CN109502598A - The method of one-step synthesis method mesoporous tungsten trioxide and zirconia-supported SBA-15 - Google Patents

The method of one-step synthesis method mesoporous tungsten trioxide and zirconia-supported SBA-15 Download PDF

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CN109502598A
CN109502598A CN201711272308.1A CN201711272308A CN109502598A CN 109502598 A CN109502598 A CN 109502598A CN 201711272308 A CN201711272308 A CN 201711272308A CN 109502598 A CN109502598 A CN 109502598A
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sba
molecular sieve
mesoporous
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preparation
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朱雯倩
倪忠斌
陈明清
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Wuxi Huitong Light Material Co Ltd
Jiangnan University
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Wuxi Huitong Light Material Co Ltd
Jiangnan University
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    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B37/00Compounds having molecular sieve properties but not having base-exchange properties
    • C01B37/005Silicates, i.e. so-called metallosilicalites or metallozeosilites
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J29/00Catalysts comprising molecular sieves
    • B01J29/03Catalysts comprising molecular sieves not having base-exchange properties
    • B01J29/0308Mesoporous materials not having base exchange properties, e.g. Si-MCM-41
    • B01J29/0341Mesoporous materials not having base exchange properties, e.g. Si-MCM-41 containing arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • B01J35/39Photocatalytic properties
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2229/00Aspects of molecular sieve catalysts not covered by B01J29/00
    • B01J2229/10After treatment, characterised by the effect to be obtained
    • B01J2229/18After treatment, characterised by the effect to be obtained to introduce other elements into or onto the molecular sieve itself
    • B01J2229/186After treatment, characterised by the effect to be obtained to introduce other elements into or onto the molecular sieve itself not in framework positions

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  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
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  • Chemical Kinetics & Catalysis (AREA)
  • Dispersion Chemistry (AREA)
  • Inorganic Chemistry (AREA)
  • Inorganic Compounds Of Heavy Metals (AREA)

Abstract

The present invention relates to a kind of methods that one-step method prepares mesoporous tungsten trioxide Yu zirconia-supported SBA-15, are named as ZrO2‑WO3/ SBA-15, belongs to technical field of inorganic nanometer material.Preparation step is as follows: using one polypropylene glycol of polyethylene glycol, one polyethylene glycol three block high molecular surfactant as template, tungsten source is added and forms total template, adds silicon source, is eventually adding zirconium source, then calcining forms meso-hole structure after crystallization.Mesoporous ZrO of the invention2‑WO3/ SBA-15 molecular sieve has the advantages that (1) solvent of the invention only has water, without other solvents, therefore will not generate by-product, be environmentally friendly;(2) the mesoporous ZrO of one-step synthesis method is used2‑WO3/ SBA-15, easy to operate, preparation time is short, saves preparation cost, and meso-hole structure is preferable, and repeatability is high;(3) mesoporous ZrO of the invention2‑WO3/ SBA-15 molecular sieve has good photocatalysis performance;(4) mesoporous ZrO of the invention2‑WO3/ SBA-15 molecular sieve has good ammonia nitrogen removal effect.

