CN109400720A - A kind of preparation method and application of amphoteric cellulose adsorbent - Google Patents

A kind of preparation method and application of amphoteric cellulose adsorbent Download PDF

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Publication number
CN109400720A
CN109400720A CN201811231679.XA CN201811231679A CN109400720A CN 109400720 A CN109400720 A CN 109400720A CN 201811231679 A CN201811231679 A CN 201811231679A CN 109400720 A CN109400720 A CN 109400720A
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cellulose
adsorbent
preparation
amphoteric
bis
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杜宏涛
马芳
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Xinyang Normal University
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Xinyang Normal University
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    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08BPOLYSACCHARIDES; DERIVATIVES THEREOF
    • C08B15/00Preparation of other cellulose derivatives or modified cellulose, e.g. complexes
    • C08B15/05Derivatives containing elements other than carbon, hydrogen, oxygen, halogens or sulfur
    • C08B15/06Derivatives containing elements other than carbon, hydrogen, oxygen, halogens or sulfur containing nitrogen, e.g. carbamates
    • 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
    • B01J20/265Synthetic macromolecular compounds modified or post-treated polymers
    • 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
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28014Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their form
    • B01J20/28023Fibres or filaments
    • 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
    • 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
    • C02F2101/103Arsenic compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds

Abstract

The present invention relates to a kind of preparation methods of amphoteric cellulose adsorbent, and cellulose is added in sodium hydroxide-aqueous solution of urea first, obtains cellulose suspension after mixing evenly;Then it thaws, is uniformly mixed again after being freezed, obtain cellulose solution;Cellulose solution is centrifuged, take supernatant, bis- (2- acetate) amine derivative aqueous solutions, bis- (pyridine ethyl) amine derivative aqueous solutions are successively added dropwise into supernatant, after being stirred to react 2-12h at a temperature of 50-100 DEG C, obtain reaction product, reaction product is successively washed with deionized water, acetone, ether, then filter, it is dry to get.What the amphoteric cellulose adsorbent material surface of the method for the present invention preparation connected is the ionic groups of " pincer " structure, this is more than the active group of single-stranded ionic group modified cellulose, suction-operated is stronger, and the method for the present invention reaction step is few, reaction condition is mild, it is easy to operate, it is conducive to large-scale production.

