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CN109248667A - A kind of chitosan graft object and its preparation method and application - Google Patents

A kind of chitosan graft object and its preparation method and application Download PDF

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Publication number
CN109248667A
CN109248667A CN201811140943.9A CN201811140943A CN109248667A CN 109248667 A CN109248667 A CN 109248667A CN 201811140943 A CN201811140943 A CN 201811140943A CN 109248667 A CN109248667 A CN 109248667A
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China
Prior art keywords
chitosan
acetic acid
preparation
chitosan graft
graft object
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Pending
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CN201811140943.9A
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Chinese (zh)
Inventor
杨隽
赵启天
徐恩松
范志玮
舒何进
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Wuhan Institute of Technology
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Wuhan Institute of Technology
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Priority to CN201811140943.9A priority Critical patent/CN109248667A/en
Publication of CN109248667A publication Critical patent/CN109248667A/en
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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
    • 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
    • B01J20/264Synthetic macromolecular compounds derived from different types of monomers, e.g. linear or branched copolymers, block copolymers, graft copolymers
    • 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
    • C02F1/285Treatment of water, waste water, or sewage by sorption using synthetic organic sorbents

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Analytical Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Polysaccharides And Polysaccharide Derivatives (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

本发明公开了一种壳聚糖接枝物及其制备方法和应用。包括以下步骤:将壳聚糖溶解在酸性溶液中,然后与有机溶剂混合;加入乙二胺四乙酸二酐接枝单体(EDTAD),并在60~80℃、惰性气体保护下进行接枝聚合反应;反应结束后洗涤、烘干,得到壳聚糖接枝物。本发明所涉及的接枝反应是壳聚糖上的酰化反应,反应过程简单,易于操作。可通过改变主体和接枝单体的质量配比以及反应条件,来控制螯合吸附剂的吸附性能。可通过洗脱法将吸附剂吸附后的金属离子进行回收,吸附剂可继续投入使用,具有良好的可持续性和环保保护性。The invention discloses a chitosan graft and its preparation method and application. The method includes the following steps: dissolving chitosan in an acidic solution, and then mixing it with an organic solvent; adding ethylenediaminetetraacetic acid dianhydride grafting monomer (EDTAD), and carrying out grafting at 60-80 DEG C under the protection of inert gas Polymerization reaction; washing and drying after the reaction to obtain a chitosan graft. The grafting reaction involved in the present invention is an acylation reaction on chitosan, and the reaction process is simple and easy to operate. The adsorption performance of the chelating adsorbent can be controlled by changing the mass ratio of the main body and the grafting monomer and the reaction conditions. The metal ions adsorbed by the adsorbent can be recovered by the elution method, and the adsorbent can continue to be put into use, with good sustainability and environmental protection.

