CN107552008A - A kind of method of corn cob fiber element based aquagel absorption heavy metal ion - Google Patents

A kind of method of corn cob fiber element based aquagel absorption heavy metal ion Download PDF

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CN107552008A
CN107552008A CN201710817499.9A CN201710817499A CN107552008A CN 107552008 A CN107552008 A CN 107552008A CN 201710817499 A CN201710817499 A CN 201710817499A CN 107552008 A CN107552008 A CN 107552008A
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corn cob
fiber element
cob fiber
mass ratio
element based
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CN107552008B (en
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杨桂花
陈嘉川
吉兴香
周慧芳
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Qilu University of Technology
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Qilu University of Technology
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Abstract

The invention discloses a kind of method of corn cob fiber element based aquagel absorption heavy metal ion.First corn cob fiber element is dissolved,Add montmorillonite heating stirring,Make in corn cob fiber element insertion montmorillonite layer,Add tetramethylethylenediamine and ammonium persulfate stirring,Then acrylic acid and N.N ' methylene-bisacrylamides are added,Continue heating stirring and obtain hydrogel,The corn cob fiber element is the pure cellulose extracted using nitric acid Ethanol Method from corncob,By to montmorillonite,N.N ' methylene-bisacrylamides,The optimization of the dosage of acrylic acid has obtained structure,The optimal corn cob fiber element based aquagel of absorption property,Lay equal stress on metal ion solution various concentrations,The optimization of pH value and adsorption time,Confirm the optimal adsorption condition of hydrogel heavy metal ion of the present invention,Preparation method technique of the present invention is simple,The hydrogel absorption property and structural stability of preparation are preferable,The advantages of good adsorption effect of heavy metal ion.

Description

A kind of method of corn cob fiber element based aquagel absorption heavy metal ion
Technical field
The present invention relates to corn cob fiber element based aquagel heavy metal ion (Zn2+, Cd2+And Cr3+) absorption property shadow Ring, the hydrogel that more particularly to prepared by nitric acid-ethanol corn core cellulose is under the conditions of Different Optimization to Zn2+, Cd2+And Cr3+Weight The absorption of metal ion.
Technical background
Corn cob fiber element (LNC) is a kind of rich reserves, reproducible natural macromolecular material, has good biology Degradability, avirulent feature, it is native grass fiber element, lignin and hemicellulose are compared with other wood in preparation process Matter cellulose is easier to remove.Utilize the hydrogel that reproducible corn cob fiber element Development and Production is degradable, it is possible to achieve its profit With the maximization of value.Hydroxyl in corn cob fiber element macromolecular, the reaction such as carboxylation, acidifying can be participated in, in corn cob fiber Various active groups, such as carbonyl, carboxyl are introduced on element, various derivatives can be formed.Because of corn cob fiber element table Face space is larger, has very strong hydrophobicity and water imbibition, and the high-specific surface area that corn cob fiber element has is advantageous to prepare water Gel.
In recent years, the heavy metal such as problem of environmental pollution such as cadmium, lead, nickel, zinc, chromium had caused worldwide extensive concern. Different from organic waste, heavy metal contaminants have the characteristics that strong toxicity, difficult degradation, are easily enriched with, and can be entered by food chain Enter human body, so as to endanger human health.Therefore, heavy metal pollutant prevention and control turn into research emphasis.Tradition The method for removing metal ion in the aqueous solution has chemical precipitation method, ion-exchange, chemical oxidation/reduction, counter-infiltration, electric osmose Analysis, ultrafiltration etc..However, traditional coagulation, chemical precipitation produce substantial amounts of waste residue, secondary pollution is easily caused;Electrolysis and ion are handed over High energy consumption is changed, cost is high.And the adsorbent advantage such as have strong adsorptivity, simple to operate, small investment, secondary pollution small, therefore, need Constantly to seek more cheap, efficient, environmental protection the adsorbent of exploitation to improve the removal effect of heavy metal ion in the aqueous solution.
Prior art (mono- acrylic acid of g of lignocellulosic one/montmorillonite hydrogel prepares and Study on adsorption properties) discloses A kind of preparation method of mono- acrylic acid of g of lignocellulosic one/montmorillonite hydrogel and its methylene is adsorbed in sewage disposal The effect of blue dyestuff.Lignocellulosic includes cellulose, hemicellulose and lignin, and structure is more complicated, and functional group is more multiple It is miscellaneous, and hemicellulose easily hydrolyzes in an acidic solution, lignin can also hydrolyze in an acidic solution, and prepared by lignocellulosic During need to handle by high temeperature chemistry, process is numerous and diverse, and the structure and performance to cellulose cause necessarily to adversely affect.It is existing Technology needs the degree of neutralization with sodium hydroxide regulation acrylic acid when preparing hydrogel, influences the suction of hydrogel in acid condition Attached effect.
The content of the invention
In order to solve traditional plant fiber-based heavy metal absorbent exist adsorption capacity is low, the rate of adsorption is slow, structure not The problems such as stable and adsorption capacity difference, improves the absorption property of hydrogel, improves the adsorption effect of hydrogel heavy metal ion, The present invention provides a kind of novel corn core cellulose base montmorillonite and is modified hydrogel.