Description

A kind of preparation method and application of amphoteric cellulose adsorbent
Technical field
The invention belongs to technical field of function materials, and in particular to a kind of preparation method of amphoteric cellulose adsorbent and its Application as water body purification adsorbent material.
Background technique
With the rapid development of sharp increase and the industry of population, water environment pollution has become a serious problem, especially It is that heavy metal pollution is particularly acute.Since heavy metal ion is difficult to degrade, can accumulate in vivo, can be transmitted by biological chain, So heavy metal ion pollution has seriously threatened aquatic ecosystem and other biological system and human life's safety.
Absorption method because the advantages that equipment is simple, operating cost is low, high treating effect always wastewater treatment research hot spot, Therefore, efficient, cheap, environmental-friendly adsorbent is developed to be concerned.Cellulose as a kind of abundance, it is cheap, Asepsis environment-protecting, good biocompatibility and can be degradable natural material, be used for sewage water process with huge economy And social value.Since hydrogen bond action is more in cellulosic molecule, cause its absorption property not strong, so many scholars are to fiber It is modified.Wherein amphoteric cellulose is that a kind of a kind of water cellulose element simultaneously containing cation and anionic group is derivative Object can simultaneously adsorb negatively charged and positively charged pollutant, and adsorption efficiency is high.This kind of material sewage treatment, The fields such as oilfield exploitation, daily-use chemical industry have broad application prospects.
About amphoteric cellulose preparation method, there are also the reports of document in recent years, such as: hear seapeak to absorbent cotton according to It is secondary to be alkalized, carboxy methylation, quaternized obtain amphoteric cellulose;(shaddock ped cellulose prepares both sexes heavy metal ion to Fu Weichang Remover and its application in Electrolytic Manganese Wastewater processing, Hunan University .2002) with epoxychloropropane, dimethylamine and monoxone As ionization reagent, cotton fiber and shaddock ped fiber are modified, betaine type amphoteric ion fiber element adsorbent is made;Clock Pretty (development of wheat straw amphoteric chelate sorbent containing and the Study on adsorption properties [D] to Cu (II) and Cr (VI), Shandong University .2011) with N, N- dimethyl methyl acid amide is medium, and the amination using wheat straw waste and epoxychloropropane, ethylenediamine, triethylamine is anti- It answers, obtains cationic wheat straw quaternary amine adsorbent;Then using isopropanol as solvent, monoxone is ionization reagent, and wheat is made Careless amphoteric ion adsorbent WSAA;Have scholar (Zhang, W., et al., Carbohydrate Polymers.2012 90 (2), 887-893.) using epoxychloropropane, trimethylamine and monoxone be ionization reagent, fiber is modified, be made both sexes from Subbundle element adsorbent.However the amphoteric cellulose of above-mentioned report, ionic groups are that single-stranded form is linked to fiber Surface, therefore, the adsorption active site of gained amphoteric fibers cellulosic material is relatively fewer, thus affect to heavy metal from The removal effect of son.
Summary of the invention
The object of the present invention is to provide a kind of preparation method and applications of amphoteric cellulose adsorbent, to solve the prior art Ionic group is that amphoteric cellulose caused by the surface of fiber is linked in single-stranded form to the removal effect of heavy metal The problem of difference.
The principle of the present invention:
The technical solution adopted in the present invention is as follows:
A kind of preparation method of amphoteric cellulose adsorbent, includes the following steps:
(1) cellulose is added in sodium hydroxide-aqueous solution of urea, obtains cellulose suspension after mixing evenly;
(2) it thaws again after freezing the cellulose suspension of step (1), is then uniformly mixed, it is molten to obtain cellulose Liquid;
(3) cellulose solution of step (2) is centrifuged, takes supernatant, bis- (2- acetate) amine are successively added dropwise into supernatant and spread out The aqueous solution of biology and the aqueous solution of bis- (pyridine ethyl) amine derivatives obtain after being stirred to react 2-12h at a temperature of 50-100 DEG C To reaction product, reaction product is successively washed with deionized water, acetone, ether, then filters, is dry, obtained product is i.e. For amphoteric cellulose adsorbent.
