CN106824288A - Magnetic quinone amboceptor nano-functional material and its preparation method and application - Google Patents

Magnetic quinone amboceptor nano-functional material and its preparation method and application Download PDF

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CN106824288A
CN106824288A CN201710066553.0A CN201710066553A CN106824288A CN 106824288 A CN106824288 A CN 106824288A CN 201710066553 A CN201710066553 A CN 201710066553A CN 106824288 A CN106824288 A CN 106824288A
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particle
amboceptor
quinone
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郭建博
逯彩彩
宋圆圆
杨丹
李海波
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Tianjin Chengjian University
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    • B82YSPECIFIC USES OR APPLICATIONS OF NANOSTRUCTURES; MEASUREMENT OR ANALYSIS OF NANOSTRUCTURES; MANUFACTURE OR TREATMENT OF NANOSTRUCTURES
    • B82Y40/00Manufacture or treatment of nanostructures
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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Abstract

The invention discloses a kind of magnetic quinone amboceptor nano-functional material and its preparation method and application, with FeCl3、FeCl2It is raw material with ammoniacal liquor, the Fe of magnetic is prepared by coprecipitation3O4Particle;By adding tetraethoxysilane, make magnetic Fe3O4Particle surface covers silicon dioxide layer;The magnetic nano-particle of surface amino groups modification, Fe are prepared by using silane coupler aminopropyl triethoxy silica alkane3O4‑SiO2@NH2Reacted under conditions of triethylamine does acid binding agent with anthraquinone sulfonic acid chlorine and prepared.Quinone amboceptor magnetic Nano material prepared by the present invention can realize its extracting and developing and recovery by externally-applied magnetic field, effectively solve water-soluble quinonyl amboceptor and outflow with water and cause secondary pollution and continuously add the increased problem of cost;Anthraquinone amboceptor is fixed on magnetic nano-particle in the form of being chemically bonded, and because the surface area of nano-particle is big, can improve the load factor of anthraquinone amboceptor, and then realize its catalytic efficiency high.

Description

Magnetic quinone amboceptor nano-functional material and its preparation method and application
Technical field
The invention belongs to water environment treatment amboceptor field of functional materials, and in particular to a kind of magnetic quinone amboceptor nano functional Material and preparation method thereof, can be used for the biodegradation of catalytic environment pollutant, such as azo dyes, perchlorate, selenite Deng.
Background technology
With maintaining sustained and rapid growth for China's economy, water resources consumption is increased considerably so that water environment pollution problem day Become serious.For example:Azo dyes is typical pollutant in textile waste, after it enters river, not only influences the colourity of river And turbidity, and carcinogenic aromatic amine can be changed into, and water environment pollution is caused, influence the health of the mankind;Perchlorate is that one kind is held The inorganic pollution of long property, diffusion velocity is fast, stability is high, difficult degradation, and it can suppress the absorption of iodine and weaken thyroid gland work( Energy;Agricultural irrigation, mining activities and industrial wastewater discharge, making the selenium slow poisoning of selenium contamination environment, animal can cause breeding Deformity, mankind's intake soluble selenium can produce alkali disease etc..Therefore the removal or conversion of research water environment pollution has Important meaning.The method of pollutant process can be divided into Physical, chemical method, bioanalysis in existing water environment.Wherein, physics Method mainly has absorption method and membrane separation process etc., and chemical method mainly has Coagulation Method and oxidizing process etc., however, the method for these purifications Operating cost is generally higher, and easily causes secondary pollution.Comparatively speaking, bioanalysis, not only low cost, and secondary dirt can be reduced The generation of dye, bioanalysis is widely used as a kind of the most economic, effective method for treating water.
The biological treatment of waste water, general using anaerobic-aerobic disposal treatment, being processed by anaerobic stages can improve thereafter Continue aerobic biodegradability.However, the microorganism fungus kind of most environmental contaminants is under anaerobic, metabolic rate is slow, treatment The efficiency of pollutant is low.Therefore, the reaction rate of anaerobic stages turns into the speed limit of environmental contaminants complete biodegradable or removal Step.The research of the chemistry and bioconversion of nearest redox mediators catalytic intensification Recalcitrant chemicals, difficult pollution degradation The degraded of thing high-performance bio provides new Research Thinking.