An object of the present invention is to provide a kind of corn cob fiber element based aquagel, the hydrogel structure is stable, Adsorption capacity is high, the rate of adsorption is fast, recyclability is good and selective adsorption capacity is strong.
The second object of the present invention is to provide a kind of preparation method of corn cob fiber element based aquagel, the preparation side Method can simply, easily obtain corn cob fiber element based aquagel, be easy to use.
The third object of the present invention is to provide a kind of application of corn cob fiber element based aquagel absorption heavy metal ion Method, the application process method can determine optimal adsorption condition and maximal absorptive capacity.
To realize above-mentioned technical purpose, specifically, the present invention relates to following technical scheme:
The invention discloses a kind of corn cob fiber element based aquagel preparation method, comprise the following steps:
(1) weigh appropriate corn cob fiber plain (LNC) to be put into three-necked flask, after adding distilled water to dissolve;
(2) montmorillonite (MMT) is added into step (1) resulting solution, in inert gas N2The lower heating stirring of protection;
(3) tetramethylethylenediamine and ammonium persulfate are added into mixing liquid obtained by step (2), is stirring evenly and then adding into third Olefin(e) acid (AA) and N.N '-methylene-bisacrylamide (MBA) continue heating stirring and obtain hydrogel;
(4) gained hydrogel is added into absolute ethyl alcohol to stand, is cleaned, dried with deionized water.
Preferably, a kind of preparation method of corn cob fiber element based aquagel, comprises the following steps:
(1) weigh appropriate corn cob fiber element to be put into three-necked flask, after adding distilled water to dissolve;
(2) MMT is added into step (1) resulting solution, wherein MMT/LNC mass ratioes are 0.03-0.11, in N2Under protection Heating stirring, heating-up temperature are 75-90 DEG C, whipping temp 50-70min;
(3) tetramethylethylenediamine (tetramethylethylenediamine/LNC volume/mass is added into mixing liquid obtained by step (2) Than for 0.2mL/g) and ammonium persulfate (ammonium persulfate/LNC mass ratioes are 0.2), it is stirring evenly and then adding into AA (AA/LNC quality Than for 8-24) and MBA (MBA/LNC mass ratio is 0.1-0.5) continue heating stirring and obtain hydrogel;
(4) gained hydrogel is added into absolute ethyl alcohol and stands 24h, cleaned with deionized water, 24h is dried at 50-70 DEG C.
Preferably, MMT/LNC mass ratioes are 0.08.
Preferably, AA/LNC mass ratioes are 16.
Preferably, MBA/LNC mass ratioes are 0.2.
The present invention also provides a kind of preparation method of above-mentioned corn cob fiber element, comprises the following steps:
(1) weigh a certain amount of corncob to be put into conical flask, add the mixed solution of nitric acid and ethanol (95%), water-bath adds Heat is reacted;
(2) it is transferred to step (1) is residue obtained in G2 glass filters, pumps filtrate, above procedure is repeated 2 times;
(3) filtration product obtained by step (2) is finally moved into baking oven, is dried to constant weight.
Preferably, the mass ratio of nitric acid and ethanol (95%) is 1 in step (1):4.
Preferably, water-bath reaction temperature is 75-90 DEG C in step (1), reaction time 1h.
Preferably, drying temperature is 100-120 DEG C in step (3).
Present invention also offers a kind of application process of corn cob fiber element based aquagel absorption heavy metal ion, including:
Corn cob fiber element based aquagel prepared by the method for the invention is added to pH=3.5-6.5, Zn2+, Cd2+ And Cr3+Ion concentration is is adsorbed in the heavy metal solution of (50-800mg/L), adsorption time 60-120min.
Preferably, corn cob fiber element based aquagel prepared by the method for the invention is added to pH=6.5, Zn2+, Cd2+And Cr3+Concentration is respectively to be adsorbed in 200mg/L, 400mg/L and 800mg/L heavy metal solution, and adsorption time is 60min。
The beneficial effects of the invention are as follows:
(1) it is combined by corn cob fiber element with MMT and prepares hydrogel, corn cob fiber element, which is inserted into sheet and covered, is taken off In soil, the lamellar structure of montmorillonite is destroyed, cellulose forms baroque tridimensional network with acrylate copolymer again, made Hydrogel structure is stable, increases the adsorbance of hydrogel, and montmorillonite elementary cell is dispersed in polymeric matrix, can be with Realize with it is compound on the nanoscale of polymer, add the water imbibition and specific surface area of hydrogel, for hydrogel performance Research extends new approaches.
(2) the corn cob fiber element of nitric acid-Ethanol Method extraction is pure cellulose, without being passed through as conventional wooden cellulose High temperature chemical treatment, cellulose purity height and structural integrity are crossed, is prepared into Stability Analysis of Structures after hydrogel.
