CN104177536A - Chelating resin adsorbing material and preparation method thereof - Google Patents

Chelating resin adsorbing material and preparation method thereof Download PDF

Info

Publication number
CN104177536A
CN104177536A CN201410360870.XA CN201410360870A CN104177536A CN 104177536 A CN104177536 A CN 104177536A CN 201410360870 A CN201410360870 A CN 201410360870A CN 104177536 A CN104177536 A CN 104177536A
Authority
CN
China
Prior art keywords
resin
sorbing material
copolymerization
preparation
agent
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201410360870.XA
Other languages
Chinese (zh)
Inventor
王津南
程澄
杨欣
陈晨
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Nanjing University
Original Assignee
Nanjing University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Nanjing University filed Critical Nanjing University
Priority to CN201410360870.XA priority Critical patent/CN104177536A/en
Publication of CN104177536A publication Critical patent/CN104177536A/en
Priority to PCT/CN2015/083882 priority patent/WO2016011900A1/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • B01J20/26Synthetic macromolecular compounds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • 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
    • C02F1/58Treatment of water, waste water, or sewage by removing specified dissolved compounds
    • C02F1/62Heavy metal compounds
    • 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
    • C08F212/34Monomers containing two or more unsaturated aliphatic radicals
    • C08F212/36Divinylbenzene
    • 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
    • C08F220/00Copolymers of compounds having one or more unsaturated aliphatic radicals, each having only one carbon-to-carbon double bond, and only one being terminated by only one carboxyl radical or a salt, anhydride ester, amide, imide or nitrile thereof
    • C08F220/02Monocarboxylic acids having less than ten carbon atoms; Derivatives thereof
    • C08F220/10Esters
    • C08F220/12Esters of monohydric alcohols or phenols
    • C08F220/14Methyl esters, e.g. methyl (meth)acrylate
    • 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
    • C08F8/00Chemical modification by after-treatment
    • C08F8/30Introducing nitrogen atoms or nitrogen-containing groups

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Health & Medical Sciences (AREA)
  • Medicinal Chemistry (AREA)
  • Polymers & Plastics (AREA)
  • Engineering & Computer Science (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Addition Polymer Or Copolymer, Post-Treatments, Or Chemical Modifications (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

The invention discloses a chelating resin adsorbing material and a preparation method thereof, and belongs to the field of environmental functional material synthesis and application. The chelating resin adsorbing material is prepared through suspension copolymerization and nucleophilic substitution reaction by adopting an organic monomer as a raw material; the chelating resin adsorbing material comprises a skeleton and hydroxamic acid, wherein the skeleton is formed by copolymerizing methyl acrylate and divinylbenzene, and the hydroxamic acid is formed through surface modification. The synthetic method disclosed by the invention is simple. According to the chelating resin adsorbing material, the equilibrium adsorption time of heavy metal ions, namely cadmium, nickel, lead and the like which are contained in group chelating water formed through the modification of a functional group modified on the surface of the prepared chelating resin adsorbing material and the resin skeleton, is about only 20 minutes, and the saturation adsorption capacity on the heavy metal ions, namely the cadmium, the nickel, the lead and the like, is more than or equal to 2 mmol/g.