The initial period of redox mediators research is that water-soluble amboceptor directly adds utilization, but water-soluble amboceptor is present easily Loss causes secondary pollution and continuously adds cost increase problem, and research is concentrated mainly on laboratory stage.In order to solve water The problem that soluble mediator is easy to run off, researcher have developed the immobilization technology of amboceptor, mainly with redox mediators with physical The modes such as embedding, absorption or chemical bonding are fixed on carrier, carry out catalysis pollutant anaerobic biodegradation/changing effect and Pilot reactor is studied.The amboceptor immobilization technology of existing report, from the size of immobilization carrier, can be divided into macro-size load Body and microscopic dimensions carrier technique for fixing.The technique for fixing of macro-size carrier effectively avoids water-soluble amboceptor loss and causes Secondary pollution and the continuous cost that adds increase problem.But the surface area of the carrier of macro-size is small, redox mediators are repaiied Decorations rate is relatively low, have impact on amboceptor catalytic efficiency.Then, the amboceptor immobilization technology of micro-nano carrier is of concern.But often The technique for fixing of the nano-carrier of rule there is also the problem for outflowing with water of amboceptor, cause the secondary pollution to environment.
The content of the invention
The technical problem to be solved in the present invention be to provide a kind of magnetic quinone amboceptor nano-functional material and preparation method thereof and Using it modifies in magnetic Fe quinone amboceptor by way of chemical bonding3O4The surface of nano-particle, is obtained quinone mediator-modified Magnetic particle, can be used for the biodegradation of catalytic environment pollutant.
In order to solve the above technical problems, the technical solution adopted by the present invention is:
A kind of magnetic quinone amboceptor nano-functional material, it is with nanometer Fe3O4Particle be magnetic kernel, with amorphous Si O2For in Between shell, in Fe3O4- SiO2Outer surface be modified with amino, the magnetic that anthraquinone -2- sulfonyls are grafted with the amino is received Rice functional material.
Present invention also offers the preparation method of above-mentioned magnetic quinone amboceptor nano-functional material, comprise the following steps:
A, preparation Fe3O4Magnetic nano-particle:With FeCl3And FeCl2For raw material is configured to solution, 40-80 DEG C is heated slowly to, Add ammoniacal liquor, stirring 10min-2h, washing, then by the Fe of hygrometric state3O4It is transferred in sodium citrate solution, ultrasonic disperse, washs, Fe is obtained3O4Magnetic nano-particle;
B, in Fe3O4Wrap up SiO in magnetic nano-particle outer surface2Layer:By Fe3O4Magnetic nano-particle is scattered in water and anhydrous second In the mixed solution of alcohol, tetraethoxysilane and ammoniacal liquor are sequentially added, under nitrogen atmosphere after stirring reaction 1-8 h, washing is produced Thing, drying, obtain Fe3O4- SiO2Magnetic particle;
C、Fe3O4- SiO2Particle modifies amino:By aminopropyl triethoxy silica alkane and Fe3O4- SiO2Magnetic particle disperses In absolute ethyl alcohol, ultrasonic 10min-2h after reacting 3-24h under 30-70 DEG C of nitrogen atmosphere, products therefrom is separated, washing, Dry, obtain amido modified Fe3O4- SiO2@ NH2Magnetic particle;
D, grafting anthraquinone sulfonyl:By the Fe3O4- SiO2@ NH2Magnetic particle is dispersed in the mixed of triethylamine and carbon dichloride Close in solution, be subsequently adding the carbon dichloride solution of anthraquinone sulfonic acid chloride, react 3-24h, FeSi-AQS magnetic particles are obtained.
Preferably, the mol ratio of FeCl3 and FeCl2 is Fe in step A3O4Metering compare 2:1, sodium citrate solution it is dense It is 0.1-1.0 mol/L to spend.
Aminopropyl triethoxy silica alkane and Fe in step C3O4- SiO2The mass ratio of particle is 1:1-3.
The synthetic method of anthraquinone sulfonic acid chloride is in step D:Weigh sodium anthraquinone sulfonate to be dissolved in dichloromethane, heating water bath is extremely 40-50 DEG C, condensing reflux measures chlorosulfonic acid and is placed in constant pressure funnel, dropwise completion of dropping, cold after the -7h of condensing reflux 6 But to room temperature, organic phase is distilled into water washing 3 times, after anhydrous magnesium sulfate dries organic phase, rotates dichloromethane, obtain anthraquinone sulphonyl Chlorine.