(3) prepare during hydrogel without the degree of neutralization that use sodium hydroxide regulation acrylic acid, reduce consumption of chemical agent, The adsorption effect of hydrogel is improved in acid condition.Not adjusting acrylic acid degree of neutralization with sodium hydroxide in preparation process can be with Improve the structural stability of pure cellulose based aquagel in acid condition, because the carboxylic acid group of polyacrylic acid is weak acid, water-setting The pH that swelling hop occurs for glue is higher, and the pH sensitiveness of hydrogel is dissociated flat by polyacrylic acid in gel in acid condition Weighing apparatus, Donnan balance influences are smaller inside and outside ion electrostatic repulsion and gel on network chain, so as to improve the absorption of hydrogel Effect.
(4) hydrogel is applied to the absorption of heavy metal ion, reduces contaminated wastewater load, and hydrogel is as biology The repeatable utilization of adsorbent and degraded can reduce cost for wastewater treatment;
(5) a kind of new method and thinking are provided for the application of hydrogel, improves the absorption property of hydrogel, widen water-setting Glue applies channel;
(6) present invention improve can corn cob fiber element value, expand corn cob fiber element application, enhancing The absorption property of hydrogel, can solve heavy metal in water ion contamination problems.
Embodiment
It is noted that described further below is all exemplary, it is intended to provides further instruction to the present invention.It is unless another Indicate, all technologies used herein and scientific terminology are with usual with general technical staff of the technical field of the invention The identical meanings of understanding.
It should be noted that term used herein above is merely to describe embodiment, and be not intended to restricted root According to the illustrative embodiments of the present invention.As used herein, unless the context clearly indicates otherwise, otherwise singulative It is also intended to include plural form, additionally, it should be understood that, when in this manual using term "comprising" and/or " bag Include " when, it indicates existing characteristics, step, operation and/or combinations thereof.
Herein, term " corn cob fiber element " refers to the pure cellulose extracted from corncob.
Term " corn cob fiber element based aquagel " refers to corn cob fiber element, montmorillonite, acrylic acid and N.N '-methylene Base bisacrylamide is hydrogel prepared by primary raw material.
Really as described in the background art, the heavy metal adsorption that prior art is prepared using traditional lignocellulosic as raw material Hydrogel has that adsorption capacity is low, the rate of adsorption is slow, structural instability and the problems such as adsorption capacity difference, thus the present invention reopening The preparation method of the good cellulose base hydrogel of Stability Analysis of Structures that to send out a kind of new, recyclability.
A kind of preparation method of corn cob fiber element based aquagel is disclosed in an embodiment of the invention, utilizes nitre Acid-Ethanol Method extracts corn cob fiber element from corncob, and corn cob fiber element is dissolved in distilled water, adds MMT in N2 The lower heating in water bath for reaction of protection;Reaction adds ammonium sulfate after terminating and tetramethylethylenediamine is stirring evenly and then adding into AA and MBA, adds Thermal agitation obtains hydrogel.
Preparation method of the present invention selection corn cob fiber element prepares one of primary raw material as hydrogel, in corncob Content of cellulose is up to 35%, is native grass fiber element, hemicellulose and lignin are easier to remove, so as to obtain The higher cellulose of purity, needing not move through high temeperature chemistry processing can obtain.
Preparation method of the present invention starts first to make corn cob fiber element with MMT in N2The lower heating water bath of protection carries out anti- Should, the plain rupture inserted between cheating engaging layer with montmorillonite layer structure of corn cob fiber is promoted, makes montmorillonite elementary cell more It is tiny, being compounded on corn cob fiber element evenly.
Degree of neutralization of the preparation method of the present invention without use sodium hydroxide regulation AA, the application directly by AA and MBA and Initiator is added in corn cob fiber element/MMT mixed solutions, the hydroxyl contracting on AA monomers polymerization crosslinking and corn cob fiber element Close two reactions to carry out simultaneously, AA reduces AA activity with the hydroxyl condensation on corn cob fiber element, so need not pass through tune The degree of neutralization for saving AA controls reaction speed.AA polymerize and grafting is carried out simultaneously, makes the three-dimensional structure of hydrogel more complicated, structure It is more stable.Herein described preparation method eliminates the step of adjusting AA degree of neutralization with sodium hydroxide, and AA does not pass through hydroxide Neutralisation treatment at sodium, the hydrogel structure of preparation are more stable.
In the preferred embodiment of the present invention, preferable, MMT/LNC mass ratioes when preparing corn cob fiber element based aquagel The mass ratio that mass ratio for 0.08, AA/LNC is 16, MBA/LNC is 0.2.
Inventor find MMT content can not it is very few can not be excessive, MMT contents are very few not to have heavy metal ion Suction-operated;The excessive MMT of content can not be dispersed in corn cob fiber element well, and cellulose can not intert well with MMT With reference to MMT interlamellar spacings cannot be modified and particle diameter is larger, and not only adsorptivity cannot improve, and can also influence the structure of hydrogel The mass ratio of stability, preferable MMT and corn cob fiber element is 0.08.
AA/LNC of the present invention preferred mass ratio, which is that 16, AA contents are too low, can not form stable three-dimensional structure, AA contents The too high molecular weight increase for easily causing polymerization rear side chain, increases system viscosity, is easily tangled between strand, improve friendship Connection degree, reduce the absorption property of product.
