CN107349909B - A kind of preparation method of magnetism stalk cellulose dye sorbent - Google Patents

A kind of preparation method of magnetism stalk cellulose dye sorbent Download PDF

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CN107349909B
CN107349909B CN201710598515.XA CN201710598515A CN107349909B CN 107349909 B CN107349909 B CN 107349909B CN 201710598515 A CN201710598515 A CN 201710598515A CN 107349909 B CN107349909 B CN 107349909B
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stalk
deionized water
dye
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CN107349909A (en
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万涛
陈巧和
熊静
唐利
廖玲
王艳芬
龚诗意
侯鹏
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Chengdu Univeristy of Technology
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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
    • B01J20/24Naturally occurring macromolecular compounds, e.g. humic acids or their derivatives
    • 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
    • B01J20/28002Solid 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 physical properties
    • B01J20/28009Magnetic properties
    • 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
    • C02F1/286Treatment of water, waste water, or sewage by sorption using natural organic sorbents or derivatives thereof
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2220/00Aspects relating to sorbent materials
    • B01J2220/40Aspects relating to the composition of sorbent or filter aid materials
    • B01J2220/48Sorbents characterised by the starting material used for their preparation
    • B01J2220/4812Sorbents characterised by the starting material used for their preparation the starting material being of organic character
    • B01J2220/4825Polysaccharides or cellulose materials, e.g. starch, chitin, sawdust, wood, straw, cotton
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/308Dyes; Colorants; Fluorescent agents

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  • Organic Chemistry (AREA)
  • Analytical Chemistry (AREA)
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  • Life Sciences & Earth Sciences (AREA)
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  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

The present invention relates to a kind of preparation methods of magnetic stalk cellulose dye sorbent, and stalk is used to sodium chlorite and NaOH pretreatment and sodium periodate oxidation respectively, obtains aldehyde radical stalk cellulose.Magnetic nano-particle is prepared using improvement chemical coprecipitation, then it is modified that surface is carried out to it with Silane coupling agent KH550, obtain KH550 modified magnetic nanoparticle, finally by KH550 modified magnetic nanoparticle, polyethyleneimine and glutaraldehyde carry out cross-linking reaction, prepare the magnetic stalk cellulose dye sorbent with schiff bases cross-linked structure and a variety of adsorption groups, saturation magnetization is 10~30 emu/g, remanent magnetism and coercivity go to zero, with paramagnetism and magnetic responsiveness, it is 100~1000mg/L aqueous dye solutions for initial concentration, Dye Adsorption capacity reaches 50~300mg/g, 60~150min reaches adsorption equilibrium, Dye Adsorption capacity after recycling utilization 5 times is more than the 75% of first time adsorption capacity, it can be extensive Applied to Dye Adsorption separation and waste water from dyestuff pollution control etc..

Description

A kind of preparation method of magnetism stalk cellulose dye sorbent
One, technical field
The present invention relates to a kind of preparation method of magnetic stalk cellulose dye sorbent, magnetism stalk prepared by the present invention Cellulose dye adsorbent is suitable for the adsorbing separation of dyestuff, can be widely applied to Dye Adsorption, dye separation purification and dye Expect environmental pollution improvement etc..
Two, background technique
Waste water from dyestuff is mainly derived from dye and dye intermediate production industry and weaving, leather, papermaking, rubber, plastics, The different industries such as cosmetics, pharmacy and food, with complicated composition, water and change of water quality are big, coloration is high, COD and BOD concentration High, the features such as suspended matter is more, recalcitrant substance is more, be one of industrial wastewater difficult to deal with.In addition, waste water from dyestuff is not only Have apparent coloration, influence sense organ, and containing to water body or the poisonous and hazardous pollutant of human body in waste water, if waste water from dyestuff without Processing direct emission is crossed, the destruction of water ecological setting can be caused, venomous injurant enters food chain, will affect the strong of human body Health, therefore environment-friendly high-efficiency handles the problem of waste water from dyestuff has become today's society urgent need to resolve.
The method of processing waste water from dyestuff mainly has chemistry, biology, physical method etc. at present.It is easy to operate to precipitate flocculence, at This is low, but a large amount of sludge generated increase operation cost.Electricity is consumed when Treatment of Wastewater by Electrolysis and metal electrode amount is big.Photocatalysis Oxidation is only good to low concentration waste water from dyestuff effect.The more single and microorganism of bioanalysis selectivity is environmentally sensitive.Absorption method operation Simply, at low cost, effect is good, adsorbent is easily recycled.The active charcoal of common adsorbent, mineral, resinae adsorbent Deng.Activated carbon adsorption power is strong, and removal rate is high, but at high cost, is normally only used for the lower treatment of dyeing wastewater of concentration or depth Reason.Mineral include natural zeolite, bentonite etc., and ion-exchange capacity and absorption property are preferable, but activity is low, and regeneration is difficult. And resinae adsorbent treatment effeciency is high, can regenerate under certain condition, can still keep efficiently, being suitable for waste water from dyestuff after regeneration Processing.
