CN111408364B - Pyroelectric catalyst for treating dye sewage at room temperature under alternating cold and heat, and preparation method and application thereof - Google Patents

Pyroelectric catalyst for treating dye sewage at room temperature under alternating cold and heat, and preparation method and application thereof Download PDF

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CN111408364B
CN111408364B CN202010198729.XA CN202010198729A CN111408364B CN 111408364 B CN111408364 B CN 111408364B CN 202010198729 A CN202010198729 A CN 202010198729A CN 111408364 B CN111408364 B CN 111408364B
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ball
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catalyst
pyroelectric
milling
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CN111408364A (en
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胡长征
孙朝中
季瑞
郭晓莹
方亮
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Guilin University of Technology
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Guilin University of Technology
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/16Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/20Vanadium, niobium or tantalum
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/0009Use of binding agents; Moulding; Pressing; Powdering; Granulating; Addition of materials ameliorating the mechanical properties of the product catalyst
    • B01J37/0027Powdering
    • 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
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/467Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
    • C02F1/4672Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electrooxydation
    • 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

Abstract

The invention discloses a pyroelectric catalyst for treating dye sewage at room temperature under alternating cold and heat, and a preparation method and application thereof. High-purity barium carbonate, sodium carbonate, niobium pentoxide and tantalum pentoxide are mixed according to a nominal chemical formula Ba4Na2Nb4Ta6O30(BNNT) burdening according to the stoichiometric ratio, carrying out the procedures of primary ball milling, drying, column pressing, presintering, secondary ball milling and the like, utilizing high-temperature solid phase reaction, and carrying out high-energy ball milling on the final product to prepare BNNT submicron powder. After the heating and cooling are alternately circulated for 30 times at 25-50 ℃, the degradation rate of the dye rhodamine B is more than 99%. The method is low in manufacturing cost, simple in preparation, suitable for large-scale industrial production, has an excellent degradation effect on dye rhodamine B, and has important significance in the aspect of treating dye sewage degradation.

