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CN105295059B - A kind of method of the chloromethylated polystyrene polymer and adsorption recovery Phenols In Industrial Liquid Waste class of immobilized cationization beta-cyclodextrin - Google Patents

A kind of method of the chloromethylated polystyrene polymer and adsorption recovery Phenols In Industrial Liquid Waste class of immobilized cationization beta-cyclodextrin Download PDF

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CN105295059B
CN105295059B CN201510853037.3A CN201510853037A CN105295059B CN 105295059 B CN105295059 B CN 105295059B CN 201510853037 A CN201510853037 A CN 201510853037A CN 105295059 B CN105295059 B CN 105295059B
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cyclodextrin
immobilized
beta
cationization
chloromethylated polystyrene
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CN105295059A (en
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纪红兵
黄小楠
杨祖金
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Huizhou new material industrial park investment and Construction Co.,Ltd.
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Huizhou Research Institute of Sun Yat Sen University
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Abstract

The invention discloses a kind of methods of the chloromethylated polystyrene polymer and adsorption recovery Phenols In Industrial Liquid Waste class of immobilized cationization beta-cyclodextrin.This method is adsorbent using the polymer that the immobilized cationized cyclodextrins of chloromethylated polystyrene are formed, phenolic substances in industrial wastewater is selectively adsorbed in polymer, and the regeneration and reuse of adsorbent material then can be realized by the processing of simply desorption.There is the Phenol Industrial Wastewater of phenolic hydroxyl group to adsorb to containing cresols, phenol, chlorophenol and salicylic acid etc. using the adsorbent, maximal absorptive capacity can achieve 96,140,250,170mg/g respectively, and just reach balance in 2 hours.The result shows that its adsorbance is apparently higher than the maximal absorptive capacity that adsorbent material has been commercialized to phenols in polyamide, DM301 and S-8 etc..Preparation process of the invention is simple and reusable, low in cost, easy to operate, adsorption efficiency is high, energy conservation and environmental protection and the advantages that can recycle phenols.

Description

It is a kind of it is immobilized cationization beta-cyclodextrin chloromethylated polystyrene polymer and suction The method of attached recycling Phenols In Industrial Liquid Waste class
Technical field
The invention belongs to waste water post-processing technology fields, specifically, being related to the immobilized cationization beta-cyclodextrin of one kind The method of chloromethylated polystyrene polymer and adsorption recovery Phenols In Industrial Liquid Waste class.
Background technique
Currently, China's environmental pollution is extremely serious, organic pollution is still a more scabrous problem, traditional environmentally friendly work Skill and environment-friendly materials cannot efficiently solve increasingly increased various complicated pollution problems, therefore develop new environment-friendly materials, Water-purifying material cheap, without secondary pollution is developed, cost of water treatment is reduced, purification efficiency is improved and has become environmental protection neck Domain urgent problem to be solved.And the waste water of phenolic substances is to the very harmful of human body and other biological in organic pollution, if long Phase, which drinks the water containing phenol, can cause dizzy, anaemia and neurological conditions;Phenols wastewater, which enters rivers,lakes and seas, will affect aquatic life The growth and breeding of object;If carrying out the underproduction irrigated will also result in crops with the excessive water quality containing phenol and withering.Meanwhile phenol It is also generally acknowledged carcinogen, it has been included in the pollutant blacklist of 129 kinds of priority acccess controls by American National Environmental Protection Agency at present.I State's phenol wastewater is mainly derived from coke-oven plant, petrochemical plant, resin processing plant, chemical plant, plastic molding and processing plant etc., is wherein with phenol in chemical plant The phenolic substancess such as a large amount of phenol and salicylic acid can be unavoidably generated during raw material production salicylic acid, and if these substances can return Receive the unification for re-using the social benefit, economic benefit and environmental benefit that will realize factory and enterprise.
