CN112791750A - Preparation method of ion exchange resin for sewage treatment - Google Patents

Preparation method of ion exchange resin for sewage treatment Download PDF

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Publication number
CN112791750A
CN112791750A CN202011574896.6A CN202011574896A CN112791750A CN 112791750 A CN112791750 A CN 112791750A CN 202011574896 A CN202011574896 A CN 202011574896A CN 112791750 A CN112791750 A CN 112791750A
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ion exchange
parts
exchange resin
gelatin
reaction
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钱平
蔡小华
刘金彪
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Jiangsu Suqing Water Treatment Engineering Group Co ltd
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Jiangsu Suqing Water Treatment Engineering Group Co ltd
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J39/00Cation exchange; Use of material as cation exchangers; Treatment of material for improving the cation exchange properties
    • B01J39/08Use of material as cation exchangers; Treatment of material for improving the cation exchange properties
    • B01J39/16Organic material
    • B01J39/17Organic material containing also inorganic materials, e.g. inert material coated with an ion-exchange resin
    • 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
    • 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
    • C02F2001/425Treatment of water, waste water, or sewage by ion-exchange using cation exchangers
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Inorganic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Addition Polymer Or Copolymer, Post-Treatments, Or Chemical Modifications (AREA)

Abstract

The invention discloses a preparation method of ion exchange resin for sewage treatment, which relates to the field of resin, and comprises the following steps: s1, preparing 20 parts of acetylated styrene, 2 parts of azodiisobutyronitrile, 8 parts of divinylxylene, 220 parts of ferroferric oxide, 80 parts of gamma ferric oxide, 5 parts of gelatin and 0.5 part of dimethyl diallyl ammonium chloride; s2, mixing the acetylated styrene with azodiisobutyronitrile and divinyl xylene, controlling the reaction temperature at 60-100 ℃ and the reaction time at 1 hour to obtain the acetylated styrene polymer solution. The ion exchange resin for sewage treatment of the invention has better economic effect on sewage through sulfation reaction, compared with the common similar products sold in the market, the ion exchange resin has similar mass/volume exchange capacity, but lower price, excellent economic effect and better preservation degree of the regenerated mass/volume exchange capacity.