When MBA/LNC of the present invention preferred mass ratio is that 0.2, MBA contents are relatively low, the degree of cross linking of hydrogel is small, water-soluble Good, adsorbance is low;During MBA too high levels, cause hydrogel crosslink density too big, the diastole of molecular network is restricted, a huge sum of money Category ion is difficult to enter from hydrogel surface inside it, and the swellbility of hydrogel diminishes, and causes adsorbance to decline.
It is excellent present invention also offers a kind of application process of the corn cob fiber element based aquagel absorption heavy metal ion The pH=6.5 of heavy metal solution, Zn in the embodiment of choosing2+, Cd2+And Cr3+Concentration is respectively 200mg/L, 400mg/L and 800mg/L, adsorption time 60min.
The pH=6.5 of application process heavy metal solution of the present invention, when pH value is smaller, substantial amounts of H is contained in solution+, H+ Certain adsorption site is fought for metal ion, on the other hand, the carboxyl, hydroxyl in hydrogel are electric in the larger solution of acidity From being suppressed, it is unfavorable for generating complex, so causing adsorbance very little;When gradual increase, being gradually reduced in solution, Comparatively adsorption site increases, carboxyl is ionized into COO-, be advantageous to the generation of complex, so adsorbance increases.
Zn in application process heavy metal solution of the present invention2+, Cd2+And Cr3+Concentration is respectively 200mg/L, 400mg/ L and 800mg/L, when concentration of heavy metal ion is smaller, increase ion concentration adsorbance increases therewith, with concentration of metal ions Increase, increase the mass transfer force of metal ion, reduce absorption resistance, while increase metal ion and adsorption site Contact area, gradually increase so as to adsorbance;Continue to increase ion concentration after adsorbance reaches maximum, adsorbance is omited on the contrary There is reduction, this is due to when ion concentration is excessive, hydrolysis degree increase, is reduced and the combination of active group, while metal The excessive swelling for being unfavorable for composite of ion concentration, is wrapped the active group on adsorbent, so adsorbance reduces.This Outside, in the heavy metal solution that different kinds of ions coexists, inhibitory action, different metal ions and the water between different ions be present The binding ability of gel active group is different, so the optium concentration of different metal ions is also different.
The preferred adsorption time of application process of the present invention is 60min, and absorption of the hydrogel to metal ion is mainly sent out On the avtive spot of adsorbent outer surface, the rate of adsorption is very fast for life;On the other hand, the absorption of adsorbate may occur at absorption The endoporus of agent, reaction rate is slower, takes more, and herein described hydrogel is to Zn during 60min2+, Cd2+And Cr3+Absorption reach To balance, continuing extension adsorption time adsorbance will not increase.
In following examples, in addition to having special instruction, other all percentages are mass percent.
Embodiment 1:
Nitric acid-ethanol corn core cellulose is extracted according to the following steps:
Weigh a certain amount of corncob to be put into conical flask, add nitric acid-ethanol (nitric acid:Ethanol is 1:4) mixed liquor, pass through Reflux condensate device heats 1h on 85 DEG C of water-bath, and residue is transferred in G2 glass filters, pumps filtrate.Above procedure It is repeated 2 times.The filter equipped with cellulose is finally moved into baking oven, constant weight is dried at 105 DEG C.
Embodiment 2:
Corn cob fiber element based aquagel is prepared according to the following steps:
The optimization of MMT/LNC mass ratioes:1. weighing appropriate corn cob fiber element to be put into three-necked flask, distilled water is added to dissolve Afterwards, being put into MMT, (MMT/LNC mass ratioes are respectively 0,0.03,0.05,0.08 and 0.11), and N is passed through at 85 DEG C2Stirring 60min, tetramethylethylenediamine (tetramethylethylenediamine/LNC is 0.2mL/g) and ammonium persulfate (ammonium persulfate/LNC matter are added afterwards Amount is than for 0.2), stirring 10min, and then adding AA (AA/LNC mass ratio is 16) and MBA, (MBA/LNC mass ratio is 0.2), continue heating stirring and obtain corn cob fiber element based aquagel.Gained hydrogel is added into absolute ethyl alcohol and stands 24h, is used Deionized water is cleaned, and 24h is dried at 60 DEG C, and stripping and slicing is standby.
2. it is 800mg/L that standby corn cob fiber element based aquagel is put into concentration, the heavy metal ion that pH is 6.5 is molten Liquid (Zn2+, Cd2+And Cr3+) in stirring and adsorbing 120min.
As a result:By adsorption experiment, the corn cob fiber element based aquagel LNC-g-AA/MMT obtained by above-mentioned processing step Heavy metal solion (Zn2+, Cd2+And Cr3+) absorption discovery is carried out with the continuous increasing of MMT/LNC mass ratioes (rate of charge) Add, i.e. the increase of MMT dosages, the adsorption capacity increase of hydrogel, when MMT/LNC mass ratioes are 0.08, hydrogel absorption weight Metal ion reaches maximum, and when more than 0.08, adsorbance downward trend occurs with the increase of ratio, it is seen that MMT/LNC compared with Suitable quality ratio is 0.08.Under this mass ratio, corn cob fiber element based aquagel LNC-g-AA/MMT is than conventional wooden cellulose Based aquagel LNC-g-AA/MMT heavy metal ions (Zn2+, Cd2+And Cr3+) adsorbance improve 16.2%.