Based on the above reasons, to the recycling of this kind of phenolic compound at the hot spot of current research.Chinese patent (publication number 101417834 A 2009 of CN) it discloses and a kind of keeps phenols wastewater serial by KL-13X first with heterogeneous catalytic oxidation technology Oxidizing tower catalysis oxidation occurs on a catalyst, so that phenols wastewater be made to degrade, method processing quickly, no solid waste, but this method Phenols can not be recycled to reach the economic unification with environmental protection, and cannot be reused, it is possible to create exhaust emission.Chinese patent (publication No. CN 103304005A 2013) reports a kind of phenol using in hollow-fibre membrane removing phenol wastewater, with phosphoric acid Extractant and strippant are mixed and made into treatment fluid using kerosene or benzene as diluent as extraction agent carrier by tributyl, will be located The tube side of liquid injection film device is managed, waste water injects shell side, reaches separating effect, although processing capacity is big, device is expensive, And there are secondary pollution, treatment process trouble to environment using substances such as benzene.Recently, Chinese patent (publication No. CN 104724783A 2015) disclose it is a kind of phenols wastewater is extracted using dephenolize extractant methyl n-butyl ketone, obtain Extraction phase and raffinate phase, this method can be effectively removed high concentration phenols wastewater, but this method needs specific extractant, cost compared with It is high and the disadvantages of cannot reuse.
Although absorption method using wide, is targetedly adsorbed specific organic pollutant in field of waste water treatment The research of material is rarely reported, using the collaboration of weak interaction and interaction force between Subjective and Objective to improve to object The research of absorption is concerned in recent years, and this kind of material there is apparent adsorption effect therefore to open specific organic substance Issue specifically for phenolic compound in water adsorption recovery method and adsorbent material prepare it is very necessary.
Summary of the invention
The purpose of the present invention is to overcome the deficiency in the prior art, provides a kind of chloromethyl of immobilized cationization beta-cyclodextrin Change the method for poly styrene polymer and adsorption recovery Phenols In Industrial Liquid Waste class.
To achieve the goals above, the present invention adopts the following technical scheme:
The present invention is immobilized to have hydrophobic sky on the basis of chloromethylated polystyrene polymer backbone contains benzene radicals The cationized cyclodextrins of chamber, water-wetted surface and quaternary ammonium group, in conjunction with phenolic substances phenolic hydroxyl group is hydrophilic and phenyl ring hydrophobic property, close At poly- to high molecular polymer, that is, immobilized cationization beta-cyclodextrin chloromethylation of the selective absorption of phenolic compound Styrene polymer.
A kind of chloromethylated polystyrene polymer of immobilized cationization beta-cyclodextrin, is prepared by following steps:
(1) in mass ratio by the etherifying agent of cyclodextrin and 2,3- epoxypropyltrimethylchloride chloride or other active groups For 1:1~10:1 mixing, 10mL water is added, and make its pH=13 with sodium hydrate regulator solution, finally at 40~90 DEG C React 1~4.5h, the cyclodextrin being cationized;
(2) by styrene or other contain the olefines and p-chloromethyl styrene 1:1~4:1 ratio in mass ratio of phenyl ring Mixed monomer dissolves the dispersant into water as polymerized monomer, at room temperature, crosslinking agent, polymerized monomer, initiation is added Agent is reacted at 40~80 DEG C;After completion of the reaction i.e. obtain polymer, through hot water washing for several times after, by obtained product into Row drying, obtains high molecular polymer;The weight fraction ratio of each substance are as follows: 10~40 parts of polymerized monomer, crosslinking agent: 1~3 part, Dispersing agent: 0.1~2 part, initiator: 0.1~4 part, water: 100~400 parts;
(3) cationized cyclodextrins and water obtained step (1) are mixed in 1:10~1:70 ratio, make the ring that is cationized Dextrin dissolution, and pyridine is added, 1h is stirred at room temperature, then at a temperature of 40~90 DEG C, chloromethyl made from step (2) is added Change polystyrene reactant for 24 hours;The chloromethylated polystyrene and cationized cyclodextrins ratio of addition are 1:1~3:1;It has reacted Required polymer is obtained after finishing, after hot water washing for several times, obtained product is dried, immobilized cationization β-is obtained The chloromethylated polystyrene polymer of cyclodextrin.