Description

Pyroelectric catalyst for treating dye sewage at room temperature under alternating cold and heat, and preparation method and application thereof
Technical Field
The invention belongs to the field of sewage treatment, relates to a method for degrading dye sewage by adopting a pyroelectric catalyst, and particularly relates to a Ba structure with a tungsten bronze structure4Na2Nb4Ta6O30A method for degrading rhodamine B dye sewage by using a pyroelectric catalyst.
Background
The dye is used as an important chemical raw material and is closely related to human clothes and food inhabitation. But a large amount of dye sewage is generated in the production and use processes of the dye, and the sewage has the characteristics of large water quantity, complex components, deep chroma, difficult degradation and the like. And most dyes have toxicity and carcinogenicity, and seriously affect the natural environment. Effective treatment of dye sewage is a difficult problem in industry development. However, the traditional biochemical treatment of dye sewage has high operation cost and more byproducts, which easily cause secondary pollution of water. Although the photocatalytic treatment degradation is a clean and green sewage treatment method, the photocatalytic efficiency is low, and the actual application of the photocatalytic treatment degradation is restricted due to insufficient response force in a dark environment. Therefore, the method for degrading the dye sewage with green color and high catalytic efficiency is of great significance.
Disclosure of Invention
The nominal chemical formula of the pyroelectric catalyst is Ba4Na2Nb4Ta6O30
In order to realize the purpose, the invention provides a method for degrading dye sewage by alternately cooling and heating at room temperature, which has high degradation efficiency, low production cost and simple treatment. The principle is that the interior of the catalyst is polarized through the change of the environmental temperature, polarization charges appear on the surface of the material macroscopically, and the charges are combined with oxygen and hydroxide ions in dye sewage to generate active particles with strong oxidizing property, so that the organic dye is oxidized and degraded, and the principle is shown in figure 1.
Based on this study, the specific process applied by the present invention: and adding 50mg of BNNT submicron powder into 50mL of rhodamine B solution (the concentration is 5-15 mg/L), degrading under the condition of 25-50 ℃ cold-hot circulation for 6-30 times, performing centrifugal separation, measuring the ultraviolet absorbance of the dye rhodamine B before and after degradation, and calculating the degradation rate of the dye.
The invention has the following advantages: (1) the invention adopts the traditional solid phase method for preparation and uses the high-energy ball mill to prepare the BNNT submicron powder, so that the treatment cost is low, the industrial production is convenient, and the application prospect is wide. (2) The degradation condition is simple, and only room temperature cold-hot circulation is needed. (3) The method has good decolorizing effect when being used for treating dye wastewater, and the efficiency of degrading dye rhodamine B is up to more than 99%. (4) Is environment-friendly and does not cause secondary pollution to water.
Drawings
FIG. 1 shows Ba prepared in an example of the present invention4Na2Nb4Ta6O30The catalytic principle of the pyroelectric catalyst is shown schematically.
FIG. 2 shows Ba prepared according to an embodiment of the present invention4Na2Nb4Ta6O30X-ray spectra of the pyroelectric catalyst.
FIG. 3 shows Ba prepared in an example of the present invention4Na2Nb4Ta6O30Surface microtopography of the pyroelectric catalyst.
FIG. 4 shows Ba prepared by an example of the present invention4Na2Nb4Ta6O30Size distribution of the pyroelectric catalyst particles.
FIG. 5 shows Ba prepared according to an embodiment of the present invention4Na2Nb4Ta6O30And (3) degrading 5mg/L rhodamine B dye solution by using the pyroelectric catalyst, and obtaining an ultraviolet-visible absorption spectrum data graph after different thermal cycle times (from 25-50 ℃). The inset shows the thermal cycling profile.
FIG. 6 shows Ba prepared according to an embodiment of the present invention4Na2Nb4Ta6O30And (3) comparing the degradation efficiency of the pyroelectric catalyst for degrading the RhB dye through thermal cycle times (25-50 ℃) with the degradation efficiency of the RhB dye through thermal catalysis without BNNT.
Detailed Description
Example 1:
BaCO with the purity of 99.99 percent3、Na2CO3、Nb2O5And Ta2O5The raw materials are BaCO according to the stoichiometric ratio3:Na2CO3:Nb2O5:Ta2O5Putting the ingredients in a ball milling tank at a ratio of 4:1:2: 3; selecting a zirconium dioxide ball and a nylon tank; the mass of the added raw materials is 8 percent of that of the grinding ball; the mixing and ball milling time is 24 hours, the rotating speed is 180 r/min, and the ball milling medium is absolute ethyl alcohol; the obtained product is placed inDrying in an oven at 100 ℃ for 4 hours, taking out the compression column, and pre-sintering for 4 hours when the temperature is raised to 1000 ℃ at the heating rate of 5 ℃/min; taking out the pre-sintered powder, grinding, ball-milling for 24 hours by taking absolute ethyl alcohol as a ball-milling medium, uniformly mixing, drying for 4 hours at 100 ℃, grinding into powder, pressing a column, raising the temperature to 1400 ℃ at the heating rate of 5 ℃/min, preserving the temperature for 10 hours in the air atmosphere of a high-temperature furnace, sintering, naturally cooling to room temperature along with the furnace, grinding the prepared sample in an agate mortar, placing the ground sample in a high-energy ball mill at the rotating speed of 300 revolutions per minute, ball-milling for 48 hours by taking absolute ethyl alcohol as a ball-milling medium, drying for 4 hours at 100 ℃, grinding into powder, thus obtaining Ba4Na2Nb4Ta6O30Submicron powder.