Description

A kind of chitosan graft object and its preparation method and application
Technical field
The invention belongs to field of material technology, and in particular to a kind of chitosan graft object and its preparation method and application.
Background technique
Tailing dam is dam body made of being rolled as tailing accumulation, is mainly used for storing up metal and nonmetal deposits mountain progress ore The tailing or industrial residue being discharged after sorting.Under normal circumstances, dam body height is up to tens meters or even rice up to a hundred.Tailings Dam and logical Reservoir in normal concept is different, and reservoir needs raising of water level, therefore dam body is mainly used to antiseepage, and Tailings Dam then needs to arrange infiltration, no Dam break is easy to cause after then water level is raised.There are silting ion (such as calcium ions, ferrous ion) in existing waste liquid in dam, in spy It is precipitated under fixed chemical environment, forms compound not soluble in water, blocked drainage pipe road and porous media, eventually lead to dam break. Once the Rock And Soil dam break of so people Pang can cause the disasters such as landslide, cause great casualties, property loss And environmental pollution.
The silting of tailing dam is mainly physics silting and chemical colmatage, main mainly for the processing of silting both at home and abroad at present It is carried out in the method for physics, by tailing dam simulated experiment, fluid experiment and founding mathematical models, to change this porous Jie Matter filtration system, there are applicability low (completely depending on the inner case of tailing dam), silting blocking performance are general, less economical for it The problems such as, this makes to be restricted in the application of tailing dam silting blocking.And it is seldom by the research of the method silting blocking of chemistry.
Summary of the invention
It is an object of that present invention to provide a kind of chitosan graft objects and preparation method thereof, and this method raw material and technique are more simple Single, at low cost, obtained chitosan graft object has good adsorptivity and environmental suitability as chelate sorbent, and not It will cause environmental pollution, there is good regulation effect for the silting of tailing dam.
In order to achieve the above objectives, as follows using technical solution:
A kind of chitosan graft object, has following structure formula:
The preparation method of above-mentioned chitosan graft object, comprising the following steps:
It dissolves chitosan in acid solution, is then mixed with organic solvent;
It is added ethylenediamine tetra-acetic acid dianhydride grafted monomers (EDTAD), and is connect under 60~80 DEG C, inert gas shielding Branch polymerization reaction;
It washs, dry after reaction, obtain chitosan graft object.
According to the above scheme, the acid solution is the glacial acetic acid of concentration 2wt%.
According to the above scheme, the organic solvent is n,N-Dimethylformamide.
According to the above scheme, the mass ratio of chitosan and ethylenediamine tetra-acetic acid dianhydride grafted monomers is 1:(1~4).
According to the above scheme, the ethylenediamine tetra-acetic acid dianhydride grafted monomers are prepared in the following manner:
Ethylenediamine tetra-acetic acid (EDTA) is suspended in anhydrous pyridine, anhydrous acetic acid is then added under inert gas protection Acid anhydride stirs and is warming up to 60-70 DEG C;
Cold filtration under inert gas shielding, washing, drying obtain ethylenediamine tetra-acetic acid dianhydride grafted monomers EDTAD.
According to the above scheme, ethylenediamine tetra-acetic acid, pyridine, acetic anhydride dosage molar ratio be 1:(5~7): (4~6).
Application of the above-mentioned chitosan graft object as tailing dam adsorbent.
The reaction process of the graft of ethylenediamine tetra-acetic acid dicarboxylic anhydride grafted chitosan of the present invention is as follows:
Chelate is the complex with cyclic structure, is formed by two or more ligands and same metal ion The chelation of chelate ring and obtain.The chelating mechanism of ethylenediamine tetra-acetic acid of the present invention is that it can be with many ions by four Carboxylic acid group and two nitrogen atom bondings, firmly chelate ion, form hexa-atomic chelate ring, and hexa-atomic chelate ring is very stable. Chitosan-ethylenediamine tetra-acetic acid dicarboxylic anhydride graft is exactly the chelating mechanism for using for reference EDTA, firmly chelating ion.
Compared with the existing technology, the present invention has the beneficial effect that:
The graft of ethylenediamine tetra-acetic acid dicarboxylic anhydride grafted chitosan prepared by the present invention is used as chelate sorbent Grafted monomers ethylenediamine tetra-acetic acid dicarboxylic anhydride can be voluntarily prepared (to purity without very high by raw material ethylenediamine tetra-acetic acid It is required that), this raw material is biodegradable, is easy to get extensively, and it is low in cost, and there is good environmental protection property.
Environment-friendly type chelate sorbent prepared by the present invention, react using n,N-Dimethylformamide as solvent, be grafted main body with And the low raw-material costs such as grafted monomers, be easy to get extensively, production cost can be substantially reduced.
Graft reaction according to the present invention is the acylation reaction on chitosan, and reaction process is simple, easily operated.
The present invention can be by the quality proportioning and reaction condition of change main body and grafted monomers, to control chelate sorbent Absorption property.
Metal ion after the present invention can be adsorbed adsorbent by elution method recycles, and adsorbent, which can continue investment, to be made With with good sustainability and environmentally friendly protectiveness.
Detailed description of the invention
Fig. 1: the infrared spectrogram of grafted monomers EDTA in the embodiment of the present invention 1 and 2.
Fig. 2: the ultraviolet spectrogram of calcium ion content after gained chelate and chitosan adsorb in the embodiment of the present invention 3.
Fig. 3: the ultraviolet spectrogram of calcium ion content after gained chelate and chitosan adsorb in the embodiment of the present invention 4.
Fig. 4: calcium ion adsorption capacity with grafted monomers EDTAD additional amount change curve.
Fig. 5: tailing dam internal environment adsorption capacity is simulated with the change curve of grafted monomers EDTAD additional amount.
Fig. 6: simulation tailing dam internal environment adsorption capacity changes over time curve.
Specific embodiment
Following embodiment further illustrates technical solution of the present invention, but not as limiting the scope of the invention.
Following embodiment further illustrates technical solution of the present invention, but not as limiting the scope of the invention.