Description

A kind of resin sorbing material and preparation method thereof
Technical field:
The invention discloses a kind of sorbing material and preparation method thereof, say more specifically a kind of resin sorbing material and preparation method thereof, the vinylformic acid formicester of modifying based on hydroxamic acid base and resin of divinylbenzene copolymerization and preparation method thereof.
Background technology:
In recent years, along with national water quality standard progressively improves, more and more strict for the restriction of heavy metals ionic concn, efficiently removing heavy metal ion in water becomes the study hotspot in water pollution control field.Although existing traditional Coagulation Method and chemical precipitation method technical maturity are simple to operate, the plurality of heavy metal body refuse producing in treating processes is difficult to dispose, and easily brings secondary pollution.And electrolytic process, membrane separation process are subject to the factor restrictions such as processing cost and are difficult for being used by large-scale promotion; Although Zeo-karb has very high adsorption rate and capacity for heavy metal ion, its immunity from interference to calcium ions and magnesium ions and natural organic matter need to improve.Resin has very strong sequestering action by contained functional group to heavy metal ion, is subject to hardly the impact of calcium ions and magnesium ions and natural organic matter in adsorption process, becomes first-selected sorbing material in heavy metal wastewater thereby improvement.
But existing resin is mainly polystyrene series and polyacrylate based series, its synthetic method is mainly synthetic polystyrene-divinylbenzene polymer or polyacrylate polymers, then on polymkeric substance, modify the functional group such as carboxyl, amino, utilize the above-mentioned group chelating of modifying to remove heavy metal ion in water, but in adsorption process, polystyrene-divinylbenzene, polyacrylic ester in polymer backbone are not participated in sequestering action, and this causes the absorption property of such resin to be controlled by the functional group quantity of finishing completely.But the functional group limited amount of existing resin surface chemical modification, therefore resin is difficult to be greatly improved to the loading capacity of heavy metal ion.
Therefore, how in resin rhetorical function group, to make resin polystyrene-divinylbenzene skeleton, polyacrylic ester skeleton itself participate in heavy metal ion in sequestering action water, it is an effective approach that improves resin loading capacity, application for resin in heavy metal wastewater thereby is administered has important pushing effect, has great theory directive significance and actual application value.
Summary of the invention:
1, the technical problem that invention will solve
The technical barrier that cannot promote because being controlled by finishing group quantity completely the loading capacity of heavy metal ion for existing resin, the invention provides a kind of resin sorbing material and preparation method thereof: the multipolymer that makes methyl acrylate and divinylbenzene by suspension polymerization, then by azanol, interpolymer skeleton itself is directly carried out to chemically modified, make the resin that contains hydroxamic acid structure.Freshly prepd resin not only can be removed heavy metal ion in water by the azanol group chelating of modifying, and carbonyl intrinsic on resin matrix also can participate in sequestering action, even in the situation that concentration of heavy metal ion is very low, still there is good Adsorption effect, and loading capacity is large.
2, technical scheme
Resin sorbing material of the present invention is by after methyl acrylate and divinylbenzene copolymerization, carries out chemically modified preparation and obtains, be i.e. the hydroxamic acid formation that its skeleton forming with methyl acrylate and divinylbenzene copolymerization and finishing forms.On resin upper skeleton, intrinsic carbonyl participates in chelating heavy metal effect (wherein M represents heavy metal ion) jointly with the azanol group on modifying.
A kind of resin sorbing material, following (the wherein R of its synthesis flow and basic structure formula 1=NH-OH, R 2=OCH 3or NH-OH):
A kind of resin sorbing material preparation method, the steps include:
(1) preparation reaction emulsion
By polymerization reaction monomer, linking agent, dispersion agent, pore-creating agent and distilled water mixed preparing reaction emulsion, wherein the proportioning of polymerization reaction monomer, linking agent, dispersion agent, pore-creating agent and distilled water is 90mL:8~12mL:6g:30~40mL:400mL;
The monomer using in step (1) is methyl acrylate; The linking agent using is divinylbenzene; The dispersion agent using is the one in gelatin, polyvinyl alcohol or polyethylene wax; The pore-creating agent using is a kind of or its two kinds the mixture in normal heptane, ethyl acetate, toluene.
(2) copolyreaction
In emulsion, add initiator, the ratio of initiator and emulsion is 1~2g:500mL or 1~2mL:500mL, reacts 8~12 hours at 90~95 DEG C, obtains copolymerization ball WJNCC, 40~50 DEG C of vacuum-dryings after ethanol cleans.
