyl alcohol/polyvinylpyrrolidone dispersing agent and sodium chloride stabilizing agent into deionized water to obtain a water phase B;
and 5, simultaneously transferring the oil phase A and the water phase B obtained in the step into a reactor, and fully polymerizing the mixed solution under the condition of heating and stirring to obtain the magnetic ion exchange resin.
2. The method for preparing the porous magnetic ion exchange resin according to claim 1, wherein the porous magnetic ion exchange resin is prepared by a method comprising a step of adding a solvent to the porous magnetic ion exchange resin
Characterized in that in the step 1, the mass ratio of ferrous chloride to ferric chloride is 1: (0-2); adjusting the pH value to 8-12; the reaction temperature is 40-80 ℃; the reaction time is 1-5 h.
3. The method for preparing the porous magnetic ion exchange resin according to claim 1, wherein the porous magnetic ion exchange resin is prepared by a method comprising a step of adding a solvent to the porous magnetic ion exchange resin
Characterized in that in the step 2, the silane coupling agent is one or the combination of vinyltrimethoxysilane, vinyltrioxysilane and vinylmethyldimethoxysilane; the concentration of the silane coupling agent is 1-5% (w/w); the reaction temperature is 40-80 ℃; the reaction time is 1-5 h.
4. The method for preparing the porous magnetic ion exchange resin according to claim 1, wherein the porous magnetic ion exchange resin is prepared by a method comprising a step of adding a solvent to the porous magnetic ion exchange resin
Characterized in that in the step 3, the crosslinking agent is one or the combination of divinyl benzene, triallyl isocyanurate and ethanedioic acid diacrylate; the pore-forming agent is one or the combination of normal heptane, toluene and xylene; the mass ratio of the monomer, the initiator, the cross-linking agent, the pore-forming agent and the modified ferroferric oxide is 10: (0-0.5): (0-2): (0-5): (0-2).
5. The method for preparing the porous magnetic ion exchange resin according to claim 1, wherein the porous magnetic ion exchange resin is prepared by a method comprising a step of adding a solvent to the porous magnetic ion exchange resin
Characterized in that in the step 4, the mass ratio of the polyvinyl alcohol to the polyvinylpyrrolidone is 1: (0-2); the mass ratio of the deionized water to the dispersant to the stabilizer is 100: (0-2): (0-5).
6. The method for preparing the porous magnetic ion exchange resin according to claim 1, wherein the porous magnetic ion exchange resin is prepared by a method comprising a step of adding a solvent to the porous magnetic ion exchange resin
Characterized in that in the step 5, the mass ratio of the oil phase to the water phase is 1 (5-20); the polymerization reaction temperature is 60-95 ℃; the reaction time is 1-5 h.
7. The method for preparing the porous magnetic ion exchange resin according to claim 1, wherein the porous magnetic ion exchange resin is prepared by a method comprising a step of adding a solvent to the porous magnetic ion exchange resin
Characterized in that in all the steps, the adopted oxygen-free condition is one or more of nitrogen, argon and helium.
8. A process for preparing the porous magnetic ion exchange resin as claimed in any one of claims 1 to 7
The porous magnetic ion exchange resin prepared by the method is applied to removing one or more organic matters in industrial wastewater.
CN202010334071.0A 2020-04-24 2020-04-24 Preparation method and application of porous magnetic ion exchange resin Pending CN111592678A (en)

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CN112403450A (en) * 2020-09-08 2021-02-26 苏州市相城环保技术有限公司 Preparation method of magnetic farmland heavy metal adsorbent
CN113231034A (en) * 2021-04-21 2021-08-10 华南师范大学 DGT binding phase and preparation method and application thereof

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Publication number Priority date Publication date Assignee Title
CN112403450A (en) * 2020-09-08 2021-02-26 苏州市相城环保技术有限公司 Preparation method of magnetic farmland heavy metal adsorbent
CN113231034A (en) * 2021-04-21 2021-08-10 华南师范大学 DGT binding phase and preparation method and application thereof

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