Traditional adsorbent such as ion exchange resin, absorption resin, carbonaceous class adsorbent and natural mesoporous mineral material Deng can only be separated by conventional methods such as centrifugation, filtering, precipitatings after, these adsorbent materials absorption dyestuff, it is not only time-consuming and laborious and And not energy-efficient and environmental protection, the structure of destructible adsorbent material affect the regeneration of adsorbent material.In recent years, nanometer The appearance of material and nanotechnology has been greatly facilitated the progress and development of dyestuff processing technique, and magnetic Nano material is because of its own spy The advantages that some bigger serfaces, active site abundant and high magnetism, shows huge application in Dye Adsorption and removal field Potentiality.Magnetic nanometer adsorbent can lead under the action of external magnetic field with the dyestuff contaminant in adsorbed water body, after the completion of absorption Magnetic Isolation is crossed, realizes the fast and effective separation of adsorbent and mother liquor, and at low cost, it is easy to operate, it preferably solves often It advises adsorbent and is separated by solid-liquid separation problem difficult and that recycling separation is difficult.
Li et al. utilizes poly- (acrylic acid-acrylamide-butyl methacrylate) hydrogel of Co deposited synthesis magnetism in situ, There is preferable Adsorption performance to Degradation of Cationic Dye Crystal Violet and basic fuchsin.Xu etc. is changed using solvent structure amino Property magnetic nano-particle, polyacrylic acid and amino modified magnetic nano-particle be then added carry out chemical graft and prepare magnetic polymeric Object adsorbent, adsorption capacity 55.8mg/g fast to the rate of adsorption of rhodamine R6G.The synthesis of super branched polyglycereol packet first such as He Magnetic Fe_3O_4 nanoparticle is covered, butanedioic anhydride is then added and obtains carboxylated modified ultra-branching coated magnetic Fe3O4 nanoparticle Son is high to dye of positive ion adsorption efficiency, the rate of adsorption is fast, favorable repeatability.Zhou etc. is prepared first with core-shell structure Then Fe3O4/SiO2 nanoparticle is added dissaving polymer progress surface and is modified, is eventually adding butanedioic anhydride and obtains carboxyl Change modified ultra-branching coated magnetic Fe3O4/SiO2 nanoparticle, rhodamine R6G and crystal violet adsorption capacity respectively reach 0.37mmol/g and 0.60mmol/g.Chen etc. uses the amino modified Fe3O4 nanoparticle of solvent structure, is then added and hands over Join agent glutaraldehyde and polyethyleneimine, generates the magnetic polyethylene imines adsorbent with three-dimensional net structure, acid matchmaker's alizarin Red, methyl orange, methylene blue, sunset yellow, core fast red and Alizarin Green adsorption capacity be respectively 145.7mg/g, 127.5mg/g, 137.0mg/g, 118.3mg/g and 126.8mg/g.
Wen etc. uses 1,2- Bromofume crosslinked polyethylenimine synthesizing polyethylene imine nanometer gel, then using original The position precipitation method prepare magnetic polyethylene imine nanometer composite hydrogel, and the removal rate of anionic dye CR is more than 99%.Cheng etc. Using one-step synthesis synthesizing magnetic polyvinyl alcohol/graphene oxide hydrogel, methylene blue and crystal violet adsorption capacity difference For 231.12mg/g and 204.74mg/g.Shanehsaz etc. prepares magnetic polypyrrole adsorbent, reactive blue using oxidative polymerization method RB19 adsorption capacity reaches 112.36mg/g.
Hosseinadeh etc. uses one-pot synthesis method to prepare carboxymethyl cellulose and polyacrylic acid as the magnetic fibre of matrix Element/polyacrylic acid hydrogel, Crystal Violet adsorption capacity reach 189mg/g.Beyki etc. is with the magnetism with core shell structure Fe3O4- cellulose is added epoxychloropropane and 1- methylimidazole prepares magnetic cellulose ionic liquid adsorbent as matrix, Congo red adsorption capacity reaches 131mg/g.γ-Fe2O3, cellulose and active carbon are crosslinked by Luo etc. with epoxychloropropane To magnetic cellulose/acticarbon, to the removal rate of methyl orange and methylene blue more than 99%.Chang etc. is by starch Then covalence graft multilayer carbon nanotube keeps magnetic nanoparticle raw in starch-grafted carbon nano tube surface by template of starch It is long, obtain magnetic starch/carbon nanotube adsorption material, methyl orange and methylene blue adsorption number capacity reach respectively 135.8mg/g and 94.1mg/g.Then starch and acrylic monomers is added in the synthesizing magnetic Fe3O4@SiO2 nanoparticle first such as Pourjavadi It carries out graft copolymerization and prepares magnetic starch graft polyacrylate hydrogel, Crystal Violet Dye removal rate is close to 90%.Baldikova Deng using sodium citrate-sodium hydroxide modified wheat stalk, magnetic wheat stalk adsorbent is then prepared using microwave process for synthesizing, Acridine orange and methyl green adsorption capacity are respectively 208.3mg/g and 384.6mg/g.
Although magnetic polymer dye sorbent gets more and more extensive concerning of people and is increasingly becoming both domestic and external grind Study carefully hot spot, but have not been reported both at home and abroad at present related magnetism stalk cellulose/polyethyleneimine dye sorbent preparation and Its Dye Adsorption performance study.