The initiator using in step (2) is selected from the one in benzoyl peroxide, di-t-butyl peroxide or azo diethyl butyronitrile.
(3) copolymerization ball finishing
(a) alkali and azanol, emulsifying agent, distilled water are mixed with to reaction solution, its proportioning is 2~3g:2~3g:1mL:100mL;
(b) after copolymerization ball is mixed with above-mentioned reaction solution, the mass ratio of copolymerization ball and azanol is 1:1~1.5,45~60 DEG C of reactions 12~16 hours, obtains final product resin sorbing material MA-DVB, 40~50 DEG C of vacuum-dryings after distilled water cleans.
The alkali using in step (3-a) is sodium hydroxide or potassium hydroxide; The azanol using is elected oxammonium hydrochloride or oxammonium sulfate as; The emulsifying agent using is the one in polyethenoxy sorbitan oleic acid ester, polyoxyethylene oleic acid ester, Glycerol dimer polypropylene glycol ether.
3, beneficial effect
The invention provides a kind of preparation method of resin sorbing material: methyl acrylate and divinylbenzene copolymer, after chemically modified, form hydroxamic acid structure on resin matrix.This resin can be used in heavy metal wastewater thereby adsorption treatment field, and the heavy metal wastewater thereby of high density and lower concentration is all had to good treatment effect.The main raw material that the present invention simultaneously adopts is large Chemicals, and cheap and easy to get, synthesis technique step is simple.
Brief description of the drawings
Owing to preparing monomer and linking agent only has one, the group that chemically modified forms only has hydroxamic acid one, so the structure of the resin sorbing material preparing only has one.Common trait be due to chemically modified be difficult to carry out completely, cause certainly existing methoxyl group in resin sorbing material chemical structure.
Fig. 1 is the structure that the structure iron of the resin sorbing material for preparing of example 1-6 of the present invention contains hydroxamic acid.
Fig. 2 is copolymerization ball and resin sorbing material infrared spectrum, wherein the δ 1736.2cm that example 4 of the present invention prepares -1for the ester group characteristic peak of copolymerization ball, 1737.8cm -1for the ester group characteristic peak of resin, 1572.8cm -1and 3432.5cm -1for resin functional group characteristic peak, according to reference (Xing Qiyi, Pei Weiwei etc., basic organic chemistry, Higher Education Publishing House, the third edition in 2005, p184); Wherein WJNCC is the copolymerization ball that copolyreaction obtains, and MA-DVB is the resin after copolymerization Geochemistry is modified.
The solid-state nuclear magnetic resonance carbon spectrum of the resin sorbing material that Fig. 3 (a) prepares for embodiment 4; Fig. 3 (b) solid-state nuclear magnetic resonance 13structure iron corresponding to C NMR collection of illustrative plates characteristic peak, in Fig. 3 (a), its characteristic peak δ 185.79, δ 175.92, δ 144.74, δ 128.48, δ 51.78, the corresponding structure of δ 40.88 are listed in Fig. 3 (b).According to reference (Xing Qiyi, Pei Weiwei etc., basic organic chemistry, Higher Education Publishing House, the third edition in 2005, p216).
Fig. 4 is 500 times of Electronic Speculum figure of resin scanning that embodiment 4 makes.
Fig. 5 is the resin graph of pore diameter distribution that embodiment 4 makes, and X-coordinate is aperture (nm), and ordinate zou is pore volume (cm 3/ g) differential (the cm to aperture 3g -1nm -1).Fig. 5 shows that resin aperture prepared by embodiment 4 is mainly distributed in 4~6nm, is mainly mesopore (mesopore).
Embodiment
Embodiment 1
90mL methyl acrylate, 9mL divinylbenzene, gelatin 6g, 35mL normal heptane, 400mL distilled water are made into emulsion.The 500mL emulsion of preparation is poured in 1000mL three-necked flask, added benzoyl peroxide 1g, 95 DEG C of heating in water bath, and with the rotating speed stirring reaction of 60r/min 8 hours, reaction gained copolymerization ball is carried out to solid-liquid separation, and by washing with alcohol, 50 DEG C of vacuum-dryings.Get 10g potassium hydroxide, 15g oxammonium sulfate, 5mL polyoxyethylene oleic acid ester, 500mL distilled water wiring solution-forming, pour in 1000mL three-necked flask, after adding 10g copolymerization ball, mix, stir speed (S.S.) with 60r/min at 45 DEG C is reacted 16 hours, after filtering, product uses distilled water wash, vacuum-drying at 50 DEG C, obtains resin sorbing material finished product.
Its physicochemical property of resin sorbing material that the present embodiment prepares is as follows:
Resin structure as shown in Figure 1.
Embodiment 2
90mL methyl acrylate, 11mL divinylbenzene, polyvinyl alcohol 6g, 40mL ethyl acetate, 400mL distilled water are made into emulsion.500mL emulsion is poured in 1000mL three-necked flask, added di-t-butyl peroxide 2mL, 94 DEG C of heating in water bath, and with the rotating speed stirring reaction of 60r/min 9 hours, reaction gained copolymerization ball is carried out to solid-liquid separation, and by washing with alcohol, 45 DEG C of vacuum-dryings.Get 15g sodium hydroxide, 10g oxammonium hydrochloride, 5mL polyethenoxy sorbitan oleic acid ester, 500mL distilled water wiring solution-forming, pour in 1000mL three-necked flask, after adding 10g copolymerization ball, mix, stir speed (S.S.) with 60r/min at 48 DEG C is reacted 15 hours, after filtering, product uses distilled water wash, vacuum-drying at 45 DEG C, obtains resin sorbing material finished product.Its physicochemical property of resin sorbing material that the present embodiment prepares is as follows:
