CN110420630A - A kind of black titanium dioxide photochemical catalyst and the preparation method and application thereof - Google Patents

A kind of black titanium dioxide photochemical catalyst and the preparation method and application thereof Download PDF

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CN110420630A
CN110420630A CN201910822203.1A CN201910822203A CN110420630A CN 110420630 A CN110420630 A CN 110420630A CN 201910822203 A CN201910822203 A CN 201910822203A CN 110420630 A CN110420630 A CN 110420630A
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titanium dioxide
mixed liquor
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photochemical catalyst
mixed
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邹国燕
周丽
辛立勋
崔娜欣
张旭
蔡敏
陈桂发
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Shanghai Academy of Agricultural Sciences
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    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01NPRESERVATION OF BODIES OF HUMANS OR ANIMALS OR PLANTS OR PARTS THEREOF; BIOCIDES, e.g. AS DISINFECTANTS, AS PESTICIDES OR AS HERBICIDES; PEST REPELLANTS OR ATTRACTANTS; PLANT GROWTH REGULATORS
    • A01N59/00Biocides, pest repellants or attractants, or plant growth regulators containing elements or inorganic compounds
    • A01N59/16Heavy metals; Compounds 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
    • B01J21/00Catalysts comprising the elements, oxides, or hydroxides of magnesium, boron, aluminium, carbon, silicon, titanium, zirconium, or hafnium
    • B01J21/06Silicon, titanium, zirconium or hafnium; Oxides or hydroxides thereof
    • B01J21/063Titanium; Oxides or hydroxides 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
    • 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
    • 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
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/50Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment
    • 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
    • C02F2101/38Organic compounds containing nitrogen
    • 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
    • C02F2103/007Contaminated open waterways, rivers, lakes or ponds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/10Photocatalysts

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Abstract

The present invention relates to water-treatment technology fields more particularly to a kind of black titanium dioxide photochemical catalyst and the preparation method and application thereof.Preparation method of the invention is hydrolyzed reaction, obtains jelly the following steps are included: will include that the first mixed liquor of titanium source and dehydrated alcohol is mixed with the second mixed liquor including inhibitor, water and dehydrated alcohol;The jelly is calcined under a nitrogen atmosphere, obtains black titanium dioxide photochemical catalyst.The present invention mixes the first mixed liquor with the second mixed liquor, and titanium source is met water and hydrolyzed, and obtains jelly;Jelly is calcined under a nitrogen atmosphere later, calcination process will form Lacking oxygen in titanium dioxide surface, while generate Ti3+, so that the band gap of titanium dioxide is narrowed, so as to which visible light is absorbed and utilized, effectively remove harmful algae in water body.

Description

A kind of black titanium dioxide photochemical catalyst and the preparation method and application thereof
Technical field
The present invention relates to water-treatment technology fields more particularly to a kind of black titanium dioxide photochemical catalyst and preparation method thereof With application.
Background technique
Currently, water body in lake eutrophication is got worse, and cyanobacterial bloom outburst is the important of water eutrophication One of characterization and China or even the whole world water environmental problems the most serious.The freshwater lake and reservoir in China 66% are long-term By the infringement of cyanobacterial bloom.The generation of wawter bloom can cause the generation of the deaths by suffocation such as fish and aquatic animal, toxic gas With the forfeiture of water ecosystem function etc., human health is directly endangered.The Control Technology of harmful algae mainly include physical method, Chemical method and bioanalysis, but in place of these traditional algae removal technologies all Shortcomings, cause the prevention and control process of wawter bloom algae especially It is difficult, it shoulders heavy responsibilities.
Nano material photocatalysis technology provides new thinking for the improvement of water environment pollution, a large number of studies show that, it utilizes Nano material photocatalytic process can successfully inhibit the growth of bloom blue algae, or even gradually degrade frustule and detrimental metabolic production Object, wherein TiO2Because having the unique performance such as low in cost, nonhazardous, high-efficient to obtain extensive research.But TiO2Band gap Wider, light abstraction width is confined to the ultraviolet region that wavelength is less than 387nm, to limit TiO2The efficiency of light energy utilization, especially It is that cannot make full use of visible light abundant in nature.Currently, TiO2Study on the modification focus on widening its visible spectrum Response range is to increase the efficiency of light energy utilization, but in terms of current research achievement, it is seen that the utilization rate of solar energy is not high, needs The modification method for preparing of innovation improves the utilization rate of visible light, is answered with accelerating popularization of the photocatalysis technology in terms of controlling algae algal control With.