Three, summary of the invention
In view of this, the object of the invention is to provide a kind of preparation side of magnetic stalk cellulose dye sorbent Method.Magnetic nano-particle is prepared using improvement chemical coprecipitation first, table is then carried out to it using Silane coupling agent KH550 Face is modified, obtains KH550 modified magnetic nanoparticle.Stalk is subjected to pretreatment and chemical oxidation prepares aldehyde radical stalk fibre Then KH550 modified magnetic nanoparticle, aldehyde radical stalk cellulose, polyethyleneimine and glutaraldehyde are chemically crosslinked by element, Prepare the magnetic stalk cellulose/polyethyleneimine Dye Adsorption with schiff bases cross-linked structure and a variety of Dye Adsorption groups Agent improves the compatibility of magnetic nano-particle and polymeric matrix by silane coupler modified magnetic nano-particle, inhibits magnetic Property nanoparticle and polymeric matrix macroface separation, realize the high magnetic of magnetic stalk cellulose adsorbent Dye Adsorption Intelligence separation preferably solves the disadvantage that common dye adsorbent is separated by solid-liquid separation hardly possible, is also easy to produce secondary pollution.
Purpose according to the present invention proposes a kind of preparation method of magnetic stalk cellulose dye sorbent, feature There is following processing step:
A) stalk is cut into fragment, be washed with deionized 3~5 times, be put into 60~80 DEG C of baking oven drying, crushed, sieve takes The stalk powder of 100~200 mesh buffers the Acetic acid-sodium acetate that stalk powder and sodium chlorite are added to pH=3.5~5.5 Solution is warming up to 50~90 DEG C, is cooled to room temperature after reacting 2~6h, filters, and deionized water is washed 3~5 times, centrifuge separation, and 60 ~80 DEG C of oven dryings crush, obtain pretreated straw;Stalk powder, sodium chlorite and acetic acid-acetic acid of pH=3.5~5.5 The mass ratio of sodium buffer solution is 10~30:3~10:100~200;
B) pretreated straw is added to the NaOH solution that mass concentration is 5~10%, is warming up to 60~90 DEG C, reaction 2 ~6h, filtering, deionized water are washed 3~5 times, and centrifuge separation obtains pretreated straw cellulose;Pretreated straw and quality are dense Degree is 10~30:100~200 for the mass ratio of 5~10% NaOH solution;
C) pretreated straw cellulose, sodium metaperiodate and deionized water are added in three-necked flask, are warming up to 40~60 DEG C, 1.5~3h is reacted, the mass ratio of pretreated straw cellulose, sodium metaperiodate and deionized water is 10~30:5~10:100 ~200;Product is washed with deionized 3~5 times, is centrifugated, obtains aldehyde radical stalk cellulose;
D) FeCl36H2O, FeCl24H2O and deionized water are added in three-necked flask, are stirred evenly, nitrogen is protected 50~80 DEG C are warming up to after shield 30min, the ammonia spirit that mass concentration is 25~30% is then added dropwise, ammonia spirit is added dropwise 3~6h of nitrogen protection isothermal reaction afterwards, FeCl36H2O, FeCl24H2O, the ammonia spirit that mass concentration is 25~30% Mass ratio with deionized water is 10~30:5~10:25~60:100~200;It is cooled to room temperature, deionized water washing 3~5 Secondary, magnet separation obtains magnetic nano-particle;
E) magnetic nano-particle, Silane coupling agent KH550 and deionized water are added in three-necked flask and are stirred evenly, nitrogen It is warming up to 50~80 DEG C after gas shielded 30min, the ammonia spirit that mass concentration is 25~30%, nitrogen protection constant temperature is then added dropwise React 3~6h, magnetic nano-particle, Silane coupling agent KH550, the ammonia spirit that mass concentration is 25~30% and deionized water Mass ratio be 1~5:2~15:2~15:100~200;It is cooled to room temperature, deionized water is washed 3~5 times, and magnet separation obtains To KH550 modified Nano magnetic particle;
F) deionized water, KH550 modified magnetic nanoparticle and polyethyleneimine are added in three-necked flask, are passed through nitrogen Gas agitating is uniform, is warming up to 40~70 DEG C, then addition aldehyde radical stalk cellulose and glutaraldehyde, and nitrogen protection isothermal reaction 1~ 3h, aldehyde radical stalk cellulose, KH550 modified magnetic nanoparticle, polyethyleneimine, glutaraldehyde and deionized water mass ratio be 1~6:0.5~5:0.5~5:0.2~2:100~200;Product is washed with deionized 3~5 times, Magnetic Isolation, 60~80 DEG C oven drying crushes, obtains magnetic stalk cellulose dye sorbent;
G) magnetic stalk cellulose dye sorbent saturation magnetization is 10~30emu/g, and remanent magnetism and coercivity become In zero, there is paramagnetism and magnetic responsiveness, be 100~1000mg/L aqueous dye solutions, Dye Adsorption capacity for initial concentration Reach 50~300mg/g, 60~150min reaches adsorption equilibrium, and the Dye Adsorption capacity after recycling utilization 5 times is more than the The 75% of adsorption capacity.