Embodiment 1
The preparation of grafted monomers EDTAD, preparation step are as follows:
18gEDTA (acid) is suspended in 31ml anhydrous pyridine, 25ml acid anhydrides is then added under nitrogen protection, at 65 DEG C Lower stirring certain time.According to this by product under stable nitrogen stream cold filtration, anhydrous acetic acid acid anhydride and anhydrous second with 200ml Acid anhydrides cleaning, finally dries at 50-60 DEG C of vacuum oven, obtains grafted monomers EDTAD.The EDTAD that reaction obtains is done Infrared test.
The infared spectrum of EDTAD obtained by the present embodiment is shown in Fig. 1, in 1809cm in the infrared spectroscopy of EDTAD-1And 1765cm-1 Occur Absorption Characteristics peak and low frequency peak it is slightly stronger than high frequency peak, be acid anhydrides C=O stretching vibration absorb 2 characteristic absorption peaks this It is the characteristic peak of cyclic acid anhydride.In 1251cm-1The stretching vibration peak at place is cyclic acid anhydride C-O-C stretching vibration peak, in 1070cm-1There is C-N stretching vibration peak and 2930,2850cm-1Locate appearance-CH2Stretching vibration peak, these characteristic peaks illustrate that synthetic is EDTAD。
Embodiment 2
30gEDTA (acid) is suspended in 50m anhydrous pyridine, 50ml acid anhydrides is then added under nitrogen protection, at 65 DEG C Lower stirring certain time.According to this by product under stable nitrogen stream cold filtration, cleaned with the acid anhydrides of 200ml and ether, finally It is dried at 50-60 DEG C of vacuum oven, obtains grafted monomers EDTAD.The EDTAD that reaction obtains is done into infrared test.
The infared spectrum of EDTAD obtained by the present embodiment is shown in Fig. 1, in 1796cm in the infrared spectroscopy of EDTAD-1And 1749cm-1 Occur Absorption Characteristics peak and low frequency peak it is slightly stronger than high frequency peak, be acid anhydrides C=O stretching vibration absorb 2 characteristic absorption peaks this It is the characteristic peak of cyclic acid anhydride.In 1252cm-1The stretching vibration peak at place is cyclic acid anhydride C-O-C stretching vibration peak, in 1060cm-1There is C-N stretching vibration peak and 2923cm-1Locate appearance-CH2Stretching vibration peak, these characteristic peaks illustrate that synthetic is EDTAD.
Embodiment 3
1g chitosan monomer is completely dissolved with 2ml glacial acetic acid, after a certain period of time, 50mlN, N- is added in solution upon dissolution In dimethylformamide, 1 gained EDTAD grafted monomers of 1g embodiment are added, and carry out at 65 DEG C, under nitrogen closing environment Polymerization reaction until the reaction is complete, uses 50mlN after reaction, and dinethylformamide is washed and filtered, then steamed with 100ml Distilled water washing is centrifuged, and is then washed and is centrifuged with 100ml saturated sodium bicarbonate solution, then distills water washing with 100ml It is centrifuged, is finally centrifuged with the ethanol washing of 50ml 95%, placed it at 70 DEG C of vacuum oven and dry, obtain Chitosan graft object of the present invention.
Obtained chitosan graft object, which is placed in the calcium solution of configuration, adsorbs 2h, and the solution after absorption is carried out ultraviolet survey Examination;It is compared simultaneously with the ultraviolet spectrogram of solution after chitosan absorption, as shown in Figure 2, respectively chitosan (Chitosan) and after chitosan graft object (Graft copolymer) absorption ionic calcium soln in solution calcium ion content purple External spectrum figure, the calcium ion solubility after graft absorption in solution are considerably less than the calcium ion solubility after chitosan absorption, the two Peak of curve illustrates that the absorption property of graft is significantly better than the absorption property of chitosan there are significant difference.
Embodiment 4
1g chitosan monomer is completely dissolved with 2ml glacial acetic acid, after a certain period of time, 50mlN, N- is added in solution upon dissolution In dimethylformamide, add 1 gained EDTAD grafted monomers of 2.5g embodiment, and at 65 DEG C, under nitrogen closing environment into Row polymerization reaction until the reaction is complete, uses 50mlN after reaction, and dinethylformamide is washed and filtered, and then uses 100ml Distillation water washing is centrifuged, and is then washed and is centrifuged with 100ml saturated sodium bicarbonate solution, then is distilled and washed with 100ml It washs and is centrifuged, is finally centrifuged with the ethanol washing of 50ml 95%, place it at 60~80 DEG C of vacuum oven and dry It is dry, obtain chitosan graft object of the present invention.
Obtained chitosan graft object is placed in configured calcium solution (by pH value adjustment to 7.2) and adsorbs 2h, will Solution after absorption carries out ultraviolet test, while comparing with the ultraviolet spectrogram of the solution after chitosan absorption.See Fig. 3 institute Show that chitosan (Chitosan) and chitosan graft object (Graft copolymer) absorption PH are molten after 7.2 ionic calcium soln The ultraviolet spectrogram of liquid;Ionic calcium soln after adjustment PH does not influence the absorption property of graft significantly, graft Absorption property of the absorption property still better than chitosan.
In addition, adsorption capacity as shown in Figure 4 is with grafted monomers with EDTA complexometric titration to calcium ion adsorption capacity The change curve of EDTAD additional amount.
With the variation of the addition quality of grafted monomers EDTAD (ethylenediamine tetra-acetic acid dianhydride), the suction of chitosan graft object Attached capacity significantly improves.This change curve shows to change the matter of chitosan and grafted monomers EDTAD (ethylenediamine tetra-acetic acid dianhydride) Amount proportion can effectively improve graft to the adsorption effect of calcium ion, promote the absorption property of chelate sorbent.
In the case where simulation tailing dam internal environment pH is 6.5--7.8, adsorption time 8h, with grafted monomers EDTAD's The variation of quality is added, the change curve of adsorption capacity is as shown in Figure 5.With the increase of grafted monomers quality, the suction of graft Attached capacity also improves.Find out that the absorption property in tailing dam of graft can be improved in control proportion by curve.
In the case where simulating tailing dam internal environment pH6.5--7.8, the quality of grafted monomers used is 2g, and adsorption capacity is at any time Between change it is as shown in Figure 6.By shown in curve, with the variation of time, the adsorption capacity of graft is improved.Illustrate to increase at any time Add, the absorption property of graft is better in tailing dam, but may eventually reach the maximum value of adsorption capacity, and last curve can become In steady.