The appearance of black titanium dioxide overcomes the above problem, and there is excellent visible absorption performance and surface reaction to live Property, therefore there is stronger photocatalysis characteristic.The representative preparation method of black titanium dioxide has hydrogen reduction method, aluminothermic reduction Method, solution-evaporation, but there are the drawbacks such as security risk and the high requirements on the equipment for the above method.How to utilize mild simple Energy band is narrow for method preparation, the black titanium dioxide more than defect is the key that promote photocatalysis technology except algae field is applied.
Summary of the invention
The purpose of the present invention is to provide a kind of black titanium dioxide photochemical catalyst and the preparation method and application thereof, the present invention The black titanium dioxide photochemical catalyst band gap of preparation is relatively narrow, can fully absorb visible light, can effectively remove the nocuousness in water body Algae, and preparation method is simple, mild.
In order to achieve the above-mentioned object of the invention, the present invention the following technical schemes are provided:
The present invention provides a kind of preparation methods of black titanium dioxide photochemical catalyst, comprising the following steps:
By the first mixed liquor for including titanium source and dehydrated alcohol and the second mixed liquor including inhibitor, water and dehydrated alcohol Mixing, is hydrolyzed reaction, obtains jelly;
The jelly is calcined under a nitrogen atmosphere, obtains black titanium dioxide photochemical catalyst.
Preferably, the titanium source includes butyl titanate or titanium tetrachloride;The inhibitor includes concentrated hydrochloric acid or concentrated nitric acid.
Preferably, in the mixed system of the hydrolysis, titanium source, inhibitor, water and dehydrated alcohol molar ratio be (3.0~4.0): 1:(23.0~24.0): (42.0~43.0).
It preferably, further include urea in first mixed liquor;When further including urea in the first mixed liquor, the hydrolysis In the mixed system of reaction, titanium source, urea, inhibitor, water and dehydrated alcohol molar ratio be (3.0~4.0): (0.28~ 1.11): 1:(23.0~24.0): (42.0~43.0).
Preferably, it is stirred in the hydrolysis reaction using glass bar, the time of hydrolysis is 1~3min.
Preferably, the temperature of the calcining is 400~600 DEG C, and soaking time is 2~4h.
It preferably, further include being dried to jelly before the calcining, the temperature of the drying is 60~80 DEG C, the time For 10~12h.
Preferably, the mode first mixed liquor mixed with second mixed liquor are as follows: the second mixed liquor is added dropwise It is mixed into the first mixed liquor.
The present invention provides the black titanium dioxide photochemical catalysts that preparation method described in above scheme is prepared.
The present invention provides black titanium dioxide photochemical catalysts described in above scheme in visible light catalytic removal algae Using.
The present invention provides a kind of preparation methods of black titanium dioxide photochemical catalyst, comprising the following steps: will include titanium First mixed liquor of source and dehydrated alcohol is mixed with the second mixed liquor for including inhibitor, water and dehydrated alcohol, is hydrolyzed anti- It answers, obtains jelly;The jelly is calcined under a nitrogen atmosphere, obtains black titanium dioxide photochemical catalyst.This hair Bright to mix the first mixed liquor with the second mixed liquor, titanium source is met water and is hydrolyzed, and obtains jelly;Later by jelly in nitrogen Under the conditions of calcined, calcination process will form Lacking oxygen in titanium dioxide surface, while generate Ti3+, make the band of titanium dioxide Gap narrows, and so as to which visible light is absorbed and utilized, effectively removes the harmful algae in water body.Embodiment the result shows that, this hair The minimum band-gap energy of bright black titanium dioxide obtained is 1.47eV, under visible light, to microcystic aeruginosa chlorophyll after 10h Degradation rate up to 72.5%.
In addition, black titanium dioxide photochemical catalyst prepared by the present invention also have under visible light illumination it is reusable, The advantages that stability is good.
Detailed description of the invention
Fig. 1 is 0.6N/b-TiO made from embodiment 12The SEM and TEM of photochemical catalyst scheme;
Fig. 2 is the XRD diagram of difference N doping black titanium dioxide photochemical catalyst made from embodiment 1;
Fig. 3 is the energy band gap diagram according to drawn by the UV-vis data of different N doping black titanium dioxides in embodiment 1;
Fig. 4 is removal of the black titanium dioxide of difference N doping amount made from embodiment 1 to microcystic aeruginosa chlorophyll Effect;
Fig. 5 is 0.6N-N obtained in embodiment 22XRD diagram of the photochemical catalyst under different calcination temperatures;
Fig. 6 is the XRD diagram of the titanium dioxide obtained by calcining at 500 DEG C under different calcination atmospheres;
Fig. 7 is energy band gap diagram drawn by the UV-vis data of the white titania according to obtained by comparative example;
Fig. 8 be prepared under different calcination temperatures according to embodiment 2 obtained by 0.6N-N2The UV-vis number of black titanium dioxide According to drawn energy band gap diagram;
Fig. 9 is removal effect of the titanium dioxide made from embodiment 2 and comparative example to microcystic aeruginosa chlorophyll;
Figure 10 is 0.6N/b-TiO2Recycling three times remove algae effect.