Embodiment 3:
Corn cob fiber element based aquagel is prepared according to the following steps:
The optimization of AA/LNC mass ratioes:1. weighing appropriate corn cob fiber element to be put into three-necked flask, distilled water is added to dissolve Afterwards, MMT (MMT/LNC mass ratioes are 0.08) is put into, N is passed through at 85 DEG C260min is stirred, adds tetramethylethylenediamine (four afterwards Methyl ethylenediamine/LNC volume/mass ratio is 0.2mL/g) and ammonium persulfate (ammonium persulfate/LNC mass ratioes are 0.2), stirring 10min, then add AA (AA/LNC mass ratio be respectively 8,12,16,20 and 24) and MBA (MBA/LNC mass ratio is 0.2), continue heating stirring and obtain corn cob fiber element based aquagel.Gained hydrogel is added into absolute ethyl alcohol and stands 24h, is used Deionized water is cleaned, and 24h is dried at 60 DEG C, and stripping and slicing is standby.
2. it is 800mg/L that standby corn cob fiber element based aquagel is put into concentration, the heavy metal ion that pH is 6.5 is molten Liquid (Zn2+, Cd2+And Cr3+) in stirring and adsorbing 120min.
As a result:By adsorption experiment, the corn cob fiber element based aquagel LNC-g-AA/MMT obtained by above-mentioned processing step Heavy metal solion (Zn2+, Cd2+And Cr3+) absorption discovery is carried out as the increase of allyl monomer amount, corncob are fine The adsorbance increase of plain based aquagel (LNC-g-AA) heavy metal ion is tieed up, but when AA/LNC mass ratio is more than 16, water-setting Downward trend is presented in glue adsorbance, and therefore, AA/LNC mass ratio should control convenient 16.Under this mass ratio, corncob Cellulose base hydrogel LNC-g-AA/MMT is than conventional wooden cellulose base hydrogel LNC-g-AA/MMT heavy metal ions (Zn2+, Cd2+And Cr3+) adsorbance improve 13.8%.
Embodiment 4:
Corn cob fiber element based aquagel is prepared according to the following steps:
The optimization of MBA/LNC mass ratioes:1. weighing appropriate corn cob fiber element to be put into three-necked flask, distilled water is added to dissolve Afterwards, MMT (MMT/LNC mass ratioes are 0.08) is put into, N is passed through at 85 DEG C260min is stirred, adds tetramethylethylenediamine (four afterwards Methyl ethylenediamine/LNC volume/mass ratio is 0.2mL/g) and ammonium persulfate (ammonium persulfate/LNC mass ratioes are 0.2), stirring 10min, then add AA (AA/LNC mass ratio be 16) and MBA (MBA/LNC mass ratio is respectively 0.1,0.2,0.3, 0.4 and 0.5), continue heating stirring and obtain corn cob fiber element based aquagel.Gained hydrogel is added into absolute ethyl alcohol to stand 24h, cleaned with deionized water, 24h is dried at 60 DEG C, stripping and slicing is standby.
2. it is 800mg/L that standby corn cob fiber element based aquagel is put into concentration, the heavy metal ion that pH is 6.5 is molten Liquid (Zn2+, Cd2+And Cr3+) in stirring and adsorbing 120min.
As a result:By adsorption experiment, the corn cob fiber element based aquagel LNC-g-AA/MMT obtained by above-mentioned processing step Heavy metal solion (Zn2+, Cd2+And Cr3+) absorption discovery is carried out with the increase of dosage of crosslinking agent, hydrogel adsorbance Downward trend after first rising is presented, hydrogel adsorbance reaches maximum when MBA/LNC mass ratio is 0.2.Therefore, MBA/ Volume/mass ratio convenient LNC is 0.2.Under this mass ratio, corn cob fiber element based aquagel LNC-g-AA/MMT is than tradition Lignocellulosic based aquagel LNC-g-AA/MMT heavy metal ions (Zn2+, Cd2+And Cr3+) adsorbance improve 14.6%.
Embodiment 5:
The absorption of corn cob fiber element based aquagel heavy metal ion is prepared according to the following steps:
The optimization of concentration of heavy metal ion:1. weighing appropriate corn cob fiber element to be put into three-necked flask, add distillation water-soluble Xie Hou, MMT (MMT/LNC mass ratioes are 0.08) is put into, N is passed through at 85 DEG C260min is stirred, adds tetramethylethylenediamine afterwards (tetramethylethylenediamine/LNC volume/mass ratio is 0.2mL/g) and ammonium persulfate (ammonium persulfate/LNC mass ratioes are 0.2), 10min is stirred, AA (AA/LNC mass ratio is 16) and MBA (MBA/LNC mass ratio is 0.2) is then added, continues to heat Stirring obtains corn cob fiber element based aquagel.Gained hydrogel is added into absolute ethyl alcohol and stands 24h, is cleaned with deionized water, 24h is dried at 60 DEG C, stripping and slicing is standby.
2. it is 50,100,200,400,600 and 800mg/L that standby corn cob fiber element based aquagel is put into concentration, PH is 6.5 heavy metal ion solution (Zn2+, Cd2+And Cr3+) in stirring and adsorbing 120min.