In above-mentioned technical proposal, with FeCl3、FeCl2It is raw material with ammoniacal liquor, magnetic is prepared by coprecipitation Fe3O4Nano-particle;By adding tetraethoxysilane, make magnetic Fe3O4Particle surface covers silicon dioxide layer;By using Silane coupler aminopropyl triethoxy silica alkane(Abbreviation APTES)Prepare the Fe of surface amino groups modification3O4- SiO2 @ NH2Magnetic particle, Fe3O4- SiO2@ NH2With anthraquinone sulfonic acid chlorine(Abbreviation AQSCl)Reacted under conditions of triethylamine does acid binding agent Prepare.Anthraquinone amboceptor is fixed on magnetic Fe by chemical bonding3O4On nano-particle, due to the particle diameter chi of nano-particle It is very little small, it is fully contacted with microorganism beneficial to amboceptor, be conducive to the biodegradation of the more preferable catalytic environment pollutant of the functional material. Magnetic functional material can make its displacement by externally-applied magnetic field, and then realize its separation and recovery and recycle, both effectively Avoid secondary pollution, and recoverable, with good economy.
Using above-mentioned technical proposal produce beneficial effect be:(1)Quinone amboceptor magnetic Nano material prepared by the present invention Its extracting and developing and recovery can be realized by externally-applied magnetic field, effectively solve water-soluble quinonyl amboceptor and outflow with water and make Into secondary pollution and continuously add the increased problem of cost;(2)Anthraquinone amboceptor of the present invention is fixed on magnetic in the form of being chemically bonded Property nano-particle on, because the surface area of nano-particle is big, the load factor of anthraquinone amboceptor can be improved, and then realize its height catalysis Efficiency.
Brief description of the drawings
Fig. 1 is the infrared spectrum of quinone amboceptor functional material prepared by embodiment 1, and wherein A represents Fe3O4- SiO2@ NH2, B Anthraquinone sulfonic acid chlorine is represented, C represents the infrared spectrum of FeSi-AQS;
Fig. 2 is the comparison chart of the quinone amboceptor functional material catalysis acceleration Azo dye decol of preparation in embodiment 1, wherein ■ generations The data of table blank group a1, ● the data of control group b1 are represented, ▲ represent the data of experimental group c1;
Fig. 3 a and 3b are respectively the Fe of preparation in embodiment 13O4The transmission electricity of magnetic nano-particle and FeSi-AQS magnetic particles Mirror figure.
Specific embodiment
Embodiment 1
A, Fe is prepared by chemical precipitation method3O4Magnetic nano-particle
FeCl is added in 250mL four-hole bottles3·6H2O(4.70g, 17.4mmol)、FeCl2·4H2O(1.72g, 8.7mmol) With 80mL redistilled waters, 80 DEG C are slowly heated to after ultrasonic 30min, dissolve to obtain orange solution;Then 10mL ammonia is added Water, solution is changed into black, and stirring reaction 30min at once.After reaction terminates, neutrality, magnetic are washed till with distilled water and absolute ethyl alcohol Directly by gained hygrometric state Fe after separation3O4Nano-particle is transferred in the sodium citrate solution of 200mL 0.3mol/L, ultrasonic disperse Open, and 12h is stirred at room temperature, washed solid product three times using redistilled water.Freeze-drying prepares black powder Last Fe3O4Magnetic particle.
B, in Fe3O4Wrap up SiO in magnetic nano-particle outer surface2Layer
By 60mg Fe3O4It is scattered in the mixed solvent of water and absolute ethyl alcohol, sequentially adds 1mL tetraethoxysilanes (TEOS)With 7mL ammoniacal liquor, under room temperature under nitrogen atmosphere after stirring reaction 5h, product Magneto separate, absolute ethyl alcohol and redistilled water Washing three times is simultaneously vacuum dried, and obtains the magnetic nano-particle Fe of Silica-coated3O4- SiO2.Mixed solvent reclaimed water and nothing The volume ratio of water-ethanol is 1:4.
C、Fe3O4- SiO2Amino is modified in magnetic particle outer surface
6mL APTES, 1.5mL ammoniacal liquor is dissolved in absolute ethyl alcohol, and in Fe3O4Disperse 100mg Fe in the absolute ethyl alcohol3O4- SiO2Magnetic particle, ultrasonic 30min is 1 after 12h, products therefrom volume ratio is reacted under 70 DEG C of nitrogen atmospheres:4 water and ethanol Mixed solvent washing, Magneto separate, vacuum drying obtain Fe3O4- SiO2@ NH2Magnetic particle.