Resin structure as shown in Figure 1.
Embodiment 3
90mL methyl acrylate, 8mL divinylbenzene, polyethylene wax 6g, 30mL toluene, 400mL distilled water are made into emulsion.500mL emulsion is poured in 1000mL three-necked flask, added azo diethyl butyronitrile 2g, 93 DEG C of heating in water bath, and with the rotating speed stirring reaction of 60r/min 10 hours, reaction gained copolymerization ball is carried out to solid-liquid separation, and by washing with alcohol, 40 DEG C of vacuum-dryings.Get 12g sodium hydroxide, 12g oxammonium sulfate, 5mL Glycerol dimer polypropylene glycol ether, 500mL distilled water wiring solution-forming, pour in 1000mL three-necked flask, after adding 10g copolymerization ball, mix, stir speed (S.S.) with 60r/min at 52 DEG C is reacted 14 hours, after filtering, product uses distilled water wash, vacuum-drying at 40 DEG C, obtains resin sorbing material finished product.Its physicochemical property of resin sorbing material that the present embodiment prepares is as follows:
Resin structure as shown in Figure 1.
Embodiment 4
90mL methyl acrylate, 12mL divinylbenzene, gelatin 6g, 20mL ethyl acetate, 20mL normal heptane, 400mL distilled water are made into emulsion.500mL emulsion is poured in 1000mL three-necked flask, added benzoyl peroxide 1.5g, 92 DEG C of heating in water bath, and with the rotating speed stirring reaction of 60r/min 11 hours, reaction gained copolymerization ball is carried out to solid-liquid separation, and by washing with alcohol, 40 DEG C of vacuum-dryings.Get 14g potassium hydroxide, 11g oxammonium hydrochloride, 5mL polyoxyethylene oleic acid ester, 500mL distilled water wiring solution-forming, pour in 1000mL three-necked flask, after adding 10g copolymerization ball, mix, stir speed (S.S.) with 60r/min at 56 DEG C is reacted 13 hours, after filtering, product uses distilled water wash, vacuum-drying at 45 DEG C, obtains resin sorbing material finished product.
Be illustrated in figure 1 the structure iron of the resin sorbing material that the present embodiment prepares, be illustrated in figure 2 the FT-IR collection of illustrative plates of the resin sorbing material that the present embodiment prepares, after copolymerization, occur ester group characteristic peak at δ 1736.2 places; After chemically modified, occurring N-H flexural vibration absorption peak at δ 1572.8, occur N-H stretching vibration absorption peak at δ 3432.5, is also O-H stretching vibration absorption peak, prove the existence of hydroxamic acid structure, the resin sorbing material preparing for the present embodiment as Fig. 3 (a) 13c NMR collection of illustrative plates, its characteristic peak δ 185.79, δ 175.92, δ 144.74, δ 128.48, δ 51.78, the corresponding structure of δ 40.88 are listed in Fig. 3 (b).Synthesizing map 2 Infrared spectroscopy and Fig. 3 nuclear magnetic resonance spectroscopy, can confirm that resin sorbing material is as the structure of Fig. 1.Fig. 4 is the resin scanning electron microscope (SEM) photograph that the present embodiment makes.Fig. 5 is the resin graph of pore diameter distribution that the present embodiment makes.Its physicochemical property of resin sorbing material that the present embodiment prepares is as follows:
This embodiment is most preferred embodiment: pore-creating agent ethyl acetate boiling point lower (77 DEG C), and normal heptane boiling point higher (98.5 DEG C), the use that mixes pore-creating agent makes the pore effect of pore-creating agent just be embodied in preparation process, along with the rising of temperature, ethyl acetate can be evaporated in advance, the space staying makes normal heptane be more prone to penetrate into resin matrix, obtains better pore passage structure.
Embodiment 5
90mL methyl acrylate, 10mL divinylbenzene, polyvinyl alcohol 6g, 20mL toluene, 20mL ethyl acetate, 400mL distilled water are made into emulsion.500mL emulsion is poured in 1000mL three-necked flask, added di-t-butyl peroxide 1.5mL, 90 DEG C of heating in water bath, and with the rotating speed stirring reaction of 60r/min 12 hours, reaction gained copolymerization ball is carried out to solid-liquid separation, and by washing with alcohol, 50 DEG C of vacuum-dryings.Getting 12g sodium hydroxide, 13g oxammonium hydrochloride, 5mL polyethenoxy sorbitan oleic acid ester, 500mL distilled water wiring solution-forming pours in 1000mL three-necked flask, after adding 10g copolymerization ball, mix, stir speed (S.S.) with 60r/min at 60 DEG C is reacted 12 hours, after filtering, product uses distilled water wash, vacuum-drying at 50 DEG C, obtains resin sorbing material finished product.
Resin structure as shown in Figure 1.
Embodiment 6
Concrete steps and amount of substance are with embodiment 5, and difference is to add di-t-butyl peroxide 1.0mL.Prepare resin sorbing material finished product.
Resin structure as shown in Figure 1.