Stalk used in the present invention be selected from corn stover, wheat stalk, soybean stalk, rice straw, broomcorn straw and Cotton stalk.
Dyestuff used in the present invention is selected from methylene blue, cationic blue FGL, cationic orange R, Cationic Bright Yellow 7GL, sun The pink FG of ion, methyl green, crystal violet, methyl orange, active black RB5, Congo red, alizarin red, sunset yellow, Alizarin Green, acidic chromium Blue K and eosin Y.
Advantages of the present invention and effect are:
1) by silane coupler modified magnetic nano-particle, improve the compatible of magnetic nano-particle and polymeric matrix Property, inhibit the separation of the macroface of magnetic nano-particle and polymeric matrix, realizes magnetic stalk cellulose/polyethyleneimine dyestuff The high magnetic of absorption intelligently separates, and preferably solves the disadvantage that common adsorbents are separated by solid-liquid separation hardly possible, are also easy to produce secondary pollution.
2) KH550 modified magnetic nanoparticle, aldehyde radical stalk cellulose, polyethyleneimine and glutaraldehyde are subjected to chemical friendship Connection prepares the magnetic stalk cellulose dye sorbent with schiff bases cross-linked structure and a variety of Dye Adsorption groups, by more The synergistic effect of kind adsorption group, further increases the absorption property of magnetic stalk cellulose adsorbent dyestuff;
3) magnetic stalk cellulose dye sorbent is prepared with this natural macromolecular material of agricultural crop straw, there is life Periodic chain is short, it is discarded after can the environmentally protective advantage such as natural degradation, that is, take full advantage of inexhaustible regenerated resources, and solve The environomental pollution source of crop straw burning realizes farming to current China's crop straw burning and dyestuff bring environmental pollution is administered The comprehensive utilization of object stalk and agricultural sustainable development have important, have huge social benefit, environmental benefit and economic effect Benefit.
The hysteresis property of magnetism stalk cellulose dye sorbent of the present invention, Dye Adsorption rate, adsorption capacity, Recycling utilization performance measurement method is as follows.
The hysteresis property of magnetic stalk cellulose dye sorbent is measured using LDJ-9600 type vibration magnetometer (VSM).
Dry, the finely ground magnetic stalk cellulose dyestuff of dye solution and 0.2g that concentration is 100~1000mg/L is inhaled Attached dose is put into 250mL conical flask, be subsequently placed in oscillator vibrate absorption, oscillation sample after a certain period of time, using it is ultraviolet/can Spectrophotometer is seen in the absorbance of dyestuff maximum absorption wave strong point measurement sample, and each sample is measured 3 times and is averaged, dyestuff Adsorbance qt, adsorption capacity qeIt is calculated as follows respectively:
qt(mg/g)={ (C0-Ct)V}/m (1)
qe(mg/g)={ (C0-Ce)V}/m (2)
Wherein C0、CtAnd CeRespectively dyestuff initial concentration, oscillation absorption certain time dye strength, Dye Adsorption balance Concentration (mg.L-1), V are liquor capacity (L), and m is the quality (g) of magnetic stalk cellulose dye sorbent.
The magnetic stalk cellulose adsorbent hydrochloric acid solution of 50mL 0.5mol/L of saturation absorption dyestuff is shaken into solution It inhales, desorption is flat until reaching desorption after a certain period of time using dye strength in ultraviolet/visible spectrophotometer measurement solution Weighing apparatus.Magnetic stalk cellulose adsorbent after desorption is dried and is crushed, then dyestuff is adsorbed again under the same conditions, Measure the Dye Adsorption capacity of magnetic stalk cellulose adsorbent using ultraviolet/visible spectrophotometer, and with first time dyestuff Adsorption capacity compare, characterize the recycling utilization performance of magnetic stalk cellulose dye sorbent, repeated regeneration circulation The absorption 5 times recycling utilization performances with the magnetic stalk cellulose dye sorbent of assessment.
Four, specific embodiment
For a better understanding of the present invention, below with reference to the embodiment content that the present invention is further explained, but it is of the invention Content be not limited solely to the following examples.
Embodiment 1:
Corn stover is cut into fragment, is washed with deionized 5 times, 60 DEG C of baking oven drying are put into, is crushed, sieve takes 200 mesh Maize straw powder, the Acetic acid-sodium acetate that 16g maize straw powder and 6g sodium chlorite are added to 150mL pH=4 is delayed Solution is rushed, is warming up to 70 DEG C, is cooled to room temperature after reacting 4h, is filtered, deionized water is washed 5 times, centrifuge separation, and 80 DEG C of baking ovens are dry It is dry, it crushes, obtains pretreatment corn stover;15g pretreatment corn stover is added to the NaOH that 150mL mass concentration is 5% Solution is warming up to 70 DEG C, reacts 4.5h, filtering, and deionized water is washed 5 times, centrifuge separation, obtains pretreatment corn stalk fiber Element;25g pretreatment corn stalk fiber element, 10g sodium metaperiodate and 200mL deionized water are added in three-necked flask, heated up To 50 DEG C, 2.5h is reacted, product is washed with deionized 5 times, be centrifugated, obtains aldehyde radical corn stalk fiber element.