Description

The method of one-step synthesis method mesoporous tungsten trioxide and zirconia-supported SBA-15
Technical field:
The present invention relates to the preparation method of a kind of one-step synthesis method mesoporous tungsten trioxide and zirconia-supported SBA-15, lives Entitled ZrO2-WO3/ SBA-15, belongs to technical field of inorganic nanometer material.
Technical background:
Currently, waste water from dyestuff, since its discharge amount is big, concentration is high, difficult the features such as decolourizing, very big environmental pollution is caused. And ammonia nitrogen waste water will lead to water body fish, algae mortality, be environmental problem now urgently to be resolved.
Light degradation processing is carried out to waste water from dyestuff studies have shown that catalysis material can be used.However much have to dyestuff The material of preferable photocatalysis performance can only all carry out light degradation under ultraviolet light, and ultraviolet light only accounts for a small portion of sunlight Point, which has limited the application ranges of catalysis material.
CN104229924A reports the synthetic method introducing rare earth element in graphene, thus the conduct under mercury lamp The catalyst of photocatalysis dyestuff.
CN104229924A is reported under ultraviolet irradiation, and the titanium dioxide of synthesized high-energy surface exposure is to rhodamine B There is good light degradation effect.
CN104229924A reports the WO of synthesis3Composite coating has the application in outdoor optical degradation of formaldehyde.
It can be seen that WO3Light degradation can be carried out under visible light, and there is good practical application effect.
And ZrO2It in addition to this and a kind of good adsorbent is a kind of excellent photochemical catalyst,.
CN201710300477.5, which is reported, a kind of prepares ZrO2The method of oxide can be used to CO absorption2, meanwhile, it uses ZrO2Modified organic amine, it may have CO absorption2Effect.
CN201611245548.8 is reported with preparation ZrO2Oxide process heavy metal wastewater thereby, the ZrO of preparation2Oxide Large specific surface area has more active sites, has better suction-operated.
The processing of ammonia nitrogen waste water generally uses bioanalysis to remove ammonia nitrogen.CN201710211783.1 is reported using bioanalysis The method for eliminating ionic ammonia nitrogen waste water.
CN201611263509.0 reports a kind of self refresh stripping device removal ammonia nitrogen, and it is certainly rotten that a kind of microorganism is utilized Organic composite deamidization, to carry out NH_3-N treating.
Mesoporous material has a kind of new material of the uniform cellular structure of nanoscale and high surface area, and being that one kind is good urges Active component is introduced mesoporous supports by load or direct synthesis, can provide and live required for catalysis reaction by agent carrier Property position.Compared with conventional carrier, the active component dispersion degree on mesoporous material is more preferable, and contact of the reactant with activated centre is more Sufficiently, it is especially suitable for big flow, the reaction system of high-speed.
US5672556 reports a series of synthesis side introducing transition metal species in MCM-41 mesoporous material skeleton Method, these transition metal species include Ti, V, Sn, Zr, Zn, Cu, Co, Cr etc..
US6391278, which is reported, to be synthesized at room temperature using electroneutral primary amine or diamines as template containing transition metal species HMS series mesoporous material, these transition metal species include Ti, V, Sn, Zr, Zn, Cu, Cr etc..
Up to the present, the mesoporous ZrO of one-step synthesis method2-WO3/ SBA-15 has not been reported for catalysis material.
Summary of the invention:
The technical problem to be solved by the present invention is to be not directed to one-step method in conventional art to prepare load tungsten and zirconium in skeleton Mesoporous silica molecular sieve ZrO2-WO3The problem of/SBA-15, provides a kind of new mesoporous ZrO2-WO3/ SBA-15 molecule The preparation method of sieve.The molecular sieve of this method preparation has biggish specific surface area, and dispersion performance is good and dispersion capacity is big, is used for Light-catalyzed reaction, reactivity are higher.In order to solve the above technical problems, The technical solution adopted by the invention is as follows: a kind of mesoporous ZrO2-WO3The preparation method of/SBA-15 molecular sieve is with polyethylene glycol-polypropylene glycol-polyethylene glycol triblock polymer M Template, to be selected from tetraethyl orthosilicate, silica solution, waterglass or white carbon black as silicon source, to be selected from ammonium metatungstate, para-tungstic acid Ammonium, sodium tungstate or tungsten hexachloride are tungsten source, to be zirconium source in acid selected from basic zirconium chloride, zirconium hydroxide, zirconium acetate or zirconyl nitrate Property under the conditions of, feed molar proportion it is as follows:
1SiO2: 0.01~0.03M:3~10H+: 50~200H2O:0.03~0.25WO3: 0.01~0.2ZrO2