Specific embodiment
The present invention provides a kind of preparation methods of black titanium dioxide photochemical catalyst, comprising the following steps:
By the first mixed liquor for including titanium source and dehydrated alcohol and the second mixed liquor including inhibitor, water and dehydrated alcohol Mixing, is hydrolyzed reaction, obtains jelly;
The jelly is calcined under a nitrogen atmosphere, obtains black titanium dioxide photochemical catalyst.
The present invention will include the first mixed liquor of titanium source and dehydrated alcohol and include the second of inhibitor, water and dehydrated alcohol Mixed liquor mixing, is hydrolyzed reaction, obtains jelly.In the present invention, the titanium source preferably includes butyl titanate or four Titanium chloride, more preferably butyl titanate;The inhibitor preferably includes concentrated hydrochloric acid or concentrated nitric acid, more preferably concentrated hydrochloric acid.In In the present invention, the concentration of the concentrated hydrochloric acid is preferably 12mol/L;The concentration of the concentrated nitric acid is preferably 16mol/L.The present invention adds Inhibiting can inhibit the hydrolysis rate of titanium source, avoid hydrolyzing the too fast performance to photochemical catalyst and have an adverse effect.
In the present invention, first mixed liquor is preferably mixed to get by titanium source and dehydrated alcohol.In the present invention, described Mixing preferably carries out under agitation, and the rate of the stirring is preferably 300~500rpm, and the time of stirring is preferably 1~ 3h。
In the present invention, it is also preferable to include urea for first mixed liquor.When first mixed liquor further includes urea, The preparation of first mixed liquor preferably includes following steps: urea being added in dehydrated alcohol, after stirring, continuously adds titanium Source simultaneously continues to stir, and obtains the first mixed liquor.In the present invention, the rate of the stirring is preferably 300~500rpm.In this hair In bright, total mixing time is preferably controlled in 1~3h.
In the present invention, second mixed liquor is preferably mixed to get by inhibitor, water and dehydrated alcohol.In the present invention In, the mixing preferably carries out under agitation, and the rate of the stirring is preferably 300~500rpm, and the time of stirring is excellent It is selected as 1~3h.
After obtaining the first mixed liquor and the second mixed liquor, the present invention mixes first mixed liquor and second mixed liquor It closes, obtains hydrolysis reaction system.In the present invention, in the hydrolysis reaction system, titanium source, inhibitor, water and dehydrated alcohol Molar ratio is preferably (3.0~4.0): 1:(23.0~24.0): (42.0~43.0), more preferably 3.43:1:23.13: 42.93.When further including urea in first mixed liquor, titanium source in the hydrolysis reaction system, urea, inhibitor, water and The molar ratio of dehydrated alcohol is preferably (3.0~4.0): (0.28~1.11): 1:(23.0~24.0): (42.0~43.0), more Preferably 3.43:(0.28~1.11): 1:23.13:42.93.In the present invention, the dehydrated alcohol is in the first mixed liquor and Capacity distribution in two mixed liquors is preferably 2:1.
In the present invention, the mode that first mixed liquor is mixed with second mixed liquor is preferred are as follows: by the second mixing Drop is added in the first mixed liquor and is mixed.In the present invention, the rate of the dropwise addition is preferably (3~4) mL/min.This hair It is bright to be conducive to react more uniform by the way of being added dropwise, and reaction speed is controlled, guarantee complete hydrolysis.Mixing of the present invention It does not use any stirring condition in the process, if mixing under agitation, will lead to the second mixed liquor and be not added that finish will Form white solid.