In the chloromethylated polystyrene polymer of above-mentioned immobilized cationization beta-cyclodextrin, the cyclodextrin is α- Cyclodextrin, beta-cyclodextrin, gamma-cyclodextrin or hydroxypropyl-β-cyclodextrin.
In the chloromethylated polystyrene polymer of above-mentioned immobilized cationization beta-cyclodextrin, the active group Etherifying agent is 2,3- epoxypropyltrimethylchloride chloride, 3- chloro-2-hydroxypropyl-trimethyl ammonium chloride, N- (2,3- glycidyl) three Methylamine salt or diethylamide ethyl chloride.
In the chloromethylated polystyrene polymer of above-mentioned immobilized cationization beta-cyclodextrin, the alkene containing phenyl ring Hydro carbons is styrene, methyl styrene, p-methylstyrene, chlorostyrene, bromstyrol, fluorobenzene ethene or to chloromethylbenzene second Alkene.
In the chloromethylated polystyrene polymer of above-mentioned immobilized cationization beta-cyclodextrin, the dispersing agent is poly- Vinyl alcohol, polyethylene glycol, hydroxyethyl cellulose, hydroxypropyl cellulose or methylcellulose.
In the chloromethylated polystyrene polymer of above-mentioned immobilized cationization beta-cyclodextrin, the initiator was Aoxidize the mixture of one or both of dibenzoyl, cumyl peroxide and azodiisobutyronitrile.
In the chloromethylated polystyrene polymer of above-mentioned immobilized cationization beta-cyclodextrin, the crosslinking agent is two Vinyl benzene, diisocyanate, acrylic acid, methacrylic acid, hydroxypropyl acrylate or hydroxy propyl methacrylate.
Industrial wastewater is recycled using the chloromethylated polystyrene Polymer adsorption of above-mentioned immobilized cationization beta-cyclodextrin The method of middle phenols, includes the following steps:
(1) chloromethylated polystyrene polymer is added in the industrial wastewater containing phenolic compound, is shaken at room temperature It swings or stirs, be separated by filtration, Phenol for Waste Water class compound is attracted in chloromethylated polystyrene polymer;
(2) the chloromethylated polystyrene polymer of absorbing phenolic compound is added in desorbing agent, is shaken at room temperature It swings or stirs, filter, phenolic compound is desorbed, recycling obtains phenolic compound and chloromethylated polystyrene polymer;
(3) the chloromethylated polystyrene polymer of recycling is placed in 60~70 DEG C of drying in oven, dry 5~6h, storage It deposits in case next time uses.
The mass volume ratio of the adsorbent material chloromethylated polystyrene polymer and industrial wastewater is 1:10~10:1 (g/L)。
The desorbing agent is the mixture of ethyl alcohol or ethyl alcohol and sodium hydroxide.
In above-mentioned adsorption recovery phenolic compound, phenolic compound and eluant, eluent in obtained eluent can lead to Peracid, recrystallization recycling.Phenols In Industrial Liquid Waste substance content after adsorption recovery is extremely low, classification recovering effect compared with It is good.Adsorbent material can be recycled and be reused, this has rush using expanding to the commercialization of this adsorbent and in the industry Into effect.
Compared with prior art, the method have the advantages that:
1. chloromethylated polystyrene polymer synthesized by the present invention, synthesis step is simple, environmentally protective, without secondary dirt Dye;And this adsorbent material, acid, alkali, organic solvent are not dissolved in, there is good mechanical strength, can be repeated several times use, is produced It is at low cost, it is saved under normal temperature and pressure.
2. adsorption separating method of the present invention directly puts into adsorbent chloromethylated polystyrene polymer containing phenols In the industrial wastewater of compound, highly selective adsorption separation process can be completed at normal temperature.
3. the present invention is desorbed using alkali and alcohol mixture matter, the regeneration technology of adsorbent is simple, and cost recovery is low.
4. the obtained adsorbent material of the present invention carries out static and dynamic to phenolic compound aqueous solution at normal temperature and inhales It is attached, there is good selective absorption effect, and after desorptive activation, reuse, adsorbance is held essentially constant.