Description

Preparation method of ion exchange resin for sewage treatment
Technical Field
The invention relates to the field of resin, in particular to a preparation method of ion exchange resin for sewage treatment.
Background
Ion exchange resins can be further classified into styrene resins and acrylic resins according to the types of the matrixes, the types of chemically active groups in the resins determine the main properties and types of the resins, and in practical use, the resins are often converted into other ion types for operation so as to meet various requirements.
The quality/volume exchange capacity performance of various resins sold in the market is obviously reduced after regeneration, so that the sewage treatment cost is increased, and the purchase cost of various resins sold in the market is extremely high due to high price.
Disclosure of Invention
The invention aims to: in order to solve the problems of high cost and large performance damage after regeneration of the existing sewage treatment, a preparation method of the ion exchange resin for sewage treatment is provided.
In order to achieve the purpose, the invention provides the following technical scheme: a preparation method of an ion exchange resin for sewage treatment comprises the following steps:
s1, preparing 20 parts of acetylated styrene, 2 parts of azodiisobutyronitrile, 8 parts of divinylxylene, 220 parts of ferroferric oxide, 80 parts of gamma ferric oxide, 5 parts of gelatin and 0.5 part of dimethyl diallyl ammonium chloride;
s2, mixing the acetylated styrene with azodiisobutyronitrile and divinyl xylene, controlling the reaction temperature to be 60-100 ℃, and controlling the reaction time to be 1 hour to obtain an acetylated styrene polymer solution;
s3, adding ferroferric oxide, gamma ferric oxide, gelatin and dimethyl diallyl ammonium chloride into the acetylated styrene polymer solution to enable the ratio of ferroferric oxide, gamma ferric oxide, gelatin and dimethyl diallyl ammonium chloride to reach 30-90% of the acetylated styrene polymer solution, carrying out polymerization reaction, controlling the reaction time to be 12 hours, and heating in a step heating mode;
s4, washing the polymerization reaction product, and polymerizing the polymerization reaction product with azodiisobutyronitrile, gelatin and isopropanol again, wherein the reaction time is controlled to be 1 hour;
s5, and mixing the reacted product according to a ratio of 1: adding ferroferric oxide and gamma ferric oxide according to the proportion of 0.5, carrying out polymerization reaction, controlling the reaction temperature at 75 ℃ and the reaction time at 12 hours, and washing after the reaction is finished;
s6, introducing sulfonic acid groups into the washed product to carry out sulfation reaction, thereby obtaining the ion exchange resin.
Preferably, the acetylated styrene is of formula (1).
Figure BDA0002863274640000021
Preferably, the gelatin may be replaced by corn starch mixed with water or the like.
Preferably, the refluxing solvent is a mixed solvent of isopropanol and acetonitrile.
Preferably, the aqueous solution of gelatin has a mass percent concentration of 2%.
Preferably, the particle size of the ferroferric oxide and the gamma ferric oxide is controlled within 20 nanometers and the plus-minus error is within 10 nanometers.
Compared with the prior art, the invention has the beneficial effects that:
the ion exchange resin for sewage treatment of the invention has better economic effect on sewage through sulfation reaction, compared with the common similar products sold in the market, the ion exchange resin has similar mass/volume exchange capacity, but lower price, excellent economic effect and better preservation degree of the regenerated mass/volume exchange capacity.
Detailed Description
The technical solutions in the embodiments of the present invention will be clearly and completely described below, and it is obvious that the described embodiments are only a part of the embodiments of the present invention, and not all embodiments. All other embodiments, which can be derived by a person skilled in the art from the embodiments given herein without making any creative effort, shall fall within the protection scope of the present invention.
Example 1
S1, preparing 20 parts of acetylated styrene, 2 parts of azodiisobutyronitrile, 8 parts of divinylxylene, 220 parts of ferroferric oxide, 80 parts of gamma ferric oxide, 5 parts of gelatin and 0.5 part of dimethyl diallyl ammonium chloride;
s2, mixing the acetylated styrene with azodiisobutyronitrile and divinyl xylene, controlling the reaction temperature at 60 ℃ and the reaction time at 1 hour to obtain an acetylated styrene polymer solution;