After obtaining hydrolysis reaction system, reaction is hydrolyzed in the hydrolysis reaction system by the present invention, obtains jelly.In In the present invention, preferably it is stirred using glass bar in the hydrolysis reaction, the time of hydrolysis is preferably 1~ 3min.Timing the time of hydrolysis of the present invention refers to after the first mixed liquor is mixed with the second mixed liquor, is arrived Form the time of jelly.The present invention is stirred using glass bar compared to for mechanical stirring, and stirring rate is more slow, no It will form and continuously stir, be conducive to titanium source and gradually hydrolyze, react more abundant.The present invention is not special to the rate of the stirring It is required that, it can be ensured that hydrolysis sufficiently carries out, and 1~3min of stirring can form jelly.In specific reality of the invention It applies in example, stirring rate 30rpm.In hydrolytic process of the present invention, titanium source is hydrolyzed, and generates the forerunner of titanium dioxide Body.When in raw material further including urea, in the hydrolytic process, titanium source is hydrolyzed, and generates the presoma of titanium dioxide, and is urinated It is plain then be dissolved in water, generate NH4+It is dispersed in jelly.
After obtaining jelly, the present invention calcines the jelly under a nitrogen atmosphere, obtains black titanium dioxide Photochemical catalyst.
Before calcining, it is also preferable to include jelly is successively dried and ground by the present invention.In the present invention, the drying Temperature be preferably 60~80 DEG C, the time is preferably 10~12h.The present invention does not have particular/special requirement to the partial size after the grinding, Those skilled in the art rule of thumb control the degree of grinding.
In the present invention, the temperature of the calcining is preferably 400~600 DEG C, and more preferably 500 DEG C;Soaking time is preferred For 2~4h.The present invention preferably is selected from the temperature that room temperature rises to calcining, and heating rate is preferably 4~6 DEG C/min.When heating rate mistake When fast, the possible uneven heating of sample generates distortion of lattice, lattice is caused to can increase, reduces sample crystallization;If heating rate mistake Low, the retention time is too long under low temperature procedure, and it is not high to may cause activity.The present invention calcines under a nitrogen atmosphere, dioxy Change titanium precursors hydrolysis to generate titanium dioxide and form Lacking oxygen in titanium dioxide surface, while generating Ti3+, make titanium dioxide Band gap narrows, so as to which visible light is absorbed and utilized.
When raw material also contains urea, the N in calcination process from urea can enter TiO2In lattice, formed Ti-N or Person's N-O key, further promotes the band gap of titanium dioxide to narrow.It, can be in catalyst surface due to being calcined in nitrogen atmosphere Form Ti3+The defects of/Lacking oxygen, so obtained catalyst is in black.
The present invention provides the black titanium dioxide photochemical catalysts that preparation method described in above scheme is prepared.In this hair In bright, the doping of the nitrogen is determined by above-mentioned preparation method;When for N doping, nitrogen-atoms is preferably incorporated in TiO2Lattice In.In the present invention, the partial size of the black titanium dioxide photochemical catalyst is preferably 10~20nm.
The present invention provides black titanium dioxide photochemical catalysts described in above scheme in visible light catalytic removal algae Using.
In the present invention, the application preferably includes following steps: by black titanium dioxide photochemical catalyst and containing algae Water mixing carries out light-catalyzed reaction under visible light conditions.In the present invention, the black titanium dioxide photochemical catalyst is in water Concentration in body is preferably 0.1~0.3g/L;The algae is preferably microcystic aeruginosa;The OD of the algae680Value is preferably 0.1~0.3, number of cells is preferably (1.0~4.0) × 106Cell/mL, chlorophyll concentration are preferably 0.2~0.9mg/L.
In the present invention, the temperature of the light-catalyzed reaction is preferably 25~30 DEG C;The time of the light-catalyzed reaction is excellent It is selected as 8~10h.Light-catalyzed reaction of the present invention preferably carries out under agitation, and the rate of the stirring is preferably 300~ 500rpm。
The present invention does not have particular/special requirement, the visible light in any source to the source of the visible light.Of the invention In specific embodiment, preferably using xenon lamp as light source, and the visible light that wavelength is greater than 420nm is obtained using edge filter.
Below with reference to embodiment to black titanium dioxide photochemical catalyst provided by the invention and the preparation method and application thereof into Row detailed description, but they cannot be interpreted as limiting the scope of the present invention.