Claims (8)

1. a kind of chitosan graft object, it is characterised in that have following structure formula:
2. the preparation method of chitosan graft object described in claim 1, it is characterised in that the following steps are included:
It dissolves chitosan in acid solution, is then mixed with organic solvent;
It is added ethylenediamine tetra-acetic acid dianhydride grafted monomers (EDTAD), and carries out grafting under 60~80 DEG C, inert gas shielding and gather Close reaction;
It washs, dry after reaction, obtain chitosan graft object.
3. the preparation method of chitosan graft object as claimed in claim 2, it is characterised in that the acid solution is concentration 2wt% Glacial acetic acid.
4. the preparation method of chitosan graft object as claimed in claim 2, it is characterised in that the organic solvent is N, N- bis- Methylformamide.
5. the preparation method of chitosan graft object as claimed in claim 2, it is characterised in that chitosan and ethylenediamine tetra-acetic acid two The mass ratio of acid anhydride grafted monomers is 1:(1~4).
6. the preparation method of chitosan graft object as claimed in claim 2, it is characterised in that the ethylenediamine tetra-acetic acid dianhydride connects Branch monomer is prepared in the following manner:
Ethylenediamine tetra-acetic acid (EDTA) is suspended in anhydrous pyridine, anhydrous acetic acid acid anhydride is then added under inert gas protection, It stirs and is warming up to 60-70 DEG C;
Cold filtration under inert gas shielding, washing, drying obtain ethylenediamine tetra-acetic acid dianhydride grafted monomers EDTAD.
7. the preparation method of chitosan graft object as claimed in claim 6, it is characterised in that ethylenediamine tetra-acetic acid, pyridine, acetic acid The dosage molar ratio of acid anhydride is 1:(5~7): (4~6).
8. application of the chitosan graft object as tailing dam adsorbent described in claim 1.
CN201811140943.9A 2018-09-28 2018-09-28 A kind of chitosan graft object and its preparation method and application Pending CN109248667A (en)