Example 2:
BaCO with the purity of 99.99 percent3、Na2CO3、Nb2O5And Ta2O5The raw materials are BaCO according to the stoichiometric ratio3:Na2CO3:Nb2O5:Ta2O5Putting the ingredients in a ball milling tank at a ratio of 4:1:2: 3; selecting a zirconium dioxide ball and a nylon tank; the mass of the added raw materials is 8 percent of that of the grinding ball; the mixing and ball milling time is 24 hours, the rotating speed is 180 r/min, and the ball milling medium is absolute ethyl alcohol; putting the obtained product into a drying oven at 100 ℃ for drying for 4 hours, taking out the pressing column, and raising the temperature to 1100 ℃ at the heating rate of 5 ℃/min for pre-sintering for 4 hours; taking out the presintered powder, grinding, ball-milling with absolute ethyl alcohol as ball-milling medium for 24 hours, uniformly mixing, drying at 100 ℃ for 4 hours, grinding into powder, pressing the column, raising the temperature to 1550 ℃ at the heating rate of 5 ℃/min, keeping the temperature in air atmosphere of a high-temperature furnace for 4 hours, sintering, naturally cooling to room temperature along with the furnace, grinding the prepared sample in an agate mortar, placing in a high-energy ball mill at the rotating speed of 350r/min, ball-milling with absolute ethyl alcohol as ball-milling medium for 36 hours, drying at 100 ℃ for 4 hours, grinding into powder, thus obtaining Ba4Na2Nb4Ta6O30Submicron powder.
Example 3:
BaC with the purity of 99.99 percentO3、Na2CO3、Nb2O5And Ta2O5The raw materials are BaCO according to the stoichiometric ratio3:Na2CO3:Nb2O5:Ta2O5Putting the ingredients in a ball milling tank at a ratio of 4:1:2: 3; selecting a zirconium dioxide ball and a nylon tank; the mass of the added raw materials is 8 percent of that of the grinding ball; the mixing and ball milling time is 24 hours, the rotating speed is 180 r/min, and the ball milling medium is absolute ethyl alcohol; putting the obtained product into a drying oven at 100 ℃ for drying for 4 hours, taking out the compression column, and raising the temperature to 1200 ℃ at the heating rate of 5 ℃/min for pre-sintering for 4 hours; taking out the pre-sintered powder, grinding, ball-milling for 24 hours by taking absolute ethyl alcohol as a ball-milling medium, uniformly mixing, drying for 4 hours at 100 ℃, grinding into powder, pressing a column, raising the temperature to 1500 ℃ at the heating rate of 5 ℃/min, preserving the heat for 6 hours in the air atmosphere of a high-temperature furnace, sintering, naturally cooling to room temperature along with the furnace, grinding the prepared sample in an agate mortar, placing the ground sample in a high-energy ball mill at the rotating speed of 350 revolutions per minute, ball-milling for 24 hours by taking absolute ethyl alcohol as a ball-milling medium, drying for 4 hours at 100 ℃, grinding into powder, thus obtaining Ba4Na2Nb4Ta6O30Submicron powder. XRD powder diffraction analysis was performed on the powder, as shown in FIG. 2, confirming Ba4Na2Nb4Ta6O30The submicron powder has good crystallinity, is a pure-phase tetragonal tungsten bronze structure, and does not generate a second phase. FIGS. 3 and 4 show the surface microscopic morphology of BNNT and the particle size distribution of the powder particles, and the results show that the particle size of BNNT powder is 60-550 nm and the average particle size is 179 nm. Indicating that the BNNT catalyst powder has a submicron size.
Adding 50mg BNNT submicron powder into 50mL of 5mg/L rhodamine B solution, and stirring for one hour in a dark environment to achieve the adsorption-desorption balance between the rhodamine B dye and the BNNT catalyst. And then, under the cold-hot circulation of 25-50 ℃, after every 6 times of circulation, taking 3mL of rhodamine B solution, centrifugally separating, taking supernatant, measuring the absorption peak intensity by an ultraviolet-visible spectrophotometer, and finally, according to a formula D ═ A (A)0-At)/A0X 100% calculation of the dye rhodamine BThe degradation rate D of (A). FIG. 5 is a final ultraviolet absorption spectrum data diagram of rhodamine B, and the degradation rate of dye rhodamine B of BNNT submicron powder after 30 times of cold-hot circulation at 25-50 ℃ is obtained through calculation. FIG. 6 shows the addition of submicron powder Ba4Na2Nb4Ta6O30A comparative graph of the degradation efficiency of the RhB dye degraded by thermal cycle times (25-50 ℃) and the RhB dye degraded by directly carrying out cold-heat exchange without BNNT submicron powder. Indicating Ba4Na2Nb4Ta6O30The submicron powder has a key function in the degradation process.
The above description is only a preferred embodiment of the present invention, and all the equivalent changes and modifications made according to the claims of the present invention should be covered by the present invention.