As a result:By adsorption experiment, the corn cob fiber element based aquagel LNC-g-AA/MMT obtained by above-mentioned processing step Heavy metal ion carries out absorption and finds to work as Zn2+, Cd2+And Cr3+When concentration is respectively 200mg/L, 400mg/L and 800mg/L, LNC-g-AA/MMT hydrogel adsorption effects are preferable.Under this concentration, corn cob fiber element based aquagel LNC-g-AA/MMT is than passing Unite lignocellulosic based aquagel LNC-g-AA/MMT heavy metal ions (Zn2+, Cd2+And Cr3+) adsorbance improve 11.7%.
Embodiment 6:
The absorption of corn cob fiber element based aquagel heavy metal ion is prepared according to the following steps:
The optimization of heavy metal ion pH value of solution:1. weighing appropriate corn cob fiber element to be put into three-necked flask, add distilled water After dissolving, MMT (MMT/LNC mass ratioes are 0.08) is put into, N is passed through at 85 DEG C260min is stirred, it is rear to add tetramethyl second two (ammonium persulfate/LNC mass ratioes are for amine (tetramethylethylenediamine/LNC volume/mass ratio is 0.2mL/g) and ammonium persulfate 0.2) 10min, is stirred, then adds AA (AA/LNC mass ratio is 16) and MBA (MBA/LNC mass ratio is 0.2), is continued Heating stirring obtains corn cob fiber element based aquagel.Gained hydrogel is added into absolute ethyl alcohol and stands 24h, it is clear with deionized water Wash, 24h is dried at 60 DEG C, stripping and slicing is standby.
2. standby corn cob fiber element based aquagel is put into Zn2+、Cd2+、Cr3+Concentration be respectively 200mg/L, Stirring and adsorbing 120min in 400mg/L and 800mg/L, pH 3.5,4.5,5.5 and 6.5 solution.
As a result:By adsorption experiment, the corn cob fiber element based aquagel LNC-g-AA/MMT obtained by above-mentioned processing step Heavy metal ion carries out absorption and finds that LNC-g-AA/MMT hydrogels are to Zn when solution ph is 6.52+, Cd2+And Cr3+'s Adsorption effect is preferable.Under this pH value, corn cob fiber element based aquagel LNC-g-AA/MMT is than conventional wooden cellulose base water-setting Glue LNC-g-AA/MMT heavy metal ions (Zn2+, Cd2+And Cr3+) adsorbance improve 12.9%.
Embodiment 7:
The absorption of corn cob fiber element based aquagel heavy metal ion is prepared according to the following steps:
The optimization of heavy metal ion solution adsorption time:1. weighing appropriate corn cob fiber element to be put into three-necked flask, add After distilled water dissolving, MMT (MMT/LNC mass ratioes are 0.08) is put into, N is passed through at 85 DEG C260min is stirred, adds tetramethyl afterwards Base ethylenediamine (tetramethylethylenediamine/LNC volume/mass ratio is 0.2mL/g) and ammonium persulfate (ammonium persulfate/LNC mass ratioes 0.2), to stir 10min, AA (AA/LNC mass ratio is 16) and MBA (MBA/LNC mass ratio is 0.2) is then added, after Continuous heating stirring obtains corn cob fiber element based aquagel.Gained hydrogel is added into absolute ethyl alcohol and stands 24h, uses deionized water Cleaning, dries 24h at 60 DEG C, and stripping and slicing is standby.
2. standby corn cob fiber element based aquagel is put into Zn2+, Cd2+And Cr3+Concentration is respectively 200mg/L, 400mg/L and 800mg/L, pH are stirring and adsorbing 10,20,40,60,90 and 120min in 6.5 solution.
As a result:By adsorption experiment, the corn cob fiber element based aquagel LNC-g-AA/MMT obtained by above-mentioned processing step Heavy metal ion carries out absorption and finds that when adsorption time is 60min LNC-g-AA/MMT hydrogels are to Zn2+, Cd2+And Cr3+ Adsorption effect it is preferable.Under this time, corn cob fiber element based aquagel LNC-g-AA/MMT is than conventional wooden cellulose base water Gel LNC-g-AA/MMT heavy metal ions (Zn2+, Cd2+And Cr3+) adsorbance improve 15.6%.
In summary, Zn is worked as2+, Cd2+And Cr3+Concentration is respectively that 200mg/L, 400mg/L and 800mg/L, solution ph are 6.5th, when adsorption time is 60min, corn cob fiber element based aquagel LNC-g-AA/MMT is to Zn2+, Cd2+And Cr3+Adsorbance It is up to 229.6mg/g, 479.3mg/g and 121mg/g.And adsorbance does not substantially change after being recycled for multiple times. Corn cob fiber element based aquagel LNC-g-AA/MMT is than conventional wooden cellulose base hydrogel LNC-g-AA/MMT heavy metals Ion (Zn2+, Cd2+And Cr3+) adsorbance improve 11-16%.