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Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108993454A (en) * 2018-09-28 2018-12-14 武汉工程大学 A kind of preparation method of chelate sorbent
CN110003356A (en) * 2019-04-12 2019-07-12 南京理工大学 Thermal gels-EDTA derivative and preparation method and the application in adsorption of metal ions
CN110639478A (en) * 2019-10-30 2020-01-03 武汉工程大学 Preparation method of modified chitosan cross-linked zeolite adsorbent
CN110665474A (en) * 2019-10-30 2020-01-10 武汉工程大学 Modified chitosan cross-linked zeolite porous adsorbent and application thereof
CN110724596A (en) * 2019-10-10 2020-01-24 浙江海洋大学 A method for removing arsenic from Antarctic krill oil
CN110975824A (en) * 2019-12-23 2020-04-10 徐州工程学院 Water body heavy metal ion adsorbent and preparation method and application thereof
CN114096576A (en) * 2019-07-12 2022-02-25 陶氏环球技术有限责任公司 Metal Polyols for Polyurethane Polymers
CN116239853A (en) * 2023-02-28 2023-06-09 宁波方太厨具有限公司 Preparation method of composite nano microsphere and application of composite nano microsphere in preparation of nanofiber membrane

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CN102849817A (en) * 2012-08-24 2013-01-02 武汉工程大学 Method for separating heavy metals lead and cadmium by using biological adsorbent packed column
CN104745198A (en) * 2015-02-12 2015-07-01 上海贯发海洋生物科技有限公司 Preparation method of soil heavy metal curing detoxicant
CN105854934A (en) * 2016-03-31 2016-08-17 天津大学 Preparation and application of green environment-friendly immobilized platinum catalyst
CN106220871A (en) * 2016-07-29 2016-12-14 清华大学 A kind of modification of chitosan gel micro-ball and preparation thereof and application
CN108993454A (en) * 2018-09-28 2018-12-14 武汉工程大学 A kind of preparation method of chelate sorbent

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Publication number Priority date Publication date Assignee Title
EP2164591A1 (en) * 2007-07-09 2010-03-24 GE Healthcare Bio-Sciences AB Method for preparation of a biomolecule adsorbent
CN102849817A (en) * 2012-08-24 2013-01-02 武汉工程大学 Method for separating heavy metals lead and cadmium by using biological adsorbent packed column
CN104745198A (en) * 2015-02-12 2015-07-01 上海贯发海洋生物科技有限公司 Preparation method of soil heavy metal curing detoxicant
CN105854934A (en) * 2016-03-31 2016-08-17 天津大学 Preparation and application of green environment-friendly immobilized platinum catalyst
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Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108993454A (en) * 2018-09-28 2018-12-14 武汉工程大学 A kind of preparation method of chelate sorbent
CN110003356A (en) * 2019-04-12 2019-07-12 南京理工大学 Thermal gels-EDTA derivative and preparation method and the application in adsorption of metal ions
CN114096576A (en) * 2019-07-12 2022-02-25 陶氏环球技术有限责任公司 Metal Polyols for Polyurethane Polymers
CN114096576B (en) * 2019-07-12 2024-11-29 陶氏环球技术有限责任公司 Metal polyols for polyurethane polymers
CN110724596A (en) * 2019-10-10 2020-01-24 浙江海洋大学 A method for removing arsenic from Antarctic krill oil
CN110639478A (en) * 2019-10-30 2020-01-03 武汉工程大学 Preparation method of modified chitosan cross-linked zeolite adsorbent
CN110665474A (en) * 2019-10-30 2020-01-10 武汉工程大学 Modified chitosan cross-linked zeolite porous adsorbent and application thereof
CN110975824A (en) * 2019-12-23 2020-04-10 徐州工程学院 Water body heavy metal ion adsorbent and preparation method and application thereof
CN110975824B (en) * 2019-12-23 2022-11-29 徐州工程学院 A kind of water heavy metal ion adsorbent and its preparation method and application
CN116239853A (en) * 2023-02-28 2023-06-09 宁波方太厨具有限公司 Preparation method of composite nano microsphere and application of composite nano microsphere in preparation of nanofiber membrane

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Application publication date: 20190122