D, grafting anthraquinone -2- sulfonyls
Anthraquinone -2- sulfonic acid chlorides are prepared first:By 2.5g anthraquinone-2-sodiums(AQS)It is dissolved in 150mL dichloromethane, ultrasound 30min, to 40 DEG C, rotor is at the uniform velocity stirred down heating water bath, condensing reflux, after reaching design temperature, is measured 4 mL chlorosulfonic acids and is put In constant pressure funnel, dropwise it is added dropwise, continues to stir, after condensing reflux 6h, be cooled to room temperature, mixed liquor is poured slowly into steaming In distilled water, point liquid goes water phase, then by organic phase distillation water washing 3 times is last dry organic phase 12h with anhydrous magnesium sulfate after, revolve Dichloromethane is steamed, yellow solid AQSCl is obtained.
Then, 5mL triethylamines are placed in there-necked flask, uniform stirring, heating water bath adds 0.118g to 30 DEG C Fe3O4- SiO2@ NH2, weigh 0.9200gAQSCl and be dissolved in 130mL chloroforms, constant pressure funnel fully is poured into after dissolving, by In dropping to flask(In 30min), clock reaction 4h.Product dichloromethane and distilled water respectively washing 3 times, drying obtain anthracene The magnetic particle of quinone modification(FeSi-AQS).
By anthraquinone-modified magnetic particle manufactured in the present embodiment, Fe3O4- SiO2@ NH2Particle and anthraquinone-2-sodium Infrared spectrum analysis is carried out respectively, referring to Fig. 1.The infrared spectrum of the front and rear magnetic particle of AQS modifications can be contrasted from figure, The characteristic absorption peak of AQS is increased in the infrared spectrum of FeSi-AQS, it was demonstrated that AQS has successfully been grafted to Fe3O4- SiO2@ NH2On magnetic particle.
To the Fe prepared in step A3O4The FeSi-AQS magnetic particles prepared in magnetic particle and step D carry out pattern Analysis, participates in Fig. 3, Fe3O4The particle diameter of magnetic particle is about 10nm, is still nano material through anthraquinone-modified FeSi-AQS.
Application Example 1
In order to verify the catalysis efficiency of FeSi-AQS, Setup Experiments blank group, control group and experimental group verify FeSi-AQS antithesis The influence of nitrogen biodegradation behavior.
First, using the acclimation method for stepping up dye strength, the azo dye that can degrade is tamed out from mud sample Expect the mixed bacterial of Reactive Brilliant Red K-2BP.Take thalline of the 10mL in exponential phase and be inoculated into 200mL LB degraded culture mediums In, at 35 DEG C, shaking speed treats that bacterium solution reaches 0.8A in 600nm absorbances to cultivate 12h under conditions of 140 r/min The research that microorganism biological reduces Azo dye decol is carried out during left and right.
Design three groups of experiments:Take three numbering be a1, b1 and c1 300mL serum bottles.1. to the serum bottle that numbering is a1 Add LB degraded culture mediums(Without inoculated bacteria)The FeSi-AQS magnetic ions prepared with 18mg embodiments 1 are used as blank group;② To numbering be above-mentioned culture is added in the serum bottle of b1 bacterium solution as a control group;3. it is to be added in the serum bottle of c1 to numbering The FeSi-AQS magnetic ions of bacterium solution and 18mg embodiments 1 preparation of culture are stated as experimental group.Active red dye in three groups of experiments The initial concentration of material is 200 mg/L.All serum bottles are sealed into bottle with serum cap and aluminium-plastic cap, it is ensured that maintained in serum bottle Anaerobic environment.
3mL is sampled every 2h, the dilution of centrifuging and taking supernatant is bent by standard after its absorbance is determined under 540nm wavelength The concentration of line computation dyestuff, and then obtain dyestuff degradation rate situation.Numbering is the biology of the corresponding azo dyes of a1, b1 and c1 group The percent of decolourization situation that changes with time is as shown in Figure 2.As can be seen from the figure because the addition of FeSi-AQS magnetic particles is catalyzed Accelerate the biological decolouring efficiency of azo dyes.