It is 20~170 DEG C in crystallization temperature, pressure is hydrothermal crystallizing 6~120 hours under the self-generated pressure of gel mixture ZrO needed for obtaining2-WO3/ SBA-15 molecular sieve;
It is cruel to be selected from positive silicic acid second for silicon source preferred embodiment in above-mentioned technical proposal;Tungsten source preferred embodiment is selected from sodium tungstate.Template Agent polyethylene glycol-polypropylene glycol-polyethylene glycol triblock polymer M molecular formula is H (- OCH2-CH2-)x[-OCH(CH3) CH2-]y(OCH2CH2-)zOH average molecular weight is 5800, abbreviation P123.Preparation method preferred embodiment is before crystallization, 20 First template M is dissolved in acidic aqueous solution at~60 DEG C, tungsten source is then added and forms common mode plate, adds the solution of silicon source, It is eventually adding zirconium source.Crystallization temperature preferred scope is 100 DEG C;Hydrothermal crystallizing time preferred scope is 24 hours.
The SBA-15 of the tungstenic and zirconium that synthesize in above-mentioned technical proposal need to be fired removed template method processing, and calcination process can It is chosen at Muffle furnace or is carried out in tube furnace;The optional temperature programming under an inert atmosphere of heating mode is roasted, heating rate is 1 ~10 DEG C, maturing temperature can choose 350 DEG C~800 DEG C, preferably 500 DEG C~750 DEG C.Calcining time is that oxidizing atmosphere 1~20 is small When, preferably 3~9 hours;Inert atmosphere 1~10 hour, preferably 3~6 hours.The present invention is mesoporous by introducing tungsten and zirconium The skeleton of SBA-15 molecular sieve, greatly improves specific surface area of catalyst, the dispersion degree of the tungsten increased, to improve catalysis Agent reactivity worth achieves preferable technical effect.
Below by embodiment, the present invention is further elaborated.
Specific embodiment:
Example one
2.0gP123, which is dissolved in 65ml deionized water, is stirred at room temperature 3h, and 10ml 2molL is added-1Hydrochloric acid solution in 40 It DEG C is vigorously stirred 1h, the 10ml aqueous solution of 0.72g (40%) Disodium tungstate (Na2WO4) dihydrate is added, forms clear solution after stirring 1h, is delayed It is slow that 4.5g tetraethyl orthosilicate is added dropwise, it is separately added into 0.1283g (m (ZrO2): m (SiO2)=3%, similarly hereinafter) chlorine hydrate oxidation Zirconium, for 24 hours in 40 DEG C of stirrings.Solution is transferred in water heating kettle, 100 DEG C it is still aging for 24 hours, take out, successively use deionized water, second Alcohol washs three times, 60 DEG C of dry 8h, 550 DEG C of calcining 6h.
It is accurate to measure 100mL10mgL-1Rhodamine B solution in beaker, the catalyst of 0.10g is added, in the dark 1h is stirred, then sampling is irradiated by light source of the xenon lamp of 200W, sample 1 time every 30min, takes 6 samples, sample is through centrifugation point From taking supernatant liquor, absorbance measured at optimal absorption wavelength (552nm) with ultraviolet-uisible spectrophotometer, according to formulaWherein D is degradation rate, A0For initial soln absorbance, A is surplus solution absorbance).Finally calculate Degradation rate to rhodamine B is 80.0%.
Prepare 50mgL-1NH4Cl solution takes 100ml, and 0.10g sample is added, and stirring is shaken at 30 DEG C, is existed respectively It is respectively sampled after 10,20,30,40,60,90,120min, constant volume, 1.0ml potassium sodium tartrate solution is added, shakes up, adds Na Shi Reagent 1.5ml, shakes up.After placing 10min, at wavelength 420nm, with 20mm cuvette, reference is made with water, measures absorbance. The mass concentration of ammonia nitrogen is according to formula in waterWherein ρNFor the mass concentration (mgL of ammonia nitrogen in water sample-1), AsFor The absorbance of water sample, AbFor the absorbance of blank test, a is the intercept of calibration curve, and b is the slope of calibration curve.Finally count Calculate ammonia nitrogen removal frank be 82.7%.
Example two
2.0gP123, which is dissolved in 65ml deionized water, is stirred at room temperature 3h, and 10ml 2molL is added-1Hydrochloric acid solution in 40 It DEG C is vigorously stirred 1h, the 10ml aqueous solution of 0.72g (40%) Disodium tungstate (Na2WO4) dihydrate is added, forms clear solution after stirring 1h, is delayed It is slow that 4.5g tetraethyl orthosilicate is added dropwise, it is separately added into 0.2139g (5%) chlorine hydrate zirconium oxide, for 24 hours in 40 DEG C of stirrings.It will be molten Liquid is transferred in water heating kettle, 100 DEG C it is still aging for 24 hours, take out, successively use deionized water, ethanol washing three times, 60 DEG C of dryings 8h, 550 DEG C of calcining 6h.
It is accurate to measure 100mL10mgL-1Rhodamine B solution in beaker, the catalyst of 0.10g is added, in the dark 1h is stirred, then sampling is irradiated by light source of the xenon lamp of 200W, sample 1 time every 30min, takes 6 samples, sample is through centrifugation point From taking supernatant liquor, absorbance measured at optimal absorption wavelength (552nm) with ultraviolet-uisible spectrophotometer, according to formulaWherein D is degradation rate, A0For initial soln absorbance, A is surplus solution absorbance).Finally calculate Degradation rate to rhodamine B is 86.6%.