Claims (3)

1. The application of the pyroelectric catalyst in degrading rhodamine B dye sewage is characterized in that: the material is used for degrading dye rhodamine B under the cold-heat cycle at the temperature of 25-50 ℃, and the catalytic efficiency is 99%;
the nominal chemical formula of the pyroelectric catalyst is Ba4Na2Nb4Ta6O30
The preparation method of the pyroelectric catalyst comprises the following steps:
(1) BaCO with purity of more than 99.9 percent3、Na2CO3、Nb2O5And Ta2O5As starting material, according to BaCO3:Na2CO3:Nb2O5:Ta2O5Proportioning according to the molar ratio of 4:1:2:3, then using absolute ethyl alcohol as a ball milling medium, mixing and ball milling for 24 hours, and drying for 4 hours at 100 ℃ to obtain a dried sample;
(2) pre-sintering the dried sample prepared in the step (1) at 1000-1200 ℃ for 4 hours to prepare a pre-sintered column body;
(3) placing the pre-sintered column body prepared in the step (2) into an agate mortar to be ground into powder, then using absolute ethyl alcohol as a ball milling medium to perform ball milling for 24 hours, uniformly mixing, drying for 4 hours at 100 ℃, and then grindingGrinding into powder, pressing into a column, sintering at 1400-1550 ℃ for 4-10 hours in air atmosphere of a high-temperature furnace, naturally cooling to room temperature along with the furnace, finally grinding the sample, placing the sample into a high-energy ball mill, ball-milling for 24 hours by taking absolute ethyl alcohol as a ball-milling medium, drying at 100 ℃ for 4 hours, and grinding into powder to obtain Ba4Na2Nb4Ta6O30The catalyst powder of (4).
2. The use of claim 1, wherein the pyroelectric catalyst is prepared from high-purity barium carbonate, sodium carbonate, niobium pentoxide and tantalum pentoxide.
3. Use according to claim 1, wherein Ba is produced4Na2Nb4Ta6O30The catalyst powder is prepared by ball-milling zirconium dioxide with a ball diameter of 0.5mm and anhydrous ethanol as a ball-milling medium in a zirconium dioxide ceramic ball-milling tank at a rotation speed of 300-350 r/min for 24-48 h.
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Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101301614A (en) * 2008-07-04 2008-11-12 武汉理工大学 Method for preparing visible light responding tungsten-containing semi-conductor photocatalysis material
CN101773823A (en) * 2010-01-02 2010-07-14 桂林理工大学 Visible light responded composite oxide photocatalyst BaLi2Nb2-xTaxO9 and preparation method thereof
CN102861569A (en) * 2012-10-17 2013-01-09 桂林理工大学 Visible light responsive vanadium-containing garnet structural oxide photocatalyst and preparation method thereof
CN102924078A (en) * 2012-10-22 2013-02-13 天津大学 BCTZ-based perovskite system multi-component lead-free piezoelectric ceramic and preparation method thereof
KR20130037985A (en) * 2011-10-07 2013-04-17 울산대학교 산학협력단 Electrostrictive lead-free ceramic composition and preparation method thereof
CN103191716A (en) * 2013-04-17 2013-07-10 桂林理工大学 Corundum structured composite oxide photocatalyst Mg4Nb2-xTaxO9 and preparation method thereof
CN105126811A (en) * 2015-07-29 2015-12-09 河南大学 Sodium columbate photocatalytic material with specific morphology and its preparation method and use
CN106865989A (en) * 2017-01-06 2017-06-20 陕西科技大学 The KNN base energy storage microcrystal glass materials and preparation method of a kind of ultralow dielectric loss
CN110092440A (en) * 2019-05-09 2019-08-06 南昌航空大学 A method of efficient degradation waste water from dyestuff is catalyzed using piezoelectricity
CN110745867A (en) * 2019-11-18 2020-02-04 桂林理工大学 Submicron powder material for printing and dyeing sewage treatment and preparation method thereof
CN110813277A (en) * 2019-10-29 2020-02-21 南昌大学 Photo-thermal synergistic enhanced full-spectrum response heterostructure photocatalyst and preparation thereof

Patent Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101301614A (en) * 2008-07-04 2008-11-12 武汉理工大学 Method for preparing visible light responding tungsten-containing semi-conductor photocatalysis material
CN101773823A (en) * 2010-01-02 2010-07-14 桂林理工大学 Visible light responded composite oxide photocatalyst BaLi2Nb2-xTaxO9 and preparation method thereof
KR20130037985A (en) * 2011-10-07 2013-04-17 울산대학교 산학협력단 Electrostrictive lead-free ceramic composition and preparation method thereof
CN102861569A (en) * 2012-10-17 2013-01-09 桂林理工大学 Visible light responsive vanadium-containing garnet structural oxide photocatalyst and preparation method thereof
CN102924078A (en) * 2012-10-22 2013-02-13 天津大学 BCTZ-based perovskite system multi-component lead-free piezoelectric ceramic and preparation method thereof
CN103191716A (en) * 2013-04-17 2013-07-10 桂林理工大学 Corundum structured composite oxide photocatalyst Mg4Nb2-xTaxO9 and preparation method thereof
CN105126811A (en) * 2015-07-29 2015-12-09 河南大学 Sodium columbate photocatalytic material with specific morphology and its preparation method and use
CN106865989A (en) * 2017-01-06 2017-06-20 陕西科技大学 The KNN base energy storage microcrystal glass materials and preparation method of a kind of ultralow dielectric loss
CN110092440A (en) * 2019-05-09 2019-08-06 南昌航空大学 A method of efficient degradation waste water from dyestuff is catalyzed using piezoelectricity
CN110813277A (en) * 2019-10-29 2020-02-21 南昌大学 Photo-thermal synergistic enhanced full-spectrum response heterostructure photocatalyst and preparation thereof
CN110745867A (en) * 2019-11-18 2020-02-04 桂林理工大学 Submicron powder material for printing and dyeing sewage treatment and preparation method thereof

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
LiBa_4Nb_(3-x)Ta_xO_(12)的光催化性能;张桂玲等;《武汉理工大学学报》;20090815(第15期);第24-26页 *
铌酸盐光催化剂的制备及其应用;胡艳君等;《国外建材科技》;20080215(第01期);第8-12页 *

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