s3, adding ferroferric oxide, gamma ferric oxide, gelatin and dimethyl diallyl ammonium chloride into the acetylated styrene polymer solution to enable the ratio of ferroferric oxide, gamma ferric oxide, gelatin and dimethyl diallyl ammonium chloride to reach 30% of the acetylated styrene polymer solution, carrying out polymerization reaction, controlling the reaction time to be 12 hours, and heating in a step heating mode;
s4, washing the polymerization reaction product, and polymerizing the polymerization reaction product with azodiisobutyronitrile, gelatin and isopropanol again, wherein the reaction time is controlled to be 1 hour;
s5, and mixing the reacted product according to a ratio of 1: adding ferroferric oxide and gamma ferric oxide according to the proportion of 0.5, carrying out polymerization reaction, controlling the reaction temperature at 75 ℃ and the reaction time at 12 hours, and washing after the reaction is finished;
s6, introducing sulfonic acid groups into the washed product to carry out sulfation reaction, thereby obtaining the ion exchange resin.
Example 2
S1, preparing 20 parts of acetylated styrene, 2 parts of azodiisobutyronitrile, 8 parts of divinylxylene, 220 parts of ferroferric oxide, 80 parts of gamma ferric oxide, 5 parts of gelatin and 0.5 part of dimethyl diallyl ammonium chloride;
s2, mixing the acetylated styrene with azodiisobutyronitrile and divinyl xylene, controlling the reaction temperature at 100 ℃ and the reaction time at 1 hour to obtain an acetylated styrene polymer solution;
s3, adding ferroferric oxide, gamma ferric oxide, gelatin and dimethyl diallyl ammonium chloride into the acetylated styrene polymer solution to enable the ratio of ferroferric oxide, gamma ferric oxide, gelatin and dimethyl diallyl ammonium chloride to reach 30% of the acetylated styrene polymer solution, carrying out polymerization reaction, controlling the reaction time to be 12 hours, and heating in a step heating mode;
s4, washing the polymerization reaction product, and polymerizing the polymerization reaction product with azodiisobutyronitrile, gelatin and isopropanol again, wherein the reaction time is controlled to be 1 hour;
s5, and mixing the reacted product according to a ratio of 1: adding ferroferric oxide and gamma ferric oxide according to the proportion of 0.5, carrying out polymerization reaction, controlling the reaction temperature at 75 ℃ and the reaction time at 12 hours, and washing after the reaction is finished;
s6, introducing sulfonic acid groups into the washed product to carry out sulfation reaction, thereby obtaining the ion exchange resin.
Example 3
S1, preparing 20 parts of acetylated styrene, 2 parts of azodiisobutyronitrile, 8 parts of divinylxylene, 220 parts of ferroferric oxide, 80 parts of gamma ferric oxide, 5 parts of gelatin and 0.5 part of dimethyl diallyl ammonium chloride;
s2, mixing the acetylated styrene with azodiisobutyronitrile and divinyl xylene, controlling the reaction temperature at 60 ℃ and the reaction time at 1 hour to obtain an acetylated styrene polymer solution;
s3, adding ferroferric oxide, gamma ferric oxide, gelatin and dimethyl diallyl ammonium chloride into the acetylated styrene polymer solution to enable the ratio of ferroferric oxide, gamma ferric oxide, gelatin and dimethyl diallyl ammonium chloride to reach 90% of the acetylated styrene polymer solution, carrying out polymerization reaction, controlling the reaction time to be 12 hours, and heating in a step heating mode;
s4, washing the polymerization reaction product, and polymerizing the polymerization reaction product with azodiisobutyronitrile, gelatin and isopropanol again, wherein the reaction time is controlled to be 1 hour;
s5, and mixing the reacted product according to a ratio of 1: adding ferroferric oxide and gamma ferric oxide according to the proportion of 0.5, carrying out polymerization reaction, controlling the reaction temperature at 75 ℃ and the reaction time at 12 hours, and washing after the reaction is finished;
s6, introducing sulfonic acid groups into the washed product to carry out sulfation reaction, thereby obtaining the ion exchange resin.
Example 4
S1, preparing 20 parts of acetylated styrene, 2 parts of azodiisobutyronitrile, 8 parts of divinylxylene, 220 parts of ferroferric oxide, 80 parts of gamma ferric oxide, 5 parts of gelatin and 0.5 part of dimethyl diallyl ammonium chloride;
s2, mixing the acetylated styrene with azodiisobutyronitrile and divinyl xylene, controlling the reaction temperature at 100 ℃ and the reaction time at 1 hour to obtain an acetylated styrene polymer solution;