Embodiment 2
A, Fe is prepared by chemical precipitation method3O4Magnetic nano-particle
FeCl is added in 250mL four-hole bottles3·6H2O(2.70g, 10mmol)、FeCl2·4H2O(0.99g, 5mmol)With 80mL redistilled waters, are slowly heated to 70 DEG C after ultrasonic 30min, dissolve to obtain orange solution;Then 8mL ammoniacal liquor is added simultaneously Stirring reaction 30min.After reaction terminates, neutrality is washed till with distilled water and absolute ethyl alcohol, directly by gained hygrometric state after Magneto separate Fe3O4Nano-particle is transferred in the sodium citrate solution that 200mL concentration is 0.3mol/L, and ultrasonic disperse is opened, and is stirred at room temperature Reaction 10h is mixed, solid product is washed three times using redistilled water.Freeze-drying prepares black powder Fe3O4Magnetic grain Son.
B, in Fe3O4Wrap up SiO in magnetic nano-particle outer surface2Layer
By 100mg Fe3O4It is scattered in the mixed solvent of water and absolute ethyl alcohol, sequentially adds 1mLTEOS and 6mL ammoniacal liquor, room Under warm nitrogen atmosphere after stirring reaction 6h, product Magneto separate, absolute ethyl alcohol and second distillation water washing three times are simultaneously vacuum dried, Obtain the magnetic nano-particle Fe of Silica-coated3O4- SiO2.The volume ratio of mixed solvent reclaimed water and absolute ethyl alcohol is 1:1.
C、Fe3O4- SiO2Amino is modified in magnetic particle outer surface
6 mLAPTES and 1.5mL ammoniacal liquor are dissolved in absolute ethyl alcohol, 100mg Fe3O4- SiO2Magnetic particle is scattered in dissolving In the ethanol solution of APTES and ammoniacal liquor, ultrasonic 30min is after reacting 12 h, products therefrom water under 70 DEG C of nitrogen atmospheres And ethanol(Volume ratio 1:3)Mixed solvent washing, Magneto separate, vacuum drying obtain Fe3O4- SiO2@ NH2Magnetic particle.
D, grafting anthraquinone -2- sulfonyls
Anthraquinone -2- sulfonic acid chlorides are prepared first:It is identical with the method in embodiment 1, unlike:The amount of chlorosulfonic acid is 4mL.
Then, 5mL triethylamines are placed in there-necked flask, uniform stirring, heating water bath adds 118mg to 30 DEG C Fe3O4- SiO2@ NH2, weigh 920mgAQSCl and be dissolved in 100mL chloroforms, constant pressure funnel fully is poured into after dissolving, dropwise In dropping to flask(In 30min), react 5h.Product dichloromethane and distilled water respectively washing 3 times, drying obtain FeSi-AQS Magnetic particle.
Application Example 2
Using the acclimation method for stepping up perchlorate concentration, the mixed of the perchlorate that can degrade is tamed out from mud sample Close flora.Take thalline of the 10mL in exponential phase to be inoculated into 200mL perchlorate degraded culture medium, at 35 DEG C, shake Bed rotating speed treats that bacterium solution absorbance reaches 0.3 to cultivate 12h under conditions of 140r/min(λ=600nm)During left and right, chlorine high is added Sour sodium simultaneously makes its initial concentration be 50mg/L.
3 300 mL serum bottles are taken, numbering is a2, b2 and c2 respectively.By above-mentioned flora and the mixed solution of perchlorate It is dispensed into the serum bottle that numbering is b2, c2, the FeSi-AQS magnetic grain of the preparation of 20mg embodiments 2 is additionally added in wherein c2 bottles Son, numbering be a2 serum bottle in add perchlorate degraded culture medium(Without inoculated bacteria)With the FeSi-AQS magnetic of 20mg Particle and sodium perchlorate, and make sodium perchlorate initial concentration be 50mg/L.All serum bottles are sealed with serum cap and aluminium-plastic cap Bottle, it is ensured that anaerobic environment is maintained in serum bottle.
Sample at regular intervals, using ion chromatography ClO4- concentration, calculate perchlorate degradation rate.By than Compared with experimental group and control group, as a result show FeSi-AQS magnetic materials in itself to the perchlorate no degradation of drop, but its Catalysis significantly accelerates ClO4 -Biological reducing.