Specific embodiment
The present invention will be further explained with reference to the examples below, but scope of protection of the present invention is not limited thereto.
Formulas I~III is the synthetic method of immobilization cyclo-dextrin-modified resin
Embodiment 1:
The preparation (1) of adsorbent material:
1g beta-cyclodextrin is dissolved in 10mL pure water, stirring 10min makes it dissolve, and 7g2,3- epoxy is added Ammonium chloride (ETMAC), and with sodium hydrate regulator solution pH make its 13,4.5h is stirred at 70 DEG C, filter, evaporation obtain it is brown Color dope i.e. cationization beta-cyclodextrin;0.12g polyvinyl alcohol is dissolved in the pure water of 50mL, 2.6g sodium chloride is added, 10g styrene, 1g divinylbenzene, 3.6g p-chloromethyl styrene and 0.16g mistake are slowly added into the solution at room temperature The mixed solution of Benzoyl Oxide reacts 30min, then heats at 60 DEG C, reacts 2h, is continuously heating to 80 DEG C, reaction 10h, obtained product is cooling, filtering, dry in 70 DEG C of air dry oven after being washed for several times with 60~80 DEG C of warm water 6h obtains light yellow final products Chloromethyl polystyrene;1g cationization beta-cyclodextrin is dissolved in 70mL water, 10mL pyrrole is added 1h is stirred in pyridine at room temperature, and 2g chloromethylated polystyrene is then added, and the product cooling obtained for 24 hours, mistake are reacted at 73 DEG C Filter, after being washed for several times with 60~80 DEG C of warm water, dry 6h, obtains yellow and surface is smooth in 70 DEG C of air dry oven Final products, that is, immobilized chloromethylated polystyrene the adsorbent of cationization beta-cyclodextrin.
The synthetic method of formula (I) cation cyclodextrin
The synthetic method of formula (II) chloromethylated polystyrene
The solid support method of formula (III) cation cyclodextrin
Embodiment 2:
The preparation (2) of adsorbent material:
1g beta-cyclodextrin is dissolved in 10mL pure water, stirring 10min makes it dissolve, and 1g2,3- epoxy is added Ammonium chloride (ETMAC), and with sodium hydrate regulator solution pH make its 13,4.5h is stirred at 70 DEG C, filter, evaporation obtain depth Brown viscous object i.e. cationization beta-cyclodextrin;0.48g polyvinyl alcohol is dissolved in the pure water of 200mL, 6.4g chlorination is added Sodium is slowly added to 30g styrene, 4g divinylbenzene, 10g p-chloromethyl styrene and 0.64g into the solution at room temperature The mixed solution of benzoyl peroxide reacts 30min, then heats at 60 DEG C, reacts 2h, is continuously heating to 80 DEG C, reaction 10h, obtained product is cooling, filtering, dry in 70 DEG C of air dry oven after being washed for several times with 60~80 DEG C of warm water 6h obtains yellow final products chloromethylated polystyrene;1g cationization beta-cyclodextrin is dissolved in 20mL water, 2mL pyrrole is added 1h is stirred in pyridine at room temperature, and 5g chloromethylated polystyrene is then added, and the product cooling obtained for 24 hours, mistake are reacted at 90 DEG C Filter, after being washed for several times with 60~80 DEG C of warm water, dry 6h, obtains dark brown and rough surface in 70 DEG C of air dry oven Final products, that is, immobilized cationization beta-cyclodextrin chloromethylated polystyrene adsorbent.