Embodiment 8:
Corn cob fiber element based aquagel adsorption-desorption cycle uses under nitric acid desorption is carried out according to the following steps:
Appropriate dry gel particle is added to preferable Zn2+, Cd2+And Cr3+In solution concentration, in preferable pH value and balance Between under the conditions of stirring mixture reach adsorption equilibrium, hydrogel particle is washed with deionized 3 times, in salpeter solution (0.5mol/ L stirring immersion desorption 2h in), is then rinsed 8h using 0.01mol/L NaOH, finally, is cleaned using deionized water, by gel Particle is re-used for adsorption experiment, and absorption-desorption process is repeated 8 times.
As a result:After LNC-g-AA/MMT hydrogels adsorption-desorption cycle uses 8 times, Cr3+、Cd2+And Zn2+Adsorption capacity Respectively 214.9mg/g, 449.8mg/g and 110.7mg/g, its adsorption capacity is slightly compared with hydrogel first adsorption effect Reduce, the recycling of this explanation LNC-g-AA/MMT hydrogel is smaller on the influence of its adsorption effect, and reason is in 0.5mol/L HNO3When being parsed in solution, proton easily produces competition with carboxyl metal ion, due to the presence of electrostatic attraction, causes a huge sum of money Belong to ionic adsorption on the surface of adsorbent, replaced with originally fixed ion.It can be seen that LNC-g-AA/MMT hydrogels have There is preferable stability, counterweight after being used 8 times than conventional wooden cellulose base hydrogel LNC-g-AA/MMT adsorption-desorption cycles Metal ion (Zn2+, Cd2+And Cr3+) adsorbance improve 8-12%.
Embodiment 9:
Corn cob fiber element based aquagel desorption cycle uses under EDTA desorptions is carried out according to the following steps:
Appropriate dry gel particle is added to preferable Zn2+, Cd2+And Cr3+In solution concentration, in preferable pH value and balance Between under the conditions of stirring mixture reach adsorption equilibrium, hydrogel particle is washed with deionized 3 times, in 0.1M EDTA solution In, the vibration desorption 3h under normal temperature, then using deionized water cleaning for several times, gel particle is re-used for adsorption experiment, inhaled Attached-desorption cycle uses 6 times.
As a result:After LNC-g-AA/MMT hydrogels adsorption-desorption cycle uses 6 times, Cr3+、Cd2+And Zn2+Adsorption capacity Respectively 216.9mg/g, 455.6mg/g and 114.7mg/g, its adsorption capacity is slightly compared with hydrogel first adsorption effect Reduce, the recycling of this explanation LNC-g-AA/MMT hydrogel is smaller on the influence of its adsorption effect.It can be seen that LNC-g-AA/MMT Hydrogel has preferable stability, and 6 are used than conventional wooden cellulose base hydrogel LNC-g-AA/MMT adsorption-desorption cycles Heavy metal ion (Zn after secondary2+, Cd2+And Cr3+) adsorbance improve 11-17%.

Claims (10)

1. a kind of preparation method of corn cob fiber element based aquagel, it is characterised in that comprise the following steps:
(1) weigh appropriate corn cob fiber element to be put into three-necked flask, after adding distilled water to dissolve;
(2) montmorillonite is added into step (1) resulting solution, the heating stirring under inert gas shielding;
(3) tetramethylethylenediamine and ammonium persulfate are added into mixing liquid obtained by step (2), is stirring evenly and then adding into acrylic acid Continue heating stirring with N.N '-methylene-bisacrylamide and obtain hydrogel;
(4) gained hydrogel is added into absolute ethyl alcohol to stand, is cleaned, dried with deionized water.
2. the preparation method of corn cob fiber element based aquagel as claimed in claim 1, it is characterised in that including following step Suddenly:
(1) weigh appropriate corn cob fiber element to be put into three-necked flask, after adding distilled water to dissolve;
(2) montmorillonite is added into step (1) resulting solution, the heating stirring under N2 protections, heating-up temperature is 75-90 DEG C, is stirred It is 50-70min to mix the time;
(3) tetramethylethylenediamine and ammonium persulfate are added into mixing liquid obtained by step (2), is stirring evenly and then adding into acrylic acid With N.N '-methylene-bisacrylamide, continue heating stirring and obtain hydrogel;
(4) gained hydrogel is added into absolute ethyl alcohol and stands 24h, cleaned with deionized water, 24h is dried at 50-70 DEG C.
3. the preparation method of corn cob fiber element based aquagel as claimed in claim 2, it is characterised in that:Add in step (2) Hot temperature is 85 DEG C, mixing time 60min.
4. the preparation method of corn cob fiber element based aquagel as claimed in claim 3, it is characterised in that:Each component mass ratio Respectively:Montmorillonite and corn cob fiber element mass ratio are 0.03-0.11;Acrylic acid and corn cob fiber element mass ratio are 8- 24;N.N '-methylene-bisacrylamide and corn cob fiber element mass ratio are 0.1-0.5;Tetramethylethylenediamine is fine with corncob The volume/mass ratio of dimension element is 0.2mL/g;Ammonium persulfate is 0.2 with corn cob fiber element mass ratio.
5. the preparation method of corn cob fiber element based aquagel as claimed in claim 4, it is characterised in that:Each component mass ratio Respectively:Montmorillonite and corn cob fiber element mass ratio are 0.05-0.08;Acrylic acid and corn cob fiber element mass ratio are 12- 20;N.N '-methylene-bisacrylamide and corn cob fiber element mass ratio are 0.2-0.4.