Embodiment 3
Fe is prepared by chemical precipitation method3O4Magnetic nano-particle.FeCl is added in 250mL four-hole bottles3·6H2O(2.70g, 10mmol)、FeCl2·4H2O(0.99g, 5mmol)With 80mL redistilled waters, 70 °C are slowly heated to after ultrasonic 30min, so After add 8mL ammoniacal liquor and stirring reaction 30min.After reaction terminates, neutrality is washed till with distilled water and absolute ethyl alcohol, after Magneto separate Directly by gained hygrometric state Fe3O4Nano-particle is transferred in the sodium citrate solution that 200mL concentration is 0.3mol/L, ultrasonic disperse Open, and reaction 10h is stirred at room temperature, washed solid product three times using redistilled water.Freeze-drying prepares black Color powder Fe3O4Magnetic particle.
By 100mg Fe3O4It is scattered in the mixed solvent of water and absolute ethyl alcohol, sequentially adds 1.5mLTEOS and 8mL ammonia Water, under room temperature under nitrogen atmosphere after stirring reaction 6h, product Magneto separate, absolute ethyl alcohol and second distillation water washing three times and vacuum Dry, obtain the magnetic particle Fe of Silica-coated3O4- SiO2
By 6mLAPTES, 1.5mL ammoniacal liquor and 100mg Fe3O4- SiO2Be scattered in absolute ethyl alcohol, ultrasonic 30min after 12h, products therefrom water and ethanol are reacted under 70 DEG C of nitrogen atmospheres(1:4)Mixed solvent washing, Magneto separate is vacuum dried To Fe3O4- SiO2@ NH2
By 2.5g anthraquinone-2-sodiums(AQS)Be dissolved in 150mL dichloromethane, ultrasonic 30min, heating water bath to 40 DEG C, Rotor is at the uniform velocity stirred down, condensing reflux, after reaching design temperature, is measured 6mL chlorosulfonic acids and is placed in constant pressure funnel, is dropwise dripped Plus, continue to stir, after condensing reflux 6h, room temperature is cooled to, mixed liquor is poured slowly into distilled water, point liquid water phase, organic phase With water washing is distilled 3 times, after drying organic phase 12h with anhydrous magnesium sulfate, dichloromethane is rotated, obtain yellow solid AQSCl.
5mL triethylamines are placed in there-necked flask, uniform stirring, heating water bath adds 100mg Fe to 30 DEG C3O4- SiO2@ NH2, weigh 900mg AQSCl and be dissolved in 100mL chloroforms, constant pressure funnel fully is poured into after dissolving, dropwise drop to In flask(In 30min), react 5h.Product dichloromethane and distilled water respectively washing 3 times, drying obtain FeSi-AQS magnetic grain Son.
Application Example 3
Take and be inoculated into 200mL Shewanella culture mediums in 10mL Shewanella liquid, at 35 DEG C, shaking speed is 140r/ 12h is cultivated under conditions of min, sodium selenite is added and is made its initial concentration be 1mmol/L.
3 300mL serum bottles are taken, numbering is a3, b3 and c3 respectively.Above-mentioned flora is equal with the mixed solution of selenite It is even to be dispensed into during numbering is b3 and c3 serum bottles, the FeSi-AQS magnetic particles of 20mg are added in wherein c3 bottles.In serum bottle a3 Add Shewanella culture medium(Without inoculated bacteria)The 20mgFeSi-AQSS magnetic particles and selenous acid prepared with embodiment 3 Sodium, makes the concentration of sodium selenite for 1mmol/L, as blank group;B2 is control group, and c3 is experimental group.All serum bottles are used Serum cap and aluminium-plastic cap envelope bottle, it is ensured that anaerobic environment is maintained in serum bottle.
Sample at regular intervals, by inductivity coupled plasma mass spectrometry(ICP-MS)The concentration of selenite radical is determined, Calculate the degradation rate of selenite radical.By comparative experiments group c3 and control group b2 and blank group, as a result show FeSi-AQS functions The addition of material catalysis significantly accelerates the biological reducing of selenite radical.
In sum, FeSi-AQS magnetic particles can realize its extracting and developing and recovery by externally-applied magnetic field, effectively Water-soluble quinonyl amboceptor is solved to outflow with water and cause secondary pollution and continuously add the increased problem of cost.FeSi-AQS magnetic Property particle has effectively been catalyzed bio-degradation reactions.