Prepare 50mgL-1NH4Cl solution takes 100ml, and 0.10g sample is added, and stirring is shaken at 30 DEG C, is existed respectively It is respectively sampled after 10,20,30,40,60,90,120min, constant volume, 1.0ml potassium sodium tartrate solution is added, shakes up, adds Na Shi Reagent 1.5ml, shakes up.After placing 10min, at wavelength 420nm, with 20mm cuvette, reference is made with water, measures absorbance. The mass concentration of ammonia nitrogen is according to formula in waterWherein ρNFor the mass concentration (mgL of ammonia nitrogen in water sample-1), AsFor The absorbance of water sample, AbFor the absorbance of blank test, a is the intercept of calibration curve, and b is the slope of calibration curve.Finally count Calculate ammonia nitrogen removal frank be 80.4%.
Example three
2.0g P123, which is dissolved in 65ml deionized water, is stirred at room temperature 3h, and 10ml 2molL is added-1Hydrochloric acid solution in 40 It DEG C is vigorously stirred 1h, the 10ml aqueous solution of 0.72g (40%) Disodium tungstate (Na2WO4) dihydrate is added, forms clear solution after stirring 1h, is delayed It is slow that 4.5g tetraethyl orthosilicate is added dropwise, it is separately added into 0.2995g (7%) chlorine hydrate zirconium oxide, for 24 hours in 40 DEG C of stirrings.It will be molten Liquid is transferred in water heating kettle, 100 DEG C it is still aging for 24 hours, take out, successively use deionized water, ethanol washing three times, 60 DEG C of dryings 8h, 550 DEG C of calcining 6h.
It is accurate to measure 100mL10mgL-1Rhodamine B solution in beaker, the catalyst of 0.10g is added, in the dark 1h is stirred, then sampling is irradiated by light source of the xenon lamp of 200W, sample 1 time every 30min, takes 6 samples, sample is through centrifugation point From taking clear 2 liquid in upper layer, absorbance measured at optimal absorption wavelength (552nm) with ultraviolet-uisible spectrophotometer, according to formulaWherein D is degradation rate, A0For initial soln absorbance, A is surplus solution absorbance).Finally calculate Degradation rate to rhodamine B is 82.8%.
Prepare 50mgL-1NH4Cl solution takes 100ml, and 0.10g sample is added, and stirring is shaken at 30 DEG C, is existed respectively It is respectively sampled after 10,20,30,40,60,90,120min, constant volume, 1.0ml potassium sodium tartrate solution is added, shakes up, adds Na Shi Reagent 1.5ml, shakes up.After placing 10min, at wavelength 420nm, with 20mm cuvette, reference is made with water, measures absorbance. The mass concentration of ammonia nitrogen is according to formula in waterWherein ρNFor the mass concentration (mgL of ammonia nitrogen in water sample-1), AsFor The absorbance of water sample, AbFor the absorbance of blank test, a is the intercept of calibration curve, and b is the slope of calibration curve.Finally count Calculate ammonia nitrogen removal frank be 77.4%.
Example four
2.0g P123, which is dissolved in 65ml deionized water, is stirred at room temperature 3h, and 10ml 2molL is added-1Hydrochloric acid solution in 40 It DEG C is vigorously stirred 1h, the 10ml aqueous solution of 0.72g (40%) Disodium tungstate (Na2WO4) dihydrate is added, forms clear solution after stirring 1h, is delayed It is slow that 4.5g tetraethyl orthosilicate is added dropwise, it is separately added into 0.385g (9%) chlorine hydrate zirconium oxide, for 24 hours in 40 DEG C of stirrings.By solution Be transferred in water heating kettle, 100 DEG C it is still aging for 24 hours, take out, successively use deionized water, ethanol washing three times, 60 DEG C of dry 8h, 550 DEG C of calcining 6h.
It is accurate to measure 100mL10mgL-1Rhodamine B solution in beaker, the catalyst of 0.10g is added, in the dark 1h is stirred, then sampling is irradiated by light source of the xenon lamp of 200W, sample 1 time every 30min, takes 6 samples, sample is through centrifugation point From taking supernatant liquor, absorbance measured at optimal absorption wavelength (552nm) with ultraviolet-uisible spectrophotometer, according to formulaWherein D is degradation rate, A0For initial soln absorbance, A is surplus solution absorbance).Finally calculate Degradation rate to rhodamine B is 84.4%.
Prepare 50mgL-1NH4Cl solution takes 100ml, and 0.10g sample is added, and stirring is shaken at 30 DEG C, is existed respectively It is respectively sampled after 10,20,30,40,60,90,120min, constant volume, 1.0ml potassium sodium tartrate solution is added, shakes up, adds Na Shi Reagent 1.5ml, shakes up.After placing 10min, at wavelength 420nm, with 20mm cuvette, reference is made with water, measures absorbance. The mass concentration of ammonia nitrogen is according to formula in waterWherein ρNFor the mass concentration (mgL of ammonia nitrogen in water sample-1), AsFor The absorbance of water sample, AbFor the absorbance of blank test, a is the intercept of calibration curve, and b is the slope of calibration curve.Finally count Calculate ammonia nitrogen removal frank be 75.3%.