s3, adding ferroferric oxide, gamma ferric oxide, gelatin and dimethyl diallyl ammonium chloride into the acetylated styrene polymer solution to enable the ratio of ferroferric oxide, gamma ferric oxide, gelatin and dimethyl diallyl ammonium chloride to reach 90% of the acetylated styrene polymer solution, carrying out polymerization reaction, controlling the reaction time to be 12 hours, and heating in a step heating mode;
s4, washing the polymerization reaction product, and polymerizing the polymerization reaction product with azodiisobutyronitrile, gelatin and isopropanol again, wherein the reaction time is controlled to be 1 hour;
s5, and mixing the reacted product according to a ratio of 1: adding ferroferric oxide and gamma ferric oxide according to the proportion of 0.5, carrying out polymerization reaction, controlling the reaction temperature at 75 ℃ and the reaction time at 12 hours, and washing after the reaction is finished;
s6, introducing sulfonic acid groups into the washed product to carry out sulfation reaction, thereby obtaining the ion exchange resin.
Example 5
S1, preparing 20 parts of acetylated styrene, 2 parts of azodiisobutyronitrile, 8 parts of divinylxylene, 220 parts of ferroferric oxide, 80 parts of gamma ferric oxide, 5 parts of gelatin and 0.5 part of dimethyl diallyl ammonium chloride;
s2, mixing the acetylated styrene with azodiisobutyronitrile and divinyl xylene, controlling the reaction temperature at 80 ℃ and the reaction time at 1 hour to obtain an acetylated styrene polymer solution;
s3, adding ferroferric oxide, gamma ferric oxide, gelatin and dimethyl diallyl ammonium chloride into the acetylated styrene polymer solution to enable the ratio of ferroferric oxide, gamma ferric oxide, gelatin and dimethyl diallyl ammonium chloride to reach 60% of the acetylated styrene polymer solution, carrying out polymerization reaction, controlling the reaction time to be 12 hours, and heating in a step heating mode;
s4, washing the polymerization reaction product, and polymerizing the polymerization reaction product with azodiisobutyronitrile, gelatin and isopropanol again, wherein the reaction time is controlled to be 1 hour;
s5, and mixing the reacted product according to a ratio of 1: adding ferroferric oxide and gamma ferric oxide according to the proportion of 0.5, carrying out polymerization reaction, controlling the reaction temperature at 75 ℃ and the reaction time at 12 hours, and washing after the reaction is finished;
s6, introducing sulfonic acid groups into the washed product to carry out sulfation reaction, thereby obtaining the ion exchange resin.
Example 6
Weak acid heavy metal wastewater discharged from a certain electroplating enterprise is extracted, fully mixed and averagely divided into 7 parts, the resins prepared in the embodiments 1, 2, 3, 4 and 5 of the invention are respectively used for treating sewage, and the mass/volume exchange capacity of the resins is measured by comparing with commercially available resins, namely, domestic 1 and domestic 2, and the results are shown in table 1.
Table 1: results of comparison of the resins obtained in examples 1, 2, 3, 4 and 5 with commercially available resins (Table values in mmol/ml)
Figure BDA0002863274640000061
Figure BDA0002863274640000071
As can be seen from Table 1, the mass/volume exchange capacity performance of the resins prepared in examples 3, 4 and 5 of the present invention for the weak acid heavy metal wastewater is similar to that of the commercially available resins, namely, domestic 1 and domestic 2, and both the mass/volume exchange capacity performance of the resins prepared in examples 3 and 4 of the present invention is above 4.2, the mass/volume exchange capacity performance of the resins prepared in examples 3 and 4 of the present invention for the weak acid heavy metal wastewater after primary regeneration is still above 4.0, the mass/volume exchange capacity performance of the resins prepared in example 3 and 4 of the resins prepared in example 3 after secondary regeneration is still 4.0, and the mass/volume exchange capacity performance of the resins prepared in domestic 2 for the weak acid heavy metal wastewater in the primary use is the highest, but the mass/volume exchange capacity performance of the resins prepared in example 3 after primary regeneration for the weak acid heavy metal wastewater is the same as that in example 3, and the mass/volume exchange capacity performance of the resins prepared in example 3 of the resins prepared in Can be similar to the commercial resin, but has good reproducibility, long service life, better economic effect and cost saving.
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 attributes 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.