Embodiment 1
(1) 400rpm in different quality urea (0,0.2,0.4,0.6,0.8g) addition 20mL dehydrated alcohol is weighed respectively to stir 1h is mixed, 14mL butyl titanate is then added, continues 400rpm and stirs 1h, form the first mixed liquor;
(2) concentrated hydrochloric acid 1mL, deionized water 5mL and 10mL dehydrated alcohol are stirred at 400rpm 1h, forms the second mixing Liquid;
(3) the second mixed liquor is added in the first mixed liquor dropwise (3mL/min), is stirred to form white size with glass bar Shape substance;
(4) white gum substance is placed in 80 DEG C of baking ovens dry 12h, grinding forms powdery white substance;
(5) whiteness of different N doping amounts is placed in the tube furnace in nitrogen atmosphere, 4 DEG C/min is warming up to 500 DEG C, 2h is kept the temperature, black titanium dioxide photochemical catalyst is formed, is denoted as 0N/b-TiO respectively2、0.2N/b-TiO2、0.4N/b-TiO2、 0.6N/b-TiO2、0.8N/b-TiO2
In the present embodiment, (0N/b-TiO in the black titanium dioxide of different N doping amounts used2、0.2N/b-TiO2、 0.4N/b-TiO2、0.6N/b-TiO2、0.8N/b-TiO2), the molar ratio of urea and butyl titanate is respectively 0,0.0033: 0.04、0.0067:0.04、0.0100:0.04、0.0133:0.04。
Fig. 1 is 0.6N/b-TiO made from the embodiment of the present invention 12The SEM and TEM of photochemical catalyst scheme, and wherein a is SEM figure, B is TEM figure.As shown in Figure 1, black titanium dioxide photochemical catalyst is in uniform spherical structure, and particle diameter distribution is in 12nm or so.
Fig. 2 is the XRD diagram of difference N doping black titanium dioxide photochemical catalyst made from the embodiment of the present invention 1.It can by Fig. 2 Know occur the titanium dioxide of rutile and anatase in black titanium dioxide photochemical catalyst, and can be due to N doping amount Difference and the object Phase Proportion of the rutile that generates and anatase is different, so as to cause different photocatalysis performances.
Fig. 3 is the energy band according to drawn by the UV-vis data of different N doping black titanium dioxides in the embodiment of the present invention 1 Gap figure.From the figure 3, it may be seen that N doping influences the band-gap energy of black titanium dioxide, wherein 0.6N doping is best, the band of resulting materials Gap can be minimum, is 1.47eV, and 0.4N adulterates the band-gap energy highest of resulting black titanium dioxide, is 1.59eV.Band-gap energy is got over Small this material of explanation is easier by excited by visible light, helps to improve photocatalysis performance.With the band-gap energy of ordinary titanium dioxide 3.2eV is compared, and band-gap energy is substantially reduced.
Application examples 1
Black titanium dioxide (0~0.8N/b-TiO of the different N doping amounts of Example 12), 20mg is respectively taken, is added respectively To 100mL, OD680Value for 0.2 algae solution in, be uniformly mixed, be placed under xenon lamp (λ > 420nm, optical power 50W), in 25 DEG C, Light-catalyzed reaction 10h is carried out under conditions of 400rpm, completes the removal to harmful algae, is to investigate with frustule Determination of Chlorophyll content Index.
The algae solution under radiation of visible light not add any catalyst is as blank group.
Fig. 4 is that the black titanium dioxide of the different N doping amounts prepared in the embodiment of the present invention 1 is green to microcystic aeruginosa leaf The removal effect of element.As shown in Figure 4, in the case where no catalysis material, it is seen that light is unobvious to microcystic aeruginosa removal effect. With the addition of black titanium dioxide photochemical catalyst, the degradation efficiency of frustule Determination of Chlorophyll is improved, wherein 0.6N/b-TiO2's Except algae effect is best, 72.5% has been reached to the degradation rate of microcystic aeruginosa chlorophyll after the 10h that degrades.
By the result in above-mentioned Fig. 1~4 it is found that the method system that the present invention is calcined by simple collosol and gel and nitrogen atmosphere The standby black titanium dioxide photochemical catalyst formed has the characteristics that uniform particle sizes, rutile/anatase mix, and 0.6N is adulterated The band-gap energy that has of black titanium dioxide is minimum, photocatalytic degradation effect is optimal.