Claims (5)

1. a resin sorbing material, is characterized in that, the hydroxamic acid that the skeleton that it forms with methyl acrylate and divinylbenzene copolymerization and finishing form forms, and its basic structure formula is as follows:
wherein R 1=NH-OH, R 2=OCH 3or NH-OH.
2. a preparation method for resin sorbing material, the steps include:
(1) preparation reaction emulsion
By polymerization reaction monomer, linking agent, dispersion agent, pore-creating agent and distilled water mixed preparing reaction emulsion, wherein the proportioning of polymerization reaction monomer, linking agent, dispersion agent, pore-creating agent and distilled water is 90mL:8~12mL:6g:30~40mL:400mL;
(2) copolyreaction
In the emulsion making in step 1, add initiator, the ratio of initiator and emulsion is 1~2g:500mL or 1~2mL:500mL, reacts 8~12 hours at 90~95 DEG C, obtains copolymerization ball WJNCC, 40~50 DEG C of vacuum-dryings after ethanol cleans;
(3) chemically modified of copolymerization ball
A. alkali and azanol, emulsifying agent, distilled water are mixed with to reaction solution, its proportioning is: 2~3g:2~3g:1mL:100mL;
B. after copolymerization ball step (2) being made mixes with the reaction solution of preparing in above-mentioned steps 3-a, wherein the mass ratio of copolymerization ball and azanol is 1:1~1.5,45~60 DEG C of reactions 12~16 hours, obtain resin sorbing material MA-DVB, 40~50 DEG C of vacuum-dryings after distilled water cleans.
3. the preparation method of resin sorbing material according to claim 2, is characterized in that, the polymerization reaction monomer of described step (1) is methyl acrylate; Linking agent is divinylbenzene; Dispersion agent is the one in gelatin, polyvinyl alcohol or polyethylene wax; Pore-creating agent is a kind of or its two or more mixtures in normal heptane, ethyl acetate, toluene.
4. according to the preparation method of the resin sorbing material described in claim 2 or 3, it is characterized in that, the initiator of described step (2) is the one in benzoyl peroxide, di-t-butyl peroxide or Diisopropyl azodicarboxylate.
5. according to the preparation method of a kind of resin sorbing material described in claim 2 or 3, it is characterized in that, the alkali of described step (3) is elected potassium hydroxide or sodium hydroxide as; Azanol is elected oxammonium hydrochloride or oxammonium sulfate as; Emulsifying agent is the one in polyethenoxy sorbitan oleic acid ester, polyoxyethylene oleic acid ester or Glycerol dimer polypropylene glycol ether.
CN201410360870.XA 2014-07-25 2014-07-25 Chelating resin adsorbing material and preparation method thereof Pending CN104177536A (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
CN201410360870.XA CN104177536A (en) 2014-07-25 2014-07-25 Chelating resin adsorbing material and preparation method thereof
PCT/CN2015/083882 WO2016011900A1 (en) 2014-07-25 2015-07-13 Chelating resin adsorbing material and preparation method therefor