6. the preparation method of corn cob fiber element based aquagel as claimed in claim 5, it is characterised in that:The quality of each component Than being respectively:Montmorillonite is 0.08 with corn cob fiber element mass ratio;Acrylic acid is 16 with corn cob fiber element mass ratio; N.N '-methylene-bisacrylamide is 0.2 with corn cob fiber element mass ratio.
7. the preparation method of corn cob fiber element based aquagel as claimed in claim 1, it is characterised in that:The corncob is fine Tieing up plain extracting method includes:Corncob is put into nitric acid-alcohol mixed solution, reacted in a heated condition, gained is reacted Product filtering, it is dried to constant weight.
8. the preparation method of corn cob fiber element based aquagel as claimed in claim 7, it is characterised in that:Nitric acid-the second Nitric acid/ethanol mass ratio is 1 in mixed alkoxide solution:4;The heating condition is heating water bath, and temperature is 85 DEG C, during heating response Between be 1h;The filtering is filtered using G2 glass filters, is repeated 2 times;Drying temperature is 100-120 DEG C.
9. the application of corn cob fiber element based aquagel absorption heavy metal ion prepared by preparation method described in a kind of claim 1 Method, it is characterised in that:Corn cob fiber element based aquagel is added to pH=3.5-6.5, Zn2+, Cd2+And Cr3+Ion concentration To be adsorbed in 50-800mg/L heavy metal solution, adsorption time 60-120min.
10. application process as claimed in claim 9, it is characterised in that:Corn cob fiber element based aquagel is added to pH= 6.5, Zn2+, Cd2+And Cr3+Concentration is respectively to be adsorbed in 200mg/L, 400mg/L and 800mg/L heavy metal solution, is inhaled The attached time is 60min.
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Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109457472A (en) * 2018-10-22 2019-03-12 武汉轻工大学 A kind of cellulose nano-fibrous hydrogel and preparation method thereof
CN109967008A (en) * 2019-04-23 2019-07-05 南京林业大学 A kind of hemicellulose based aquagel and its preparation method and application
CN110003892A (en) * 2019-05-15 2019-07-12 齐鲁工业大学 A kind of sol-gal process preparation CdS/ZnS quantum dot of modification and its photocatalysis liberation of hydrogen application
CN110003392A (en) * 2019-04-15 2019-07-12 安徽农业大学 A kind of transparent superpower hydrogel and preparation method thereof in specific range of temperatures
CN110813263A (en) * 2019-11-27 2020-02-21 中国海洋大学 Biomass-based hydrogel adsorbent for immobilized yeast and preparation method and application thereof
CN112316860A (en) * 2020-10-13 2021-02-05 华南农业大学 Biomass-based hydrogel and preparation method and application thereof
CN112604667A (en) * 2020-11-25 2021-04-06 南京乐透思环保科技有限公司 Mud-water simultaneous treatment type bottom mud repairing material and preparation method and application thereof
CN112831491A (en) * 2021-02-09 2021-05-25 杭州楠大环保科技有限公司 Preparation method of microbial agent carrier
WO2021151748A1 (en) * 2020-01-29 2021-08-05 Givaudan Sa Process
CN114752078A (en) * 2022-04-26 2022-07-15 西北农林科技大学 Hydrogel adsorbent of cellulose grafted polyacrylic acid and bentonite, and preparation method and application thereof
CN114870813A (en) * 2021-11-30 2022-08-09 吉林工程技术师范学院 Preparation of non-swelling cellulose-based composite hydrogel and method for adsorbing heavy metal ions

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102690487A (en) * 2012-05-31 2012-09-26 新疆大学 Structure-controllable cellulose graft copolymer and montmorillonite composite and preparation method thereof
CN103709328A (en) * 2013-10-28 2014-04-09 北京林业大学 Preparation method of hemicelluloses-based organic-inorganic compound hydrogel
CN106750380A (en) * 2016-11-28 2017-05-31 吉林大学珠海学院 A kind of polymer-modified environmentally friendly composite aquogel and its application in heavy metal containing sewage is processed

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102690487A (en) * 2012-05-31 2012-09-26 新疆大学 Structure-controllable cellulose graft copolymer and montmorillonite composite and preparation method thereof
CN103709328A (en) * 2013-10-28 2014-04-09 北京林业大学 Preparation method of hemicelluloses-based organic-inorganic compound hydrogel
CN106750380A (en) * 2016-11-28 2017-05-31 吉林大学珠海学院 A kind of polymer-modified environmentally friendly composite aquogel and its application in heavy metal containing sewage is processed

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
史艳茹 等: "木质纤维素-g-丙烯酸/蒙脱土水凝胶制备及吸附性能研究", 《功能材料》 *

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CN110003392B (en) * 2019-04-15 2021-09-24 安徽农业大学 Super-strong hydrogel transparent in specific temperature range and preparation method thereof
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CN110813263A (en) * 2019-11-27 2020-02-21 中国海洋大学 Biomass-based hydrogel adsorbent for immobilized yeast and preparation method and application thereof
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