In step (1), the cellulose is microcrystalline cellulose or gossypin.
Further, in step (1), in the sodium hydroxide-aqueous solution of urea, sodium hydroxide, urea, deionized water weight Amount is than being 20:10:170.
Further, in step (1), speed of agitator 2000rpm, time 10min.
Further, in step (2), cryogenic temperature is -20 DEG C, and the time is for 24 hours.
Further, in step (2), speed of agitator 1000rpm.
Further, in step (3), centrifugal rotational speed 5000rpm.
Further, in step (3), the dosage of bis- (2- acetate) amine derivatives and bis- (pyridine ethyl) amine derivatives is 0.1-2 times of cellulose quality.
Further, in step (3), bis- (2- acetate) amine derivatives are bis- ((3- chlorine-2-hydroxyl) 2- acetates) Propylamine.
Further, in step (3), bis- (pyridine ethyl) amine derivatives are bis- ((3- chlorine-2-hydroxyl) pyridine ethyls) Propylamin hydrochloride.
The beneficial effects of the present invention are: the present invention provides a kind of " one kettle way " preparations to have the both sexes of " pincer " structure fine The method for tieing up plain adsorbent, the amphoteric cellulose adsorbent material surface connection of the method for the present invention preparation be " pincer " structure from Subtype group, this is more than the active group of single-stranded ionic group modified cellulose, and suction-operated is stronger, and side of the present invention Method reaction step is few, and reaction condition is mild, easy to operate, is conducive to large-scale production.
Detailed description of the invention
Fig. 1 is the infared spectrum of amphoteric cellulose adsorbent made from embodiment 1.
Specific embodiment
The following describes the present invention in detail with reference to the accompanying drawings and specific embodiments.
Embodiment 1
A kind of preparation method of amphoteric cellulose adsorbent, includes the following steps:
(1) it weighs 20.0g NaOH and 10g urea and is added in 170g deionized water and dissolve, obtain sodium hydroxide-urea 5g microcrystalline cellulose is added in sodium hydroxide-aqueous solution of urea by aqueous solution, and 2000rpm stirs 10min, obtains cellulose Suspension;
(2) it will thaw again, then stirred at 1000rpm mixed after -20 DEG C of cellulose suspension freezings for 24 hours of step (1) It closes uniformly, obtains cellulose solution;
(3) cellulose solution of step (2) is centrifuged 30min under conditions of 5000rpm, takes supernatant, into supernatant according to Secondary aqueous solution, bis- ((3- chlorine-2-hydroxyl) pyridine ethyls) containing 5g that bis- ((3- chlorine-2-hydroxyl) 2- acetate) propylamine Han 5g are added dropwise The aqueous solution of propylamin hydrochloride, 100 DEG C at a temperature of be stirred to react 12h after, obtain reaction product, reaction product successively used 200mL deionized water, acetone, ether washing, then filter, are dried in vacuo 48h at room temperature, obtained product is amphoteric fibers Plain adsorbent.
Structural characterization is carried out using amphoteric cellulose adsorbent of the infrared spectrum to embodiment 1, as a result as shown in Figure 1.Figure In, 3428cm-1Neighbouring width and strong absorption peak are the stretching vibration peaks of-OH;2920cm-1The peak of left and right is-CH2Asymmetry Stretching vibration peak;1632cm-1Neighbouring peak may be C=C stretching vibration peak or the flexural vibrations peak for adsorbing water;1031cm-1Place Peak be to be generated by the asymmetric stretching vibration of C-O-C;1589cm-1And 1412cm-1Belong to carboxylic acid sodium (- COO-) asymmetry Stretching vibration peak and symmetrical stretching vibration peak.1562cm-1And 1360cm-1Belong to the stretching vibration peak of C=N and C-N.
Embodiment 2
A kind of preparation method of amphoteric cellulose adsorbent, includes the following steps:
(1) it weighs 20.0g NaOH and 10g urea and is added in 170g deionized water and dissolve, obtain sodium hydroxide-urea 3g gossypin is added in sodium hydroxide-aqueous solution of urea by aqueous solution, and 2000rpm stirs 10min, and it is outstanding to obtain cellulose Supernatant liquid;
(2) it will thaw again, then stirred at 1000rpm mixed after -20 DEG C of cellulose suspension freezings for 24 hours of step (1) It closes uniformly, obtains cellulose solution;