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410360870.XA CN104177536A (en) 2014-07-25 2014-07-25 Chelating resin adsorbing material and preparation method thereof

Publications (1)

Publication Number Publication Date
CN104177536A true CN104177536A (en) 2014-12-03

Family

ID=51958901

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410360870.XA Pending CN104177536A (en) 2014-07-25 2014-07-25 Chelating resin adsorbing material and preparation method thereof

Country Status (2)

Country Link
CN (1) CN104177536A (en)
WO (1) WO2016011900A1 (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2016011900A1 (en) * 2014-07-25 2016-01-28 南京大学 Chelating resin adsorbing material and preparation method therefor
CN106807340A (en) * 2017-02-06 2017-06-09 中南大学 A kind of crosslinked resin hydroximic acid composite adsorbing material and preparation method and application
CN109183199A (en) * 2018-11-22 2019-01-11 淮安天然丝纺织科技有限公司 A kind of NMMO solvent recovery method for concentration
CN113083256A (en) * 2021-04-13 2021-07-09 北京赛科康仑环保科技有限公司 Adsorbing material for deep oil removal of neutral phosphorus-containing extraction system and preparation and application methods thereof

Families Citing this family (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105597687B (en) * 2016-03-04 2017-11-14 云南圣清环保科技有限公司 A kind of sorbing material preparation method for the carrying functional form microorganism for being used to handle arsenic-containing waste water
CN112724455B (en) * 2020-12-10 2022-12-23 中国科学院青岛生物能源与过程研究所 Preparation method of efficient high-selectivity polyol adsorption material
CN113277475B (en) * 2021-05-27 2023-12-12 浙江凯圣氟化学有限公司 Method for removing metal ions in anhydrous hydrogen fluoride
CN113498790A (en) * 2021-07-02 2021-10-15 上海鑫灵精细化工有限公司 Functional group immobilized nano-silver material, and preparation method and application thereof
CN113856640A (en) * 2021-08-26 2021-12-31 中南大学 Preparation method of hydroximic acid modified resin and application of hydroximic acid modified resin in separation of gallium from high-acid high-impurity gallium-containing solution
CN115121231B (en) * 2022-05-11 2023-11-24 中核四0四有限公司 Special resin for adsorbing americium in radioactive wastewater and preparation method thereof
CN115672287B (en) * 2022-09-16 2024-02-09 苏州博进生物技术有限公司 Modified chelating resin for heavy metal ion adsorption
CN115819652B (en) * 2022-12-06 2023-09-05 中南大学 2-aminopentanedioxime acid modified polyacrylic acid chelate resin and preparation method and application thereof

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS62182113A (en) * 1986-02-01 1987-08-10 Agency Of Ind Science & Technol Fractionation and recovery of gallium and indium
JPH0770231A (en) * 1993-07-13 1995-03-14 Hoechst Ag Metal-ion-absorbing modified acrylonitrile polymer
CN102921393A (en) * 2012-04-25 2013-02-13 河北工业大学 Granular three-dimensional ordered macroporous chelating resin preparation method
CN103464124A (en) * 2013-10-09 2013-12-25 南京大学 Spongy emergency adsorbing material and preparation method thereof

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE102007034731A1 (en) * 2007-07-23 2009-01-29 Lanxess Deutschland Gmbh chelating resins
JP5631363B2 (en) * 2011-08-31 2014-11-26 ダウ グローバル テクノロジーズ エルエルシー Improved shell functionalized ion exchange resin
CN104177536A (en) * 2014-07-25 2014-12-03 南京大学 Chelating resin adsorbing material and preparation method thereof

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS62182113A (en) * 1986-02-01 1987-08-10 Agency Of Ind Science & Technol Fractionation and recovery of gallium and indium
JPH0770231A (en) * 1993-07-13 1995-03-14 Hoechst Ag Metal-ion-absorbing modified acrylonitrile polymer
CN102921393A (en) * 2012-04-25 2013-02-13 河北工业大学 Granular three-dimensional ordered macroporous chelating resin preparation method
CN103464124A (en) * 2013-10-09 2013-12-25 南京大学 Spongy emergency adsorbing material and preparation method thereof