Embodiment 3:
The preparation (3) of adsorbent material:
1g beta-cyclodextrin is dissolved in 20mL pure water, stirring 10min makes it dissolve, and 10g2,3- glycidyl front three is added Ammonium chloride (ETMAC), and with sodium hydrate regulator solution pH make its 13,4.5h is stirred at 70 DEG C, is filtered, evaporation obtains Dark brown dope i.e. cationization beta-cyclodextrin;0.24g polyvinyl alcohol is dissolved in the pure water of 100mL, 3.2g chlorine is added Change sodium, be slowly added at room temperature into the solution 15g styrene, 2g divinylbenzene, 15g p-chloromethyl styrene and The mixed solution of 0.32g benzoyl peroxide reacts 30min, then heats at 60 DEG C, reacts 2h, is continuously heating to 80 DEG C, 10h is reacted, obtained product is cooling, filtering, after being washed for several times with 60~80 DEG C of warm water, does in 70 DEG C of air dry oven Dry 6h obtains yellow final products Chloromethyl polystyrene;1g cationization beta-cyclodextrin is dissolved in 10mL water, 1mL pyrrole is added 1h is stirred in pyridine at room temperature, and 2.5g chloromethylated polystyrene is then added, and the product cooling obtained for 24 hours is reacted at 30 DEG C, Filtering, after being washed for several times with 60~80 DEG C of warm water, dry 6h, is obtained faint yellow and powder in 70 DEG C of air dry oven Final products, that is, immobilized chloromethylated polystyrene the adsorbent of beta-cyclodextrin.
Embodiment 4:
The processing of wastewater containing phenol solution:
By the adsorbent material 0.15g of embodiment 1, puts into the phenolic waste water solution of 100mL 500mg/L and is placed at 25 DEG C, 2h is vibrated with the full temperature culture shaking table of the speed oscillation of 200rpm, after oscillation, supernatant is taken to use UV-Vis spectrophotometry Luminosity measures the content of Phenol in Aqueous Solution, is learnt by result, and the adsorbance of adsorbent Pyrogentisinic Acid is 140mg/g;Then with 0.4% + 50% ethyl alcohol of sodium hydroxide is eluted, and the content of Phenol in Aqueous Solution sodium is surveyed using ultraviolet-visible spectrophotometer, by tying Eluting rate known to fruit is 95%.
Embodiment 5:
The processing of the waste water solution containing salicylic acid:
By the adsorbent material 0.15g of embodiment 1, puts into the salicylic acid waste water solution of 100mL 400mg/L and be placed in 25 DEG C Under, 2h is vibrated with the full temperature culture shaking table of the speed oscillation of 200rpm, after oscillation, supernatant is taken to use ultraviolet-visible light Spectrophotometric measures salicylic content in solution, is learnt by result, and the adsorbance of adsorbent Pyrogentisinic Acid is 170mg/g;Then It is eluted with+50% ethyl alcohol of 0.02% sodium hydroxide, surveys sodium salicylate in solution using ultraviolet-visible spectrophotometer Content, eluting rate is 80% as can be seen from the results.
Embodiment 6:
The processing of the waste water solution containing parachlorophenol:
By the adsorbent material 0.15g of embodiment 1, puts into the parachlorophenol waste water solution of 100mL 500mg/L and be placed in 25 At DEG C, 2h is vibrated with the full temperature culture shaking table of the speed oscillation of 200rpm, after oscillation, supernatant is taken to use ultraviolet-visible Light spectrophotometric measures the content of Phenol in Aqueous Solution, is learnt by result, and adsorbent is 250mg/g to the adsorbance of parachlorophenol; Then it is eluted with+50% ethyl alcohol of 0.4% sodium hydroxide, surveys parachlorphenol in solution using ultraviolet-visible spectrophotometer The content of sodium, eluting rate is 90% as can be seen from the results.
Embodiment 7:
The processing of the waste water solution containing p-cresol:
By the adsorbent material 0.15g of embodiment 1, puts into the parachlorophenol waste water solution of 100mL 200mg/L and be placed in 25 At DEG C, 2h is vibrated with the full temperature culture shaking table of the speed oscillation of 200rpm, after oscillation, supernatant is taken to use ultraviolet-visible Light spectrophotometric measures the content of Phenol in Aqueous Solution, is learnt by result, and adsorbent is 96mg/g to the adsorbance of parachlorophenol;So It is eluted afterwards with+50% ethyl alcohol of 0.4% sodium hydroxide, surveys p-cresol in solution using ultraviolet-visible spectrophotometer The content of sodium, eluting rate is 85% as can be seen from the results.