Claims (5)

1. A preparation method of ion exchange resin for sewage treatment is characterized in that: the preparation method of the ion exchange resin for sewage treatment comprises the following steps:
s1, preparing 20 parts of acetylated styrene, 2 parts of azodiisobutyronitrile, 8 parts of divinylxylene, 220 parts of ferroferric oxide, 80 parts of gamma ferric oxide, 5 parts of gelatin and 0.5 part of dimethyl diallyl ammonium chloride;
s2, mixing the acetylated styrene with azodiisobutyronitrile and divinyl xylene, controlling the reaction temperature to be 60-100 ℃, and controlling the reaction time to be 1 hour to obtain an acetylated styrene polymer solution;
s3, adding ferroferric oxide, gamma ferric oxide, gelatin and dimethyl diallyl ammonium chloride into the acetylated styrene polymer solution to enable the ratio of ferroferric oxide, gamma ferric oxide, gelatin and dimethyl diallyl ammonium chloride to reach 30-90% of the acetylated styrene polymer solution, carrying out polymerization reaction, controlling the reaction time to be 12 hours, and heating in a step heating mode;
s4, washing the polymerization reaction product, and polymerizing the polymerization reaction product with azodiisobutyronitrile, gelatin and isopropanol again, wherein the reaction time is controlled to be 1 hour;
s5, and mixing the reacted product according to a ratio of 1: adding ferroferric oxide and gamma ferric oxide according to the proportion of 0.5, carrying out polymerization reaction, controlling the reaction temperature at 75 ℃ and the reaction time at 12 hours, and washing after the reaction is finished;
s6, introducing sulfonic acid groups into the washed product to carry out sulfation reaction, thereby obtaining the ion exchange resin.
2. The method for preparing the ion exchange resin for sewage treatment according to claim 1, wherein the ion exchange resin comprises: the chemical formula of the acetylated styrene is shown as a formula (1).
Figure FDA0002863274630000011
Figure FDA0002863274630000021
3. The method for preparing the ion exchange resin for sewage treatment according to claim 1, wherein the ion exchange resin comprises: the gelatin can be replaced by corn starch mixed with water or other similar products.
4. The method for preparing the ion exchange resin for sewage treatment according to claim 1, wherein the ion exchange resin comprises: the mass percentage concentration of the aqueous solution of the gelatin is 2%.
5. The method for preparing the ion exchange resin for sewage treatment according to claim 1, wherein the ion exchange resin comprises: the particle size of the ferroferric oxide and the gamma ferric oxide is controlled within 20 nanometers, and the plus-minus error is within 10 nanometers.
CN202011574896.6A 2020-12-28 2020-12-28 Preparation method of ion exchange resin for sewage treatment Pending CN112791750A (en)

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Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1053622A (en) * 1991-01-29 1991-08-07 华南理工大学 Preparation of magnetic macroporous ion-exchange resin for adsorption
KR20040026904A (en) * 2002-09-26 2004-04-01 한국과학기술연구원 Magnetic cation exchange resin and preparation method thereof
CN101440166A (en) * 2007-11-22 2009-05-27 中国石油化工股份有限公司 Composite magnetic cationic ion-exchange resin, and preparation and use thereof
CN107486254A (en) * 2017-08-24 2017-12-19 江苏亚峰科技集团有限公司 A kind of sewage disposal spent ion exchange resin
CN107973872A (en) * 2017-12-11 2018-05-01 西南科技大学 Nano ferriferrous oxide adulterates the preparation method of styrene diethylene benzene copoly mer hydrophobic catalyst carrier
CN108219087A (en) * 2018-01-12 2018-06-29 南京大学 A kind of acidproof high mechanical properties weak acid cation exchange microballoon resin of magnetic acrylic acid series and preparation method thereof

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1053622A (en) * 1991-01-29 1991-08-07 华南理工大学 Preparation of magnetic macroporous ion-exchange resin for adsorption
KR20040026904A (en) * 2002-09-26 2004-04-01 한국과학기술연구원 Magnetic cation exchange resin and preparation method thereof
CN101440166A (en) * 2007-11-22 2009-05-27 中国石油化工股份有限公司 Composite magnetic cationic ion-exchange resin, and preparation and use thereof
CN107486254A (en) * 2017-08-24 2017-12-19 江苏亚峰科技集团有限公司 A kind of sewage disposal spent ion exchange resin
CN107973872A (en) * 2017-12-11 2018-05-01 西南科技大学 Nano ferriferrous oxide adulterates the preparation method of styrene diethylene benzene copoly mer hydrophobic catalyst carrier
CN108219087A (en) * 2018-01-12 2018-06-29 南京大学 A kind of acidproof high mechanical properties weak acid cation exchange microballoon resin of magnetic acrylic acid series and preparation method thereof

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