Embodiment 2
Black titanium dioxide is prepared under different calcination temperatures, comprising the following steps:
(1) it weighs different quality urea (0,0.6g) respectively to be added in 20mL dehydrated alcohol, 400rpm stirs 1h, then adds Enter 14mL butyl titanate, continues 400rpm and stir 1h, form the first mixed liquor;
(2) concentrated hydrochloric acid 1mL, deionized water 5mL and 10mL dehydrated alcohol are stirred at 400rpm 1h, forms the second mixing Liquid;
(3) second mixed liquor is added in the first mixed liquor dropwise (4mL/min), stirred with glass bar to be formed it is white Color colloid substance;
(4) white gum substance is placed in 80 DEG C of baking ovens dry 12h, grinding forms powdery white substance;
(5) whiteness of different N doping amounts is placed in the tube furnace in nitrogen atmosphere, 4 DEG C/min is warming up to 400, 500,600 DEG C, 2h is kept the temperature, is formed under nitrogen atmosphere and calcines resulting black titanium dioxide, be denoted as 0.6N-N respectively2(400℃)、 0.6N-N2(500℃)、0.6N-N2(600℃)、0N-N2(500℃)。
Comparative example
Calcining prepares titanium dioxide in air atmosphere:
The whiteness for the different N doping amounts that step (4) in embodiment 2 obtains is placed in Muffle furnace, 4 DEG C/min liter Temperature keeps the temperature 2h to 500 DEG C, and gained white titania is denoted as 0N-AIR (500 DEG C), 0.6N-AIR (500 DEG C).
Fig. 5 is 0.6N-N obtained in the embodiment of the present invention 22XRD diagram of the photochemical catalyst under different calcination temperatures.By scheming 5 it is found that under a nitrogen atmosphere, with the raising of calcination temperature, the anatase titania ratio of generation increases.
Fig. 6 is the XRD diagram of the titanium dioxide obtained by calcining at 500 DEG C under different calcination atmospheres, and titanium dioxide sample is specific Are as follows: the 0.6N-N of embodiment 22(500℃)、0N-N20N-AIR (500 DEG C), the 0.6N-AIR (500 of (500 DEG C) and comparative example ℃).It will be appreciated from fig. 6 that black titanium dioxide made under nitrogen atmosphere and the white titania prepared under air atmosphere In there is the titanium dioxide of rutile and anatase, and in the white titania calcined in air of anatase crystal Proportion is greater than in nitrogen atmosphere proportion in black titanium dioxide obtained by calcining.
Fig. 7 is energy band gap diagram drawn by the UV-vis data of the white titania according to obtained by comparative example;
Fig. 8 be prepared under different calcination temperatures according to embodiment 2 obtained by 0.6N-N2Black titanium dioxide UV-vis data Drawn energy band gap diagram.As shown in Figure 8, calcination temperature influences band-gap energy size, 0.6N-N2(400℃)、0.6N-N2(500℃)、 0.6N-N2The band-gap energy of (600 DEG C) is respectively 2.58eV, 1.47eV and 1.53eV.Calcination temperature is 500 DEG C, and resulting light is urged The band-gap energy of agent is minimum.As shown in Figure 7, under 500 DEG C of calcination temperatures, 0N-AIR (500 DEG C), 0.6N-AIR (500 DEG C) band Gap can be respectively 2.51eV and 2.50eV, hence it is evident that be greater than calcining gained photochemical catalyst in a nitrogen atmosphere.Illustrate that calcination temperature is 500 DEG C, calcination atmosphere is that the band-gap energy of black titanium dioxide obtained by nitrogen is minimum.
Application examples 2
Take titanium dioxide (0N-AIR (500 DEG C), 0.6N-AIR (500 DEG C), 0.6N- prepared in comparative example and embodiment 2 N2(400℃)、0.6N-N2(500℃)、0.6N-N2(600℃)、0N-N2(500 DEG C)), 20mg is respectively taken, is respectively added to 100mL、OD680Value for 0.2 algae solution in, be uniformly mixed, be placed under xenon lamp (λ > 420nm, optical power 50W), in 25 DEG C, Light-catalyzed reaction 10h is carried out under conditions of 400rpm, completes the removal to harmful algae, is to investigate with frustule Determination of Chlorophyll content Index.
Fig. 9 is removal effect of the titanium dioxide made from the embodiment of the present invention 2 and comparative example to microcystic aeruginosa chlorophyll. As shown in Figure 9, it calcines in air atmosphere and in (400 DEG C) of the low temperature resulting titanium dioxide of calcining except algae effect is unobvious, and In a nitrogen atmosphere calcine and calcination temperature at 500 and 600 DEG C obtained by titanium dioxide significantly improve except algae effect, optimal material Material is 0.6N-N2(500℃)。
By the result in above-mentioned Fig. 5~9 it is found that calcination atmosphere and calcination temperature influence the object Phase Proportion and band of photochemical catalyst Gap energy size, to finally influence to remove algae effect.It is 0.6N-N that gained, which removes the highest photochemical catalyst of algae efficiency, in embodiment 22 Result obtained in (500 DEG C) and embodiment 1, embodiment 2 is identical, illustrates 0.6N-N2(500 DEG C) can be used as most optimum materials into One step is investigated.
