CN105642364B - A kind of composite photo-catalyst and its preparation method and application - Google Patents

A kind of composite photo-catalyst and its preparation method and application Download PDF

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CN105642364B
CN105642364B CN201610043759.7A CN201610043759A CN105642364B CN 105642364 B CN105642364 B CN 105642364B CN 201610043759 A CN201610043759 A CN 201610043759A CN 105642364 B CN105642364 B CN 105642364B
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acfs
composite photo
mos
catalyst
coal
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CN105642364A (en
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李嘉
李红艳
徐超超
左敏
宋鹏
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University of Jinan
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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
    • B01J31/00Catalysts comprising hydrides, coordination complexes or organic compounds
    • B01J31/26Catalysts comprising hydrides, coordination complexes or organic compounds containing in addition, inorganic metal compounds not provided for in groups B01J31/02 - B01J31/24
    • B01J31/34Catalysts comprising hydrides, coordination complexes or organic compounds containing in addition, inorganic metal compounds not provided for in groups B01J31/02 - B01J31/24 of chromium, molybdenum or tungsten
    • 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
    • B01J35/50Catalysts, in general, characterised by their form or physical properties characterised by their shape or configuration
    • B01J35/58Fabrics or filaments
    • 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
    • B01J35/60Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/61Surface area
    • B01J35/61310-100 m2/g
    • 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
    • B01J35/60Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/63Pore volume
    • B01J35/633Pore volume less than 0.5 ml/g
    • 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
    • B01J35/60Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/64Pore diameter
    • B01J35/643Pore diameter less than 2 nm
    • 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
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/30Nature of the water, waste water, sewage or sludge to be treated from the textile industry
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
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  • Inorganic Chemistry (AREA)
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Abstract

The invention discloses a kind of composite photo-catalyst and its preparation method and application, belongs to catalysis material technical field.The present invention is prepared for NACF by biological template of kapok(ACFs), MoS is grown using hydro-thermal method simultaneously on ACFs2With CoAl LDH, MoS is finally given2/ CoAl-LDH/ACFs composite photo-catalysts.The present invention is easy to operate, technique is simple, and reaction condition is gentle, and the catalyst appearance structure of acquisition is novel special, the organic pollution in its sewage that can efficiently be degraded under simulated solar light irradiation.