Claims (10)

1. a kind of magnetic quinone amboceptor nano-functional material, it is characterised in that it is with nanometer Fe3O4Particle be magnetic kernel, with non- Crystalline state SiO2It is subshell, in Fe3O4- SiO2Outer surface be modified with amino, anthraquinone -2- sulphurs are grafted with the amino The magnetic Nano functional material of acyl group.
2. the preparation method of magnetic quinone amboceptor nano-functional material described in a kind of claim 1, it is characterised in that including following step Suddenly:
A, preparation Fe3O4Magnetic nano-particle:With FeCl3And FeCl2For raw material is configured to solution, 40-80 DEG C is heated slowly to, plus Enter ammoniacal liquor, stirring 10min-2h, washing, then by the Fe of hygrometric state3O4It is transferred in sodium citrate solution, ultrasonic disperse, washs, system Obtain Fe3O4Magnetic nano-particle;
B, in Fe3O4Wrap up SiO in magnetic nano-particle outer surface2Layer:By Fe3O4Magnetic nano-particle is scattered in water and absolute ethyl alcohol Mixed solution in, sequentially add tetraethoxysilane and ammoniacal liquor, under nitrogen atmosphere after stirring reaction 1-8h, washed product, Dry, obtain Fe3O4-SiO2Magnetic particle;
C, amido modified Fe3O4-SiO2Particle:By aminopropyl triethoxy silica alkane and Fe3O4-SiO2Magnetic particle is scattered in In absolute ethyl alcohol, products therefrom is separated, washed, done by ultrasonic 10min-2h after 3-24h is reacted under 30-70 DEG C of nitrogen atmosphere It is dry, obtain amido modified Fe3O4-SiO2@NH2Magnetic particle;
D, grafting anthraquinone sulfonyl:By the Fe3O4-SiO2@NH2Magnetic particle is dispersed in triethylamine and the mixing of carbon dichloride is molten In liquid, the carbon dichloride solution of anthraquinone sulfonic acid chloride is subsequently adding, reacts 3-24h, FeSi-AQS magnetic particles are obtained.
3. the preparation method of magnetic quinone amboceptor nano-functional material according to claim 2, it is characterised in that in step A FeCl3And FeCl2Mol ratio be 2:1, the concentration of sodium citrate solution is 0.1-1.0 mol/L.
4. the preparation method of magnetic quinone amboceptor nano-functional material according to claim 2, it is characterised in that institute in step B It is 1 that mixed solution reclaimed water is stated with the volume ratio of absolute ethyl alcohol:1-10.
5. the preparation method of magnetic quinone amboceptor nano-functional material according to claim 4, it is characterised in that step B reclaimed waters It is 1 with the volume ratio of absolute ethyl alcohol:4-10.
6. the preparation method of magnetic quinone amboceptor nano-functional material according to claim 2, it is characterised in that ammonia in step C Base propyl-triethoxysilicane oxygen alkane and Fe3O4-SiO2The mass ratio of magnetic particle is 1:1-3.
7. the preparation method of magnetic quinone amboceptor nano-functional material according to claim 2, it is characterised in that step B and C Middle washing volume ratio is 1:The water of 1-10 and the mixed liquor of absolute ethyl alcohol.
8. the preparation method of magnetic quinone amboceptor nano-functional material according to claim 2, it is characterised in that anthracene in step D The synthetic method of quinone sulfonic acid chloride is:Sodium anthraquinone sulfonate is weighed to be dissolved in dichloromethane, heating water bath to 40-50 DEG C, condensing reflux, Measure chlorosulfonic acid to be placed in constant pressure funnel, dropwise completion of dropping, after condensing reflux 6-7h, be cooled to room temperature, by organic phase Distillation water washing 3 times, after anhydrous magnesium sulfate dries organic phase, rotates dichloromethane, obtains anthraquinone sulfonic acid chloride.
9. the preparation method of magnetic quinone amboceptor nano-functional material according to claim 8, it is characterised in that chlorosulfonic acid with The mol ratio of sodium anthraquinone sulfonate is 2-10:1.
10. application of the magnetic quinone amboceptor nano-functional material described in claim 1 in the biodegradation of catalytic environment pollutant.
CN201710066553.0A 2017-02-07 2017-02-07 Magnetic quinone amboceptor nano-functional material and its preparation method and application Pending CN106824288A (en)

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CN113019339A (en) * 2021-02-19 2021-06-25 武汉绿知行环保科技有限公司 Preparation method of magnetic nano material for printing and dyeing wastewater

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