20gFeCl36H2O and 8gFeCl24H2O and 200mL deionized water are added in three-necked flask, stirring is equal It is even, it is warming up to 70 DEG C after nitrogen protection 30min, the ammonia spirit that 50g mass concentration is 25~30%, ammonia spirit is then added dropwise Rear nitrogen protection isothermal reaction 4h is added dropwise, is cooled to room temperature, deionized water is washed 4 times, and magnet separation obtains magnetic Nano Particle;4g magnetic nano-particle, 12g Silane coupling agent KH550 and 200mL deionized water are added in three-necked flask and stirred It is even, it is warming up to 80 DEG C after nitrogen protection 30min, the ammonia spirit that 12g mass concentration is 25~30%, nitrogen protection is then added dropwise Room temperature is cooled to after isothermal reaction 3h, deionized water is washed 3 times, and magnet separation obtains KH550 modified Nano magnetic particle.
200mL deionized water, 4g KH550 modified magnetic nanoparticle and 4g polyethyleneimine are added to three-necked flask In, it is uniform to be passed through nitrogen gas stirring, is warming up to 60 DEG C, and 4g aldehyde radical corn stalk fiber element and 1.8g glutaraldehyde, nitrogen is then added Isothermal reaction 1.5h is protected, product is washed with deionized 5 times, Magnetic Isolation, 80 DEG C of oven dryings, crushes, obtains magnetism Corn stalk fiber element dye sorbent, saturation magnetization are 10~30emu/g, and remanent magnetism and coercivity go to zero, have Paramagnetism and magnetic responsiveness;Crystal violet, Cationic Bright Yellow 7GL, active black RB5 and the methyl for being 1000mg/L for initial concentration Orange aqueous solution, magnetic corn stalk fiber element dye sorbent crystal violet, Cationic Bright Yellow 7GL, active black RB5 and methyl orange are inhaled Attached capacity respectively reaches 300mg/g, 228mg/g, 150mg/g and 125mg/g, and 60min reaches adsorption equilibrium, recycling utilization Crystal violet, Cationic Bright Yellow 7GL, active black RB5 and Adsorption of Methyl Orange capacity after 5 times are more than first time adsorption capacity 75%.
Embodiment 2:
Wheat stalk is cut into fragment, is washed with deionized 3 times, 80 DEG C of baking oven drying are put into, is crushed, sieve takes 150 mesh Wheat stalk powder, 12g wheat stalk powder and 3.5g sodium chlorite are added to acetic acid-acetic acid of 100mL pH=5.5 Sodium buffer solution is warming up to 70 DEG C, is cooled to room temperature after reacting 4h, filters, and deionized water is washed 5 times, centrifuge separation, 80 DEG C of bakings Case dry, pulverize, and obtain pretreatment wheat stalk;It is 10% that 12g pretreatment wheat stalk, which is added to 100mL mass concentration, NaOH solution is warming up to 80 DEG C, reacts 3h, filtering, and deionized water is washed 5 times, centrifuge separation, and it is fine to obtain pretreatment wheat stalk Dimension element;12g pretreatment wheat straw fiber element, 6g sodium metaperiodate and 100mL deionized water are added in three-necked flask, heated up To 50 DEG C, 2.5h is reacted, product is washed with deionized 5 times, be centrifugated, obtains aldehyde radical wheat straw fiber element.
15gFeCl36H2O and 6gFeCl24H2O and 150mL deionized water are added in three-necked flask, stirring is equal It is even, it is warming up to 50 DEG C after nitrogen protection 30min, the ammonia spirit that 35g mass concentration is 25~30%, ammonia spirit is then added dropwise Rear nitrogen protection isothermal reaction 6h is added dropwise, is cooled to room temperature, deionized water is washed 5 times, and magnet separation obtains magnetic Nano Particle;2.5g magnetic nano-particle, 5g Silane coupling agent KH550 and 100mL deionized water are added in three-necked flask and are stirred Uniformly, 50 DEG C are warming up to after nitrogen protection 30min, the ammonia spirit that 6g mass concentration is 25~30% is then added dropwise, nitrogen is protected Room temperature is cooled to after shield isothermal reaction 6h, deionized water is washed 5 times, and magnet separation obtains KH550 modified Nano magnetic particle.
100mL deionized water, 1.5g KH550 modified magnetic nanoparticle and 3g polyethyleneimine are added to three mouthfuls of burnings In bottle, it is uniform to be passed through nitrogen gas stirring, is warming up to 60 DEG C, and 4g aldehyde radical wheat straw fiber element and 1g glutaraldehyde, nitrogen is then added Isothermal reaction 1.5h is protected, product is washed with deionized 3 times, Magnetic Isolation, 60 DEG C of oven dryings, crushes, obtains magnetism Wheat straw fiber element dye sorbent, saturation magnetization 10emu/g, remanent magnetism and coercivity go to zero, and have paramagnetic Property and magnetic responsiveness;Cationic Bright Yellow 7GL, active black RB5, alizarin red and the sunset yellow water for being 800mg/L for initial concentration Solution, magnetic wheat straw fiber element dye sorbent Cationic Bright Yellow 7GL, active black RB5, alizarin red and sunset yellow absorption are held Amount respectively reaches 193mg/g, 120mg/g, 98mg/g and 86mg/g, and 80min reaches adsorption equilibrium, after recycling utilization 5 times Cationic Bright Yellow 7GL, active black RB5, alizarin red and sunset yellow adsorption capacity be more than the 75% of first time adsorption capacity.