Description

A kind of composite photo-catalyst and its preparation method and application
Technical field
The present invention relates to the catalyst in terms of a kind of sewage disposal, and in particular to it is a kind of prepared using kapok as template it is porous MoS2/ CoAl-LDH/ACFs composite photo-catalysts and its preparation method and application.
Background technology
The species of Pollutants in Wastewater has a lot, and wherein organic pollution accounts for major part, is one mostly in waste water from dyestuff A little molecular structures hardly possiblies are decomposed, the organic matter that chemical property is sufficiently stable, therefore application photocatalytic oxidation degradation Organic Pollution is As one of important method, and photocatalysis technology non-secondary pollution.
MoS2Energy gap is narrower, about 1.97eV, under visible light illumination, has excellent photocatalysis performance.However, MoS2Although photochemical catalyst response optical wavelength can extend to visible-range, because its photo-generate electron-hole recombination rate is fast, inhales Attached poor performance make it that its visible light catalytic performance is not especially high.The present invention is by ACF and MoS2Compound, ACF can be used as electronics Grabber, so as to reduce photo-generate electron-hole recombination rate, to improve its photocatalysis efficiency.Layered double hydroxide class Compound(Layered double hydroxides, LDHs), due to its special layer structure, surface positively charged, interlayer can be cloudy Ion, which swaps etc., assigns its wide application, such as absorption, photocatalysis, medical science field.By LDHs and MoS2, ACF it is multiple Close, not only the absorption property of combination product improves, and the efficiency of photocatalytic degradation dirt Organic substance in water is also greatly improved.
The content of the invention
It is an object of the invention to provide a kind of composite photo-catalyst and its preparation method and application.
The present invention is achieved through the following technical solutions:
A kind of composite photo-catalyst, it is characterised in that the catalyst is MoS2/ CoAl-LDH/ACFs composite photo-catalysts.
Described composite photo-catalyst, it is characterised in that it is made of the MoS using kapok as biological template2And CoAl- LDH is grown on ACFs fibers, micropore and mesoporous graded porous structure be present simultaneously on every fiber.
A kind of preparation method of composite photo-catalyst, it is characterised in that it is prepared by following methods:
(1)Configure the ZnCl that 75 ~ 85 mL concentration are 95 mg/L2Solution, while 15mg neopelexes are added, 2g kapoks are put into the solution after time of infusion, take out drying;
(2)Take step(1)In obtained kapok, it is then heated to 900 DEG C of progress in the environment of logical nitrogen Calcining, is then cooled to 300 DEG C, finally naturally cools to room temperature, wash, dry to obtain ACFs;
(3)By 20mg steps(2)The ACFs of middle gained and 0.242 g sodium molybdates, 0.38g thiocarbamide mixed dissolutions are in 55 ~ 65 In mL distilled water, stir;
(4)By step(3)The middle reaction solution configured is transferred in hydrothermal reaction kettle liner, is fitted into hydrothermal reaction kettle anti- Should, reaction is cooled to room temperature after terminating, and supernatant is removed, and filters, washs, drying and obtain MoS2/ACFs;
(5)Take 200mg steps(4)Described in MoS2/ ACFs is placed in 55 ~ 65 mL cobalt salts, silicon source, urea and ammonium fluoride It is according to mol ratio(2~3):1:25:(8~9)In the mixed solution of composition, stir to obtain mixed reaction solution;
(6)By step(5)Gained mixed reaction solution is transferred in hydrothermal reaction kettle liner, is fitted into hydrothermal reaction kettle and is reacted, Reaction is cooled to room temperature after terminating, and supernatant is removed, filters, wash, drying to MoS2/CoAl-LDH/ACFs。
The step(1)Dip time is 2h, and drying temperature is 80 DEG C.
The step(2)Rate of heat addition during middle calcining is 5 DEG C/min, calcination time 1h.
The step(4)Middle reaction temperature is 210 DEG C, soaking time 24h.
The step(6)Middle reaction temperature is 100 DEG C, soaking time 10-24h.
Above-mentioned composite photo-catalyst can be used for catalytic degradation processing waste water from dyestuff.The photochemical catalyst is right in 120 min Congo red degradation rate reaches more than 78%, shows that the composite photo-catalyst has efficient catalytic effect to congo red.
The beneficial effects of the invention are as follows:The present invention prepares MoS by biological template of kapok2/ CoAl-LDH/ACFs complex lights Catalyst, required raw material are easy to get, and cost is cheap, preparation technology is simple, easy to operate, efficiency high, the composite photocatalyst dosage form of acquisition Looks structure is special, has micropore and mesoporous graded porous structure.Due to the MoS of preparation2/ CoAl-LDH/ACFs complex lights are urged Agent has special graded porous structure, therefore has excellent absorption property.The composite photo-catalyst is in radiation of visible light Under there is preferable degradation efficiency to organic pollution, more than 78% is reached to Congo red degradation rate in 120 min.
Brief description of the drawings
Fig. 1 is the made photochemical catalysts of embodiment 1-3 in the present invention under visible light to Congo red degraded figure.
Fig. 2 is the XRD curves of 3 made photochemical catalyst of embodiment in the present invention;
Fig. 3 is the SEM figures and EDS spectrograms of 3 made photochemical catalyst of embodiment in the present invention;In figure, (a) is that embodiment 3 is made The MoS obtained2The SEM figures of/CoAl-LDHs/ACFs composite photo-catalysts, (b), (c) are(a)In corresponding to 1,2 point EDS spectrum Figure.
Fig. 4 is the N of 3 made photochemical catalyst of embodiment in the present invention2Adsorption/desorption curve and respective aperture distribution curve.
Embodiment
With reference to specific embodiment, the present invention is described further.
Embodiment 1
(1)Configure 75 mL 95 mg/L ZnCl2Solution, while 15 mg neopelexes are added, by 2 g wood Cotton is put into the solution impregnated for 2 h times after, take out after 80 DEG C of drying, then 900 DEG C of calcinings under logical nitrogen by it, forge Heating rate is 5 DEG C/min during burning, and soaking time is 1 h, is then cooled to 300 DEG C, finally naturally cools to room temperature, Obtain ACFs;
(2)Take 20 mg steps(1)Described in ACFs mix with 0.242 g sodium molybdates, 0.38 g thiocarbamides and be dissolved in 60 mL In distilled water, stir, the reaction solution configured is transferred in 100 mL hydrothermal reaction kettle liners, load hydrothermal reaction kettle Middle reaction, reaction temperature are 210 DEG C, and soaking time is 24 h, and reaction is cooled to room temperature after terminating, and supernatant is removed, mistake Filter, washing, drying obtain MoS2/ACFs;