Application examples 3
Investigate optimal photochemical catalyst 0.6N/b-TiO2Except the stability during algae, comprising the following steps: take 20mg optimal Photochemical catalyst 0.6N/b-TiO2, it is added to 100mL, OD680Value for 0.2 algae solution in, be uniformly mixed, be placed in xenon lamp (λ > 420nm, optical power 50W) under, light-catalyzed reaction 10h is carried out under conditions of 25 DEG C, 400rpm, harmful algae is gone in completion It removes, using the chlorophyll content extracted in frustule as inspection target.And after the completion of reaction, 5000rpm is centrifugated photocatalysis Clear water and washes of absolute alcohol 3 times are used in agent respectively, after 80 DEG C of oven dryings, repeat next time except algae is tested, repeat altogether 3 times.After per treatment, alga-killing rate is calculated as inspection target using the chlorophyll extracted in frustule, the results are shown in Figure 10.
Figure 10 is most optimum materials 0.6N/b-TiO of the present invention2Recycling three times remove algae effect.As shown in Figure 10, pass through After 3 cyclic tests, 0.6N/b-TiO of the present invention2Alga-killing rate after photochemical catalyst reaction 10h is under the 78.5% of first time 66.8% is dropped to, only has dropped 11.7%.This illustrates that black titanium dioxide photochemical catalyst of the invention has excellent stability, It is reusable.
As seen from the above embodiment, the present invention provides a kind of black titanium dioxide photochemical catalyst and preparation method thereof with answer With, it is not only mild using the method for the present invention, simple, and the band gap for the black titanium dioxide being prepared narrows, and can be absorbed Using visible light, the harmful algae in water body is effectively removed.In addition, black titanium dioxide photochemical catalyst prepared by the present invention also has Have the advantages that reusable, stability is good under visible light illumination.
The above is only a preferred embodiment of the present invention, it is noted that for the ordinary skill people of the art For member, various improvements and modifications may be made without departing from the principle of the present invention, these improvements and modifications are also answered It is considered as protection scope of the present invention.

Claims (10)

1. a kind of preparation method of black titanium dioxide photochemical catalyst, which comprises the following steps:
The first mixed liquor including titanium source and dehydrated alcohol is mixed with the second mixed liquor for including inhibitor, water and dehydrated alcohol It closes, reaction is hydrolyzed, obtains jelly;
The jelly is calcined under a nitrogen atmosphere, obtains black titanium dioxide photochemical catalyst.
2. preparation method according to claim 1, which is characterized in that the titanium source includes butyl titanate or four chlorinations Titanium;The inhibitor includes concentrated hydrochloric acid or concentrated nitric acid.
3. preparation method according to claim 1 or 2, which is characterized in that in the mixed system of the hydrolysis, titanium Source, inhibitor, water and dehydrated alcohol molar ratio be (3.0~4.0): 1:(23.0~24.0): (42.0~43.0).
4. preparation method according to claim 1, which is characterized in that further include urea in first mixed liquor;When When further including urea in one mixed liquor, in the mixed system of the hydrolysis, titanium source, urea, inhibitor, water and dehydrated alcohol Molar ratio be (3.0~4.0): (0.28~1.11): 1:(23.0~24.0): (42.0~43.0).
5. preparation method according to claim 1, which is characterized in that carried out in the hydrolysis reaction using glass bar Stirring, the time of hydrolysis are 1~3min.
6. preparation method according to claim 1, which is characterized in that the temperature of the calcining is 400~600 DEG C, heat preservation Time is 2~4h.
7. preparation method according to claim 1 or 6, which is characterized in that further include being carried out to jelly before the calcining Drying, the temperature of the drying are 60~80 DEG C, and the time is 10~12h.
8. preparation method according to claim 1, which is characterized in that by first mixed liquor and second mixed liquor Mixed mode are as follows: the second mixed liquor is added drop-wise in the first mixed liquor and is mixed.
9. the black titanium dioxide photochemical catalyst that any one of claim 1~8 preparation method is prepared.
10. application of the black titanium dioxide photochemical catalyst described in claim 9 in visible light catalytic removal algae.