Embodiment 3:
Broomcorn straw is cut into fragment, is washed with deionized 3 times, 60 DEG C of baking oven drying are put into, is crushed, sieve takes 150 mesh Broomcorn straw powder, 30g broomcorn straw powder and 10g sodium chlorite are added to the Acetic acid-sodium acetate of 200mL pH=3.5 Buffer solution is warming up to 90 DEG C, is cooled to room temperature after reacting 2h, filters, and deionized water is washed 5 times, centrifuge separation, 80 DEG C of baking ovens It dry, pulverize, obtain pretreatment broomcorn straw;It is 5% that 15g pretreatment broomcorn straw, which is added to 150mL mass concentration, NaOH solution is warming up to 60 DEG C, reacts 6h, filtering, and deionized water is washed 5 times, centrifuge separation, and it is fine to obtain pretreatment broomcorn straw Dimension element;20g is pre-processed broomcorn straw cellulose, 8g sodium metaperiodate and 150mL deionized water to be added in three-necked flask, is heated up To 40 DEG C, 3h is reacted, product is washed with deionized 5 times, is centrifugated, obtain aldehyde radical broomcorn straw cellulose.
10gFeCl36H2O and 5gFeCl24H2O and 100mL deionized water are added in three-necked flask, stirring is equal It is even, it is warming up to 80 DEG C after nitrogen protection 30min, the ammonia spirit that 25g mass concentration is 25~30%, ammonia spirit is then added dropwise Rear nitrogen protection isothermal reaction 3h is added dropwise, is cooled to room temperature, deionized water is washed 4 times, and magnet separation obtains magnetic Nano Particle;3g magnetic nano-particle, 8g Silane coupling agent KH550 and 150mL deionized water are added in three-necked flask and stirred It is even, it is warming up to 80 DEG C after nitrogen protection 30min, the ammonia spirit that 10g mass concentration is 25~30%, nitrogen protection is then added dropwise Room temperature is cooled to after isothermal reaction 3h, deionized water is washed 3 times, and magnet separation obtains KH550 modified Nano magnetic particle.
150mL deionized water, 5g KH550 modified magnetic nanoparticle and 2g polyethyleneimine are added to three-necked flask In, it is uniform to be passed through nitrogen gas stirring, is warming up to 40 DEG C, and 3g aldehyde radical broomcorn straw cellulose and 1g glutaraldehyde is then added, and nitrogen is protected Isothermal reaction 3h is protected, product is washed with deionized 5 times, Magnetic Isolation, 80 DEG C of oven dryings, crushes, obtains magnetic sorghum Stalk cellulose dye sorbent, saturation magnetization 30emu/g, remanent magnetism and coercivity go to zero, have paramagnetism and Magnetic responsiveness;Crystal violet, methylene blue, sunset yellow and the Alizarin Green aqueous solution for being 600mg/L for initial concentration, magnetic sorghum Stalk cellulose dye sorbent crystal violet, methylene blue, sunset yellow and Alizarin Green adsorption capacity respectively reach 150mg/g, 100mg/g, 85mg/g and 72mg/g, 100min reach adsorption equilibrium, crystal violet, methylene blue after recycling utilization 5 times, Sunset yellow and Alizarin Green adsorption capacity are more than the 75% of first time adsorption capacity.
Embodiment 4:
Soybean stalk is cut into fragment, is washed with deionized 5 times, 80 DEG C of baking oven drying are put into, is crushed, sieve takes 200 mesh Soybean stalk powder, 15g soybean stalk powder and 4g sodium chlorite are added to the Acetic acid-sodium acetate of 150mL pH=4.8 Buffer solution is warming up to 50 DEG C, is cooled to room temperature after reacting 6h, filters, and deionized water is washed 5 times, centrifuge separation, 60 DEG C of baking ovens It dry, pulverize, obtain pretreated soybean stalk;It is 10% that 30g pretreated soybean stalk, which is added to 200mL mass concentration, NaOH solution is warming up to 90 DEG C, reacts 2h, filtering, and deionized water is washed 5 times, and it is fine to obtain pretreated soybean stalk for centrifuge separation Dimension element;30g pretreated soybean stalk cellulose, 10g sodium metaperiodate and 200mL deionized water are added in three-necked flask, risen Temperature reacts 1.5h, product is washed with deionized 5 times to 60 DEG C, is centrifugated, obtains aldehyde radical soybean stalk cellulose.