(3) cellulose solution of step (2) is centrifuged 15min under conditions of 5000rpm, takes supernatant, into supernatant according to The secondary aqueous solution that bis- ((3- chlorine-2-hydroxyl) 2- acetate) propylamine Han 1g are added dropwise, bis- ((3- chlorine-2-hydroxyl) pyridine second containing 0.8g Base) propylamin hydrochloride aqueous solution, 80 DEG C at a temperature of be stirred to react 9h after, obtain reaction product, successively by reaction product It is washed with 200mL deionized water, acetone, ether, then filters, is dried in vacuo 48h at room temperature, obtained product is both sexes fibre Tie up plain adsorbent.
Comparative example 1
A kind of amphoteric cellulose, the preparation method comprises the following steps: by the sodium hydrate aqueous solution of cotton fiber immersion 17.5%, stirring 1h, static soak for 24 hours, are washed with water to neutrality after taking-up, filter, 45 DEG C of baking 6h, and alkali fiber is made.Weigh above-mentioned alkali fiber 5g It is put into conical flask, 75mL ethyl alcohol is added, stir 5min, 20% sodium hydrate aqueous solution 50mL is added, is placed in 45 DEG C of water It bathes in constant temperature oscillator, rises to 45 DEG C to mixed solution temperature in conical flask, the chloroethene aqueous acid 25mL of 5mol/L is added dropwise, Cyclotron oscillation frequency is 100 times/min, reacts 45min, takes out solid content, is used again after being washed with 95% ethyl alcohol of 300mL point 3 times Distillation washing 3 times filters, carboxymethyl cellulose (CMC) is made in 45 DEG C of baking 6h.It weighs CMC 1.6g to be put into conical flask, be added 60mL isopropanol stirs 5min, the 4% chloro- 2- Hydroxyproyl Trimethyl chlorination of sodium hydrate aqueous solution 12mL and 50%3- is added dropwise Aqueous ammonium 6.0mL reacts 4h at 45 DEG C, and product is washed with water 2 times, then uses again after being washed with 95% ethyl alcohol of 300mL point 3 times Distillation washing 3 times filters, amphoteric cellulose is made in 45 DEG C of baking 6h.
Comparative example 2
A kind of cation-modified cellulose, preparation method: PAN precursor is fixed on sample frame, hot in 250 DEG C of baking ovens 30min is handled, is made PAN pre-oxidized fibers (PANS fiber).PANS fiber uses dense sulfuric acid treatment 2h at room temperature, then spend from Sub- water impregnates, until solution is neutrality, takes out and dries at 105 DEG C, obtains modified PAN fiber (SA-PANS fiber).
Comparative example 3
A kind of anion-modified cellulose, preparation method:
0.5g cellulose fibre is placed in 42mL and contains 0.69mol/L nitric acid, 4.34 × 10-2The water of mol/L ammonium ceric nitrate Stirring, makes it be uniformly dispersed after in solution.System is led into N23mL Dimethylaminoethyl Methacrylate is added in 0.5h (DMAEMA), continue logical N210min, closed system are transferred in 50 DEG C of water-baths and react 3h.After reaction terminates, wash repeatedly Reaction product, vacuum drying, obtains the cellulose base adsorbent material for arsenic removal in water.
Performance test:
Embodiment 1 and 2 amphoteric cellulose adsorbent of embodiment are used to simulate the suction of heavy metal ion Pb (II) and As (V) It is attached, while being compared with the cellulose adsorbent in comparative example 1-3, it the results are shown in Table 1.
Specific experiment method:
Take 200mg L-1Pb (II) solution 20mL, be added in the triangular flask of 50mL, adjust pH to 5.0, be then added 0.5–3g L-1Adsorbent, at room temperature adsorb 12 hours, after filtering measure solution in residue Pb (II) content, calculate suction Attached amount.
Take 20mg L-1As (V) solution 20mL, be added in the triangular flask of 50mL, adjust pH to 1.0 ± 0.1, then plus Enter 0.5-3g L-1Adsorbent, adsorb 12h at room temperature, after filtering measure solution in residue As (V) content, calculate adsorb Amount and.
The different adsorbents of table 1 compare the maximal absorptive capacity qmax of Pb (II) and As (V)
From result above as it can be seen that compared with microcrystalline cellulose and modified cellulose reported in the literature, two prepared by the present invention Property cellulose adsorbent ion pair Pb (II) and As (V) show stronger adsorption capacity, illustrate that the present invention is prepared into suction Attached dose can be used as a kind of adsorbent material of good performance to handle the heavy metal cation and anion in waste water.