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
YUAN-HUI PENG ET AL: ""Preparation of a novel chelating resin for the removal of Ni2+ from water"", 《CHINESE CHEMICAL LETTERS》 *
YUAN-HUI PENG ET AL: ""Preparation of a novel chelating resin for the removal of Ni2+ from water"", 《CHINESE CHEMICAL LETTERS》, vol. 25, 4 December 2013 (2013-12-04), XP028829062, DOI: doi:10.1016/j.cclet.2013.11.001 *
张骞: ""羟肟酸树脂的合成及其对矿山酸性废水的吸附特性研究"", 《中国优秀硕士学位论文全文数据库·工程科技I辑》 *
蔺相阳: "《含能高分子材料球形化技术》", 31 January 2014, 北京:化学工业出版社 *

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2016011900A1 (en) * 2014-07-25 2016-01-28 南京大学 Chelating resin adsorbing material and preparation method therefor
CN106807340A (en) * 2017-02-06 2017-06-09 中南大学 A kind of crosslinked resin hydroximic acid composite adsorbing material and preparation method and application
CN106807340B (en) * 2017-02-06 2019-07-12 中南大学 A kind of crosslinked resin-hydroximic acid composite adsorbing material and the preparation method and application thereof
CN109183199A (en) * 2018-11-22 2019-01-11 淮安天然丝纺织科技有限公司 A kind of NMMO solvent recovery method for concentration
CN113083256A (en) * 2021-04-13 2021-07-09 北京赛科康仑环保科技有限公司 Adsorbing material for deep oil removal of neutral phosphorus-containing extraction system and preparation and application methods thereof

Also Published As

Publication number Publication date
WO2016011900A1 (en) 2016-01-28

Similar Documents

Publication Publication Date Title
CN104177536A (en) Chelating resin adsorbing material and preparation method thereof
Cao et al. Synthesis and evaluation of molecularly imprinted polymers with binary functional monomers for the selective removal of perfluorooctanesulfonic acid and perfluorooctanoic acid
CN101434673B (en) Preparation of monodisperse porous polymer microsphere
CN104437396B (en) Preparation method of lignin-amine microsphere
US9950319B2 (en) High exchange-capacity anion exchange resin with dual functional-groups and method of synthesis thereof
CN102500296A (en) Preparation method for mesoporous silicon oxide hollow microspheres with magnetic nanoparticles embedded in shell layers
CN101045755A (en) Preparation method of non-porous or porous polymer microsphere of surface function
CN105254818A (en) High-oil-absorption resin and preparation method thereof
Roy et al. Valorization of waste eggshell-derived bioflocculant for harvesting T. obliquus: process optimization, kinetic studies and recyclability of the spent medium for circular bioeconomy
Chai et al. In-suit ion-imprinted bio-sorbent with superior adsorption performance for gallium (III) capture
CN105664897A (en) Method for preparing magnetic porous microsphere adsorbing material by utilizing O/W/O double emulsion template
CN105949395A (en) Molecular cluster material of supramolecular polymer and preparation method and application of molecular cluster material
Mishra et al. Treatment of gray wastewater and heavy metal removal from aqueous medium using hydrogels based on novel crosslinkers
Qiu et al. Facile preparation of acrylic ester-based crosslinked resin and its adsorption of phenol at high concentration
CN104262521A (en) Preparation method of styrene-divinylbenzene copolymer hydrophobic catalyst support
CN111437798A (en) Amidoxime group hypercrosslinked microporous resin efficient uranium adsorbent and preparation method thereof
CN104324702A (en) Preparation method of sodium alginate-lignin composite gel beads
CN106317742B (en) A kind of function nano network structure polymer material and the preparation method and application thereof
CN104004131B (en) High specific surface area amphoteric adsorption resin containing pyrrolidone bases and preparation method thereof
Lin et al. Film-like chitin/polyethylenimine biosorbent for highly efficient removal of uranyl-carbonate compounds from water
CN104478056A (en) Sewage disposal agent
Li et al. Study on the dispersion performance and mechanism of polycarboxylate superplasticizer by the long side‐chain dicarboxyl terminated
CN106242005B (en) A kind of fatty long-chain can be used for the high polymer coagulant and preparation method thereof of coal chemical industrial waste water oil removing
Guo et al. Modified corn-core powder for enhancing sludge dewaterability: Synthesis, characterization and sludge dewatering performance
CN103464124B (en) Spongy emergency adsorbing material and preparation method thereof

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20141203

RJ01 Rejection of invention patent application after publication