30gFeCl36H2O and 10gFeCl24H2O and 200mL deionized water are added in three-necked flask, stirred Uniformly, 70 DEG C are warming up to after nitrogen protection 30min, the ammonia spirit that 60g mass concentration is 25~30% is then added dropwise, ammonium hydroxide is molten Rear nitrogen protection isothermal reaction 4h is added dropwise in liquid, is cooled to room temperature, and deionized water is washed 5 times, and magnet separation obtains magnetism and receives Rice corpuscles;5g magnetic nano-particle, 15g Silane coupling agent KH550 and 200mL deionized water are added in three-necked flask and are stirred Uniformly, 70 DEG C are warming up to after nitrogen protection 30min, the ammonia spirit that 15g mass concentration is 25~30% is then added dropwise, nitrogen is protected Room temperature is cooled to after shield isothermal reaction 4h, deionization is washed 5 times or so, and magnet separation obtains KH550 modified Nano magnetic particles Son.
200mL deionized water, 5g KH550 modified magnetic nanoparticle and 5g polyethyleneimine are added to three-necked flask In, it is uniform to be passed through nitrogen gas stirring, is warming up to 70 DEG C, and 6g aldehyde radical soybean stalk cellulose and 2g glutaraldehyde is then added, and nitrogen is protected Isothermal reaction 1h is protected, product is washed with deionized 5 times, Magnetic Isolation, 60 DEG C of oven dryings, crushes, obtains magnetic soybean Stalk cellulose dye sorbent, saturation magnetization 18.6emu/g, remanent magnetism and coercivity go to zero, and have paramagnetism And magnetic responsiveness;Methylene blue, methyl green, active black RB5 and the Alizarin Red Aqueous Solution for being 300mg/L for initial concentration, magnetic Property soybean stalk cellulose dye adsorbent methylene blue, methyl green, active black RB5 and alizarin red adsorption capacity respectively reach 82mg/g, 77mg/g, 72mg/g and 60mg/g, 120min reach adsorption equilibrium, methylene blue after recycling utilization 5 times, Methyl green, active black RB5 and alizarin red adsorption capacity are more than the 75% of first time adsorption capacity.
Embodiment 5:
Cotton stalk is cut into fragment, is washed with deionized 3 times, 60 DEG C of baking oven drying are put into, is crushed, sieve takes 100 mesh Cotton stalk powder, 10g cotton stalk powder and 3g sodium chlorite are added to the Acetic acid-sodium acetate of 100mL pH=4.5 Buffer solution is warming up to 80 DEG C, is cooled to room temperature after reacting 3h, filters, and deionized water is washed 3 times, centrifuge separation, 80 DEG C of baking ovens It dry, pulverize, obtain pretreatment cotton stalk;It is 10% that 10g pretreatment cotton stalk, which is added to 100mL mass concentration, NaOH solution is warming up to 80 DEG C, reacts 3h, filtering, and deionized water is washed 3 times, centrifuge separation, and it is fine to obtain pretreatment cotton stalk Dimension element;10g pretreatment producing fibre from cotton stalk element, 5g sodium metaperiodate and 100mL deionized water are added in three-necked flask, heated up To 55 DEG C, 2h is reacted, product is washed with deionized 3 times, be centrifugated, obtains aldehyde radical producing fibre from cotton stalk element.
19.6g FeCl36H2O and 7.2g FeCl24H2O and 150mL deionized water is added in three-necked flask, It stirs evenly, 60 DEG C is warming up to after nitrogen protection 30min, the ammonia spirit that 50g mass concentration is 25~30%, ammonia is then added dropwise Rear nitrogen protection isothermal reaction 5h is added dropwise in aqueous solution, is cooled to room temperature, and deionized water is washed 3 times, and magnet separation obtains magnetic Property nanoparticle;1g magnetic nano-particle, 2g Silane coupling agent KH550 and 100mL deionized water are added in three-necked flask It stirs evenly, 60 DEG C is warming up to after nitrogen protection 30min, the ammonia spirit that 2g mass concentration is 25~30%, nitrogen is then added dropwise Room temperature is cooled to after gas shielded isothermal reaction 5h, deionized water is washed 5 times, and magnet separation obtains KH550 modified Nano magnetic particles Son.
100mL deionized water, 0.5g KH550 modified magnetic nanoparticle and 0.5g polyethyleneimine are added to three mouthfuls In flask, it is uniform to be passed through nitrogen gas stirring, is warming up to 50 DEG C, and 1g aldehyde radical producing fibre from cotton stalk element and 0.2g glutaraldehyde is then added, Nitrogen protection isothermal reaction 2h product is washed with deionized 3 times, Magnetic Isolation, 80 DEG C of oven dryings, crushes, obtains magnetic Property producing fibre from cotton stalk element dye sorbent, saturation magnetization 15.2emu/g, remanent magnetism and coercivity go to zero, have Paramagnetism and magnetic responsiveness;Crystal violet, Cationic Bright Yellow 7GL, sunset yellow and the alizarin clear water for being 100mg/L for initial concentration Solution, magnetic producing fibre from cotton stalk element dye sorbent crystal violet, Cationic Bright Yellow 7GL, methyl orange and Congo red adsorption capacity 73mg/g, 68mg/g, 54mg/g and 50mg/g are respectively reached, 150min reaches adsorption equilibrium, the knot after recycling utilization 5 times Crystalviolet, Cationic Bright Yellow 7GL, methyl orange and Congo red adsorption capacity are more than the 75% of first time adsorption capacity.