Claims (8)

1. a kind of chloromethylated polystyrene polymer of immobilized cationization beta-cyclodextrin, it is characterised in that by following steps system It is standby to form:
(1) by cyclodextrin and 2,3- epoxypropyltrimethylchloride chloride is 1:1~10:1 mixing in mass ratio, adds 10mL Water, and make its pH=13 with sodium hydrate regulator solution, 1~4.5h is finally reacted at 40~90 DEG C, is cationized Cyclodextrin;
(2) styrene or other olefines for containing phenyl ring and p-chloromethyl styrene 1:1~4:1 ratio in mass ratio are mixed Monomer as polymerized monomer, dissolve the dispersant into water, at room temperature, be added crosslinking agent, polymerized monomer, initiator, 40~80 DEG C are reacted;Polymer is obtained after completion of the reaction, after hot water washing for several times, obtained product is done It is dry, obtain high molecular polymer;The weight fraction ratio of each substance are as follows: 10~40 parts of polymerized monomer, crosslinking agent: 1~3 part, dispersion Agent: 0.1~2 part, initiator: 0.1~4 part, water: 100~400 parts;
(3) cationized cyclodextrins and water obtained step (1) are mixed in 1:10~1:70 ratio, make cationized cyclodextrins Dissolution, and pyridine is added, 1h is stirred at room temperature, then at a temperature of 40~90 DEG C, it is poly- that chloromethylation made from step (2) is added Styrene reacts for 24 hours;The chloromethylated polystyrene and cationized cyclodextrins ratio of addition are 1:1~3:1;After completion of the reaction Required polymer is obtained, after hot water washing for several times, obtained product is dried, obtains immobilized cationization β-ring paste The chloromethylated polystyrene polymer of essence.
2. the chloromethylated polystyrene polymer of immobilized cationization beta-cyclodextrin according to claim 1, feature It is, the cyclodextrin is beta-cyclodextrin or hydroxypropyl-β-cyclodextrin.
3. the chloromethylated polystyrene polymer of immobilized cationization beta-cyclodextrin according to claim 1, feature It is, the dispersing agent is polyvinyl alcohol, polyethylene glycol, hydroxyethyl cellulose, hydroxypropyl cellulose or methylcellulose.
4. the chloromethylated polystyrene polymer of immobilized cationization beta-cyclodextrin according to claim 1, feature It is, the initiator is one or both of dibenzoyl peroxide, cumyl peroxide and azodiisobutyronitrile Mixture.
5. the chloromethylated polystyrene polymer of immobilized cationization beta-cyclodextrin according to claim 1, feature It is, the crosslinking agent is divinylbenzene, diisocyanate, acrylic acid, methacrylic acid, hydroxypropyl acrylate or methyl Hydroxypropyl acrylate.
6. the chloromethylated polystyrene Polymer adsorption using immobilized cationization beta-cyclodextrin described in claim 1 recycles The method of Phenols In Industrial Liquid Waste class, it is characterised in that include the following steps:
(1) the chloromethylated polystyrene polymer of immobilized cationization beta-cyclodextrin is added to the work containing phenolic compound It in industry waste water, vibrates or stirs at room temperature, be separated by filtration, Phenol for Waste Water class compound is attracted to immobilized cationization β-ring paste In the chloromethylated polystyrene polymer of essence;
(2) the chloromethylated polystyrene polymer of the immobilized cationization beta-cyclodextrin of absorbing phenolic compound is added to In desorbing agent, at room temperature vibrate or stir, filtering, phenolic compound is desorbed, recycling obtain phenolic compound and it is immobilized sun from The chloromethylated polystyrene polymer of sonization beta-cyclodextrin;
(3) the chloromethylated polystyrene polymer of the immobilized cationization beta-cyclodextrin of recycling is placed in 60~70 DEG C of baking ovens Drying, dry 5~6h, storage is in case use next time.
7. according to the method described in claim 6, it is characterized in that, the chloromethyl of the immobilized cationization beta-cyclodextrin of adsorbent material The mass volume ratio for changing poly styrene polymer and industrial wastewater is 1:10~10:1g/L.
8. according to the method described in claim 6, it is characterized in that, desorbing agent is the mixing of ethyl alcohol or ethyl alcohol and sodium hydroxide Object.
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