(3)Take 200 mg steps(2)Described in MoS2/ ACFs is placed in 60 mL cobalt salts, aluminium salt, urea and ammonium fluoride and rubbed You are than being 2:1:25:In 9 mixed solution, stir, the reaction solution configured is transferred to 100 mL hydrothermal reaction kettles In liner, it is fitted into hydrothermal reaction kettle and reacts, reaction temperature is 100 DEG C, and soaking time is 10 h, and reaction is cooled to after terminating Room temperature, supernatant is removed, filter, wash, drying and obtain MoS2/CoAl-LDH/ACFs。
Embodiment 2
(1)Configure 85mL 95mg/L ZnCl2Solution, while 15mg neopelexes are added, 2g kapoks are put Enter after impregnating the 2h times in the solution, take out after 80 DEG C of drying, then calcine it for 900 DEG C under logical nitrogen, calcination process Middle heating rate is 5 DEG C/min, soaking time 1h, is then cooled to 300 DEG C, finally naturally cools to room temperature, obtain ACF;
(2)Take 20 mg steps(1)Described in ACF mixed with 0.242 g sodium molybdates, 0.38 g thiocarbamides be dissolved in 60 mL steaming In distilled water, stir, the reaction solution configured is transferred in 100 mL hydrothermal reaction kettle liners, is fitted into hydrothermal reaction kettle Reaction, reaction temperature are 210 DEG C, and soaking time is 24 h, and reaction is cooled to room temperature after terminating, and supernatant is removed, filtering, Washing, drying obtain MoS2/ACFs;
(3)Take 200 mg steps(2)Described in MoS2/ ACFs is placed in 60 mL cobalt salts, aluminium salt, urea and ammonium fluoride and rubbed You are than being 3:1:25:In 8 mixed solution, stir, the reaction solution configured is transferred to 100 mL hydrothermal reaction kettles In liner, it is fitted into hydrothermal reaction kettle and reacts, reaction temperature is 100 DEG C, and soaking time is 15 h, and reaction is cooled to after terminating Room temperature, supernatant is removed, filter, wash, drying and obtain MoS2/CoAl-LDH/ACFs。
Embodiment 3
(1)Configure 80 mL 95 mg/L ZnCl2Solution, while 15 mg neopelexes are added, by 2 g wood Cotton is put into the solution impregnated for 2 h times after, take out after 80 DEG C of drying, then 900 DEG C of calcinings under logical nitrogen by it, forge Heating rate is 5 DEG C/min during burning, and soaking time is 1 h, is then cooled to 300 DEG C, finally naturally cools to room temperature, Obtain ACFs;
(2)Take 20 mg steps(1)Described in ACFs mix with 0.242 g sodium molybdates, 0.38 g thiocarbamides and be dissolved in 60 mL In distilled water, stir, the reaction solution configured is transferred in 100 mL hydrothermal reaction kettle liners, load hydrothermal reaction kettle Middle reaction, reaction temperature are 210 DEG C, and soaking time is 24 h, and reaction is cooled to room temperature after terminating, and supernatant is removed, mistake Filter, washing, drying obtain MoS2/ACFs;
(3)Take 200 mg steps(2)Described in MoS2/ ACFs is placed in 60 mL cobalt salts, aluminium salt, urea and ammonium fluoride and rubbed You are than being 2:1:25:In 8 mixed solution, stir, the reaction solution configured is transferred in 100 mL hydrothermal reaction kettles In lining, it is fitted into hydrothermal reaction kettle and reacts, reaction temperature is 100 DEG C, and soaking time is 24 h, and reaction is cooled to room after terminating Temperature, supernatant is removed, filter, wash, drying and obtain MoS2/CoAl-LDH/ACFs。
Test case
The present invention have studied the MoS prepared by embodiment 1-32/ CoAl-LDH/ACFs composite photo-catalysts are under visible light Catalytic effect.Dirty organic pollutants are simulated with Congo red solution, its method is:0.1 g embodiments 1-3 is taken to prepare respectively MoS2/ CoAl-LDH/ACFs composite photo-catalysts are put into the mg/L of 80 mL 200 Congo red solution, first in dark ring 30 min are placed under border, to adsorption equilibrium.After the completion of absorption, light-catalyzed reaction, photocatalysis are carried out under the irradiation of 500 W xenon lamps Cheng Zhong, the Congo red solution of 4 mL is taken out as sample every 10 min, 5 min are centrifuged under 4000 r/min, with light splitting Photometer tests the absorbance of Congo red solution under different catalysis times and is converted into concentration, to characterize degradation effect, specific knot Fruit sees Fig. 1.Fig. 1 is degradation rate and the relation curve of time when photocatalytic degradation is Congo red under simulated solar light irradiation.By scheming 1 is visible, and three samples are to Congo red degradation rate more than 70%, and the photochemical catalyst wherein prepared by embodiment 3 is in 120 min It is interior that more than 78% is reached to Congo red degradation rate, show that the photochemical catalyst has efficient catalytic effect to congo red, can use In the efficient process of waste water from dyestuff.
The present invention is investigated the MoS prepared by embodiment 32The XRD of/CoAl-LDH/ACFs composite photo-catalyst samples Spectrogram, as shown in Figure 2.Sample is by MoS it can be seen from Fig. 2 XRD spectra2, CoAl-LDH and amorphous activated carbon composition. MoS2Sharp peak is respectively provided with CoAl-LDH, illustrates well-crystallized.The sample prepared by embodiment 3 is also have detected simultaneously SEM schemes and EDS spectrograms, as shown in Figure 3.In Fig. 3(a)It is MoS2The SEM figures of/CoAl-LDH/ACFs composite photo-catalysts, by scheming In it can be seen that ACFs fibers be in hollow tubulose, diameter is about 20 μm, has the MoS of sheet in its superficial growth2And CoAl- LDH, CoAl-LDH size are about 1.5-2 μm;(b)It is(a)In 1 point of EDS spectrograms, as can be seen from Figure containing Co, Al, C, O elements, with reference to XRD spectrum above, it can be seen that CoAl-LDH has been grown on ACF;(c)It is(a)In 2 points of EDS spectrograms, As can be seen from Figure containing elements such as Mo, S, with reference to XRD spectra above, it is known that MoS2Grow on ACFs.
The present invention also have detected the N of the sample prepared by embodiment 32Adsorption/desorption curve and respective aperture distribution curve, As shown in Figure 4.In Fig. 4(a)It can be seen that low-pressure end is inclined to X-axis, and V-type etc. is belonged to by obvious hysteresis loop at mesohigh end Warm line, show to exist in sample a number of mesoporous;In Fig. 4(b)It can be seen that containing substantial amounts of mesoporous, and have a small amount of micro- Hole, illustrate to be successfully prepared the MoS containing micropore Yu mesoporous graded porous structure2/ CoAl-LDH/ACFs composite photocatalysts Agent.The sample specific surface area is 34.04 m2/ g, total pore volume are 0.2 cm3/ g, average pore size are 1.04 nm.