CN201910822203.1A 2019-09-02 2019-09-02 A kind of black titanium dioxide photochemical catalyst and the preparation method and application thereof Pending CN110420630A (en)

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Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110790307A (en) * 2019-11-27 2020-02-14 上海纳米技术及应用国家工程研究中心有限公司 Preparation method of colored titanium dioxide, product and application thereof
CN111359642A (en) * 2020-03-17 2020-07-03 北京大学 Semiconductor broad-spectrum bactericidal antiviral composite material, preparation method and preparation method
CN111545184A (en) * 2020-03-31 2020-08-18 上海电力大学 Preparation method of oxygen-enriched vacancy titanium dioxide, product and application thereof
CN113304742A (en) * 2021-04-30 2021-08-27 昆明理工大学 Ti3+Self-doping TiO2Preparation method of activated carbon-supported photocatalytic material
CN113546615A (en) * 2021-07-29 2021-10-26 常州大学 Bi2WO6/Black-TiO2Composite catalyst and preparation method and application thereof
CN113663664A (en) * 2021-08-10 2021-11-19 常州大学 RuTe2/B-TiO2Preparation method of material and application of material in photocatalytic degradation of antibiotics
CN114314964A (en) * 2021-12-20 2022-04-12 东珠生态环保股份有限公司 Method for controlling growth of filamentous algae to improve ornamental value of landscape water body
WO2023108824A1 (en) * 2021-12-15 2023-06-22 梁显庭 Nano photocatalytic marine antifouling and anticorrosive coating and preparation method therefor

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102258996A (en) * 2010-05-28 2011-11-30 张旭星 Method for preparing molybdenum-doped nano titanium dioxide by sol-gel process
US20140011674A1 (en) * 2012-07-09 2014-01-09 National Chi Nan University Process of producing a titanium dioxide-based photocatalyst used for degradation of organic pollutants
CN103964503A (en) * 2014-05-27 2014-08-06 新疆大学 Preparation method of black titanium dioxide
CN107837800A (en) * 2017-10-27 2018-03-27 南京理工大学 A kind of Titanium Dioxide ozonisation catalyst and preparation, denitration application
CN108675383A (en) * 2018-05-18 2018-10-19 安徽安成工业设备有限公司 The method for preventing bacterium algae in water body

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102258996A (en) * 2010-05-28 2011-11-30 张旭星 Method for preparing molybdenum-doped nano titanium dioxide by sol-gel process
US20140011674A1 (en) * 2012-07-09 2014-01-09 National Chi Nan University Process of producing a titanium dioxide-based photocatalyst used for degradation of organic pollutants
CN103964503A (en) * 2014-05-27 2014-08-06 新疆大学 Preparation method of black titanium dioxide
CN107837800A (en) * 2017-10-27 2018-03-27 南京理工大学 A kind of Titanium Dioxide ozonisation catalyst and preparation, denitration application
CN108675383A (en) * 2018-05-18 2018-10-19 安徽安成工业设备有限公司 The method for preventing bacterium algae in water body

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
WEI SHUNHANG ET AL.,: ""One-step synthetic approach for core-shelled black anatase titania with high visible light photocatalytic performance"", 《CHEMICAL ENGINEERING JOURNAL》 *

Cited By (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
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CN111359642A (en) * 2020-03-17 2020-07-03 北京大学 Semiconductor broad-spectrum bactericidal antiviral composite material, preparation method and preparation method
CN111359642B (en) * 2020-03-17 2021-06-11 北京大学 Semiconductor broad-spectrum bactericidal antiviral composite material, preparation method and preparation method
CN111545184A (en) * 2020-03-31 2020-08-18 上海电力大学 Preparation method of oxygen-enriched vacancy titanium dioxide, product and application thereof
CN113304742A (en) * 2021-04-30 2021-08-27 昆明理工大学 Ti3+Self-doping TiO2Preparation method of activated carbon-supported photocatalytic material
CN113304742B (en) * 2021-04-30 2023-09-29 昆明理工大学 Activated carbon supported Ti 3+ Self-doping TiO 2 Preparation method of photocatalytic material
CN113546615A (en) * 2021-07-29 2021-10-26 常州大学 Bi2WO6/Black-TiO2Composite catalyst and preparation method and application thereof
CN113663664A (en) * 2021-08-10 2021-11-19 常州大学 RuTe2/B-TiO2Preparation method of material and application of material in photocatalytic degradation of antibiotics
CN113663664B (en) * 2021-08-10 2022-09-27 常州大学 RuTe 2 /B-TiO 2 Preparation method of material and application of material in photocatalytic degradation of antibiotics
WO2023108824A1 (en) * 2021-12-15 2023-06-22 梁显庭 Nano photocatalytic marine antifouling and anticorrosive coating and preparation method therefor
CN114314964A (en) * 2021-12-20 2022-04-12 东珠生态环保股份有限公司 Method for controlling growth of filamentous algae to improve ornamental value of landscape water body
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