Claims (7)

1. a kind of method that one-step method prepares mesoporous tungsten trioxide Yu zirconia-supported SBA-15, is named as ZrO2-WO3/SBA- 15 molecular sieves, using polyethylene glycol-polypropylene glycol-polyethylene glycol triblock polymer M as template, to be selected from positive silicic acid tetrem Ester, silica solution, waterglass or white carbon black are silicon source, to be selected from ammonium metatungstate, ammonium paratungstate, sodium tungstate or tungsten hexachloride as tungsten Source, using, as zirconium source, in acid condition, feed molar is with such as selected from basic zirconium chloride, zirconium hydroxide, zirconium acetate or zirconyl nitrate Under:
1SiO2: 0.01~0.03M:3~10H+: 50~200H2O:0.03~0.25WO3: 0.01~0.2ZrO2
It is 20~170 DEG C in crystallization temperature, pressure is to obtain within hydrothermal crystallizing 6~120 hours under the self-generated pressure of gel mixture Required ZrO2-WO3/ SBA-15 molecular sieve.
2. mesoporous ZrO according to claim 12-WO3The preparation method of/SBA-15 molecular sieve, it is characterised in that tungsten source choosing From sodium tungstate.
3. mesoporous ZrO according to claim 12-WO3The preparation method of/SBA-15 molecular sieve, it is characterised in that silicon source choosing From tetraethyl orthosilicate.
4. mesoporous ZrO according to claim 12-WO3The preparation method of/SBA-15 molecular sieve, it is characterised in that zirconium source choosing From basic zirconium chloride.
5. mesoporous ZrO according to claim 12-WO3The preparation method of/SBA-15 molecular sieve, it is characterised in that crystallization temperature Degree is 100 DEG C, crystallization time 24 hours.
6. mesoporous ZrO according to claim 12-WO3The preparation method of/SBA-15 molecular sieve, it is characterised in that in crystallization Before, first template M is dissolved in acidic aqueous solution at 20~60 DEG C, tungsten source is then added and forms common mode plate, adds silicon The solution in source is eventually adding zirconium source.
7. mesoporous ZrO according to claim 12-WO3The preparation method of/SBA-15 molecular sieve, it is characterised in that acid water The acid of solution is selected from hydrochloric acid.
CN201711272308.1A 2017-12-06 2017-12-06 The method of one-step synthesis method mesoporous tungsten trioxide and zirconia-supported SBA-15 Withdrawn CN109502598A (en)

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Publication number Priority date Publication date Assignee Title
CN110078195A (en) * 2019-04-24 2019-08-02 上海交通大学 The ammonia nitrogen waste water degeneration system and method for chlorine oxygen radical are generated based on photoelectrocatalysis
CN110078195B (en) * 2019-04-24 2021-04-23 上海交通大学 Ammonia nitrogen wastewater degradation system and method based on generation of chlorine-oxygen free radicals through photoelectrocatalysis

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