Claims (10)

1. a kind of preparation method of amphoteric cellulose adsorbent, which comprises the steps of:
(1) cellulose is added in sodium hydroxide-aqueous solution of urea, obtains cellulose suspension after mixing evenly;
(2) it thaws again after freezing the cellulose suspension of step (1), is then uniformly mixed, obtains cellulose solution;
(3) cellulose solution of step (2) is centrifuged, takes supernatant, bis- (2- acetate) amine derivatives are successively added dropwise into supernatant Aqueous solution, bis- (pyridine ethyl) amine derivative aqueous solutions after being stirred to react 2-12h at a temperature of 50-100 DEG C, obtain reaction and produce Object successively washs reaction product with deionized water, acetone, ether, then filters, is dry, and obtained product is both sexes fibre Tie up plain adsorbent;
In step (1), the cellulose is microcrystalline cellulose or gossypin.
2. the preparation method of amphoteric cellulose adsorbent as described in claim 1, which is characterized in that in step (1), the hydrogen-oxygen Change sodium-aqueous solution of urea in, sodium hydroxide, urea, deionized water weight ratio be 20:10:170.
3. the preparation method of amphoteric cellulose adsorbent as described in claim 1, which is characterized in that in step (1), speed of agitator For 2000rpm, time 10min.
4. the preparation method of amphoteric cellulose adsorbent as described in claim 1, which is characterized in that in step (2), cryogenic temperature It is -20 DEG C, the time is for 24 hours.
5. the preparation method of amphoteric cellulose adsorbent as described in claim 1, which is characterized in that in step (2), speed of agitator For 1000rpm.
6. the preparation method of amphoteric cellulose adsorbent as described in claim 1, which is characterized in that in step (3), centrifugal rotational speed For 5000rpm.
7. the preparation method of amphoteric cellulose adsorbent as described in claim 1, which is characterized in that in step (3), bis- (2- second Acidic group) dosages of amine derivative and bis- (pyridine ethyl) amine derivatives is 0.1-2 times of cellulose quality.
8. the preparation method of amphoteric cellulose adsorbent as described in claim 1, which is characterized in that described double in step (3) (2- acetate) amine derivative is bis- ((3- chlorine-2-hydroxyl) 2- acetate) propylamine.
9. the preparation method of amphoteric cellulose adsorbent as described in any one of claim 1 to 8, which is characterized in that step (3) In, in step (3), bis- (pyridine ethyl) amine derivatives are bis- ((3- chlorine-2-hydroxyl) pyridine ethyl) propylamin hydrochlorides.
10. application of the amphoteric cellulose adsorbent as water body purification adsorbent material made from claim 1-9 the method.
CN201811231679.XA 2018-10-22 2018-10-22 A kind of preparation method and application of amphoteric cellulose adsorbent Withdrawn CN109400720A (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111214391A (en) * 2019-11-25 2020-06-02 重庆东寰科技开发有限公司 Amphoteric hydroxyethyl cellulose ether and preparation method thereof
CN113842894A (en) * 2021-10-04 2021-12-28 桂林理工大学 Preparation method and application of microcrystalline cellulose betaine ester adsorbent
CN114835826A (en) * 2022-04-22 2022-08-02 深圳华源再生医学有限公司 Zwitterionic cellulose and preparation method and application thereof

Citations (1)

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Publication number Priority date Publication date Assignee Title
CN102626608A (en) * 2012-04-16 2012-08-08 南京大学 Straw modified into amphiprotic adsorbent and preparation method thereof

Patent Citations (1)

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Publication number Priority date Publication date Assignee Title
CN102626608A (en) * 2012-04-16 2012-08-08 南京大学 Straw modified into amphiprotic adsorbent and preparation method thereof

Non-Patent Citations (1)

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Title
马芳: ""小麦秸秆及其纤维素的改性与吸附水体中Pb(II)和As(V)的机理研究"", 《中国博士学位论文全文数据库 工程科技I辑》 *

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111214391A (en) * 2019-11-25 2020-06-02 重庆东寰科技开发有限公司 Amphoteric hydroxyethyl cellulose ether and preparation method thereof
CN111214391B (en) * 2019-11-25 2023-04-14 重庆东寰科技开发有限公司 Amphoteric hydroxyethyl cellulose ether and preparation method thereof
CN113842894A (en) * 2021-10-04 2021-12-28 桂林理工大学 Preparation method and application of microcrystalline cellulose betaine ester adsorbent
CN114835826A (en) * 2022-04-22 2022-08-02 深圳华源再生医学有限公司 Zwitterionic cellulose and preparation method and application thereof
CN114835826B (en) * 2022-04-22 2023-08-22 深圳华源再生医学有限公司 Zwitterionic cellulose and preparation method and application thereof

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Application publication date: 20190301