Claims (3)

1. a kind of preparation method of magnetism stalk cellulose dye sorbent, it is characterised in that there is following processing step:
A) stalk being cut into fragment, be washed with deionized 3~5 times, be put into 60~80 DEG C of baking oven drying, crushed, sieve takes 100~ Stalk powder and sodium chlorite are added to the NaAc_HAc buffer solution of pH=3.5~5.5 by the stalk powder of 200 mesh, 50~90 DEG C are warming up to, is cooled to room temperature after reacting 2~6h, is filtered, deionized water is washed 3~5 times, centrifuge separation, and 60~80 DEG C oven drying crushes, obtains pretreated straw;Stalk powder, sodium chlorite and the Acetic acid-sodium acetate of pH=3.5~5.5 are slow The mass ratio for rushing solution is 10~30:3~10:100~200;
B) pretreated straw is added to the NaOH solution that mass concentration is 5~10%, is warming up to 60~90 DEG C, react 2~6h, Filtering, deionized water are washed 3~5 times, and centrifuge separation obtains pretreated straw cellulose;Pretreated straw and mass concentration are 5 The mass ratio of~10% NaOH solution is 10~30:100~200;
C) pretreated straw cellulose, sodium metaperiodate and deionized water are added in three-necked flask, are warming up to 40~60 DEG C, instead 1.5~3h is answered, the mass ratio of pretreated straw cellulose, sodium metaperiodate and deionized water is 10~30:5~10:100~200; Product is washed with deionized 3~5 times, is centrifugated, obtains aldehyde radical stalk cellulose;
D) FeCl36H2O, FeCl24H2O and deionized water are added in three-necked flask, are stirred evenly, nitrogen protection It is warming up to 50~80 DEG C after 30min, the ammonia spirit that mass concentration is 25~30% is then added dropwise, after ammonia spirit is added dropwise Nitrogen protection isothermal reaction 3~6h, FeCl36H2O, FeCl24H2O, mass concentration be 25~30% ammonia spirit and The mass ratio of deionized water is 10~30:5~10:25~60:100~200;It is cooled to room temperature, deionized water is washed 3~5 times, Magnet separation, obtains magnetic nano-particle;
E) magnetic nano-particle, Silane coupling agent KH550 and deionized water are added in three-necked flask and are stirred evenly, nitrogen is protected 50~80 DEG C are warming up to after shield 30min, the ammonia spirit that mass concentration is 25~30%, nitrogen protection isothermal reaction is then added dropwise 3~6h, the matter of magnetic nano-particle, Silane coupling agent KH550, the ammonia spirit that mass concentration is 25~30% and deionized water Amount is than being 1~5:2~15:2~15:100~200;It is cooled to room temperature, deionized water is washed 3~5 times, and magnet separation obtains KH550 modified Nano magnetic particle;
F) deionized water, KH550 modified magnetic nanoparticle and polyethyleneimine are added in three-necked flask, are passed through nitrogen and stir It mixes uniformly, is warming up to 40~70 DEG C, aldehyde radical stalk cellulose and glutaraldehyde, nitrogen protection 1~3h of isothermal reaction, aldehyde is then added Base stalk cellulose, KH550 modified magnetic nanoparticle, polyethyleneimine, glutaraldehyde and deionized water mass ratio be 1~6: 0.5~5:0.5~5:0.2~2:100~200;Product is washed with deionized 3~5 times, Magnetic Isolation, 60~80 DEG C of bakings Case dry, pulverize, and obtain magnetic stalk cellulose dye sorbent;
G) magnetic stalk cellulose dye sorbent saturation magnetization is 10~30emu/g, and remanent magnetism and coercivity go to zero, It is 100~1000mg/L aqueous dye solutions for initial concentration with paramagnetism and magnetic responsiveness, Dye Adsorption capacity reaches 50 ~300mg/g, 60~150min reach adsorption equilibrium, and the Dye Adsorption capacity after recycling utilization 5 times is more than to inhale for the first time The 75% of attached capacity.
2. a kind of preparation method of magnetic stalk cellulose dye sorbent according to claim 1, it is characterised in that: institute The stalk stated is selected from corn stover, wheat stalk, soybean stalk, rice straw, jowar stalk and cotton stalk.
3. a kind of preparation method of magnetic stalk cellulose dye sorbent according to claim 1, it is characterised in that: institute The dyestuff stated be selected from methylene blue, cationic blue FGL, cationic orange R, Cationic Bright Yellow 7GL, cationic pink fg, methyl green, Crystal violet, methyl orange, active black RB5, Congo red, alizarin red, sunset yellow, Alizarin Green, acid chromium blue k and eosin Y.
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Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2014044182A1 (en) * 2012-09-19 2014-03-27 清华大学 Magnetic-core coated type inorganic ion adsorbent for removing cs ion from radioactive waste water, and preparation method thereof
CN103881033A (en) * 2014-02-26 2014-06-25 成都理工大学 Preparation method of crop straw dye adsorption material

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2014044182A1 (en) * 2012-09-19 2014-03-27 清华大学 Magnetic-core coated type inorganic ion adsorbent for removing cs ion from radioactive waste water, and preparation method thereof
CN103881033A (en) * 2014-02-26 2014-06-25 成都理工大学 Preparation method of crop straw dye adsorption material

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