Claims (7)

1. a kind of composite photo-catalyst, it is characterised in that the catalyst is MoS2/ CoAl-LDH/ACFs composite photo-catalysts;Institute The composite photo-catalyst stated is prepared by following methods:
(1)Configure the ZnCl that 75 ~ 85 mL concentration are 95 mg/L2Solution, while 15mg neopelexes are added, by 2g Kapok is put into the solution after time of infusion, takes out drying;
(2)Take step(1)In obtained kapok, it is then heated to 900 DEG C in the environment of logical nitrogen and forged Burn, be then cooled to 300 DEG C, finally naturally cool to room temperature, wash, dry to obtain ACFs;
(3)By 20mg steps(2)The ACFs of middle gained and 0.242 g sodium molybdates, 0.38g thiocarbamides mixed dissolution steam in 55 ~ 65 mL In distilled water, stir;
(4)By step(3)The middle reaction solution configured is transferred in hydrothermal reaction kettle liner, is fitted into hydrothermal reaction kettle and is reacted, Reaction is cooled to room temperature after terminating, and supernatant is removed, and filters, washs, drying and obtain MoS2/ACFs;
(5)Take 200mg steps(4)Described in MoS2/ ACFs is placed in 55 ~ 65 mL cobalt salts, silicon source, urea and ammonium fluoride according to rubbing You are at ratio(2~3):1:25:(8~9)In the mixed solution of composition, stir to obtain mixed reaction solution;
(6)By step(5)Gained mixed reaction solution is transferred in hydrothermal reaction kettle liner, is fitted into hydrothermal reaction kettle and is reacted, reaction Room temperature is cooled to after end, supernatant is removed, filters, wash, drying to MoS2/CoAl-LDH/ACFs。
2. composite photo-catalyst according to claim 1, it is characterised in that it be made of using kapok as biological template, MoS2It is grown in CoAl-LDH on ACFs fibers, micropore and mesoporous graded porous structure is present simultaneously on every fiber.
3. composite photo-catalyst according to claim 1, it is characterised in that the step(1)Dip time is 2h, drying Temperature is 80 DEG C.
4. composite photo-catalyst according to claim 1, it is characterised in that the step(2)Heating speed during middle calcining Rate is 5 DEG C/min, calcination time 1h.
5. composite photo-catalyst according to claim 1, it is characterised in that the step(4)Middle reaction temperature is 210 DEG C, soaking time 24h.
6. composite photo-catalyst according to claim 1, it is characterised in that the step(6)Middle reaction temperature is 100 DEG C, soaking time 10-24h.
7. the application of the composite photo-catalyst described in a kind of claim 1 or 2, it is characterised in that available for catalytic degradation processing Waste water from dyestuff.
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CN107096525B (en) * 2017-05-04 2019-08-27 济南大学 A kind of composite photo-catalyst and its preparation method and application
CN108103766B (en) * 2017-12-29 2021-07-30 澄江市力点科技有限公司 Molybdenum disulfide composite fiber photocatalyst for sewage treatment and preparation method thereof
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