CN106807408A - Ce(IO3)4Application - Google Patents
Ce(IO3)4Application Download PDFInfo
- Publication number
- CN106807408A CN106807408A CN201510851367.9A CN201510851367A CN106807408A CN 106807408 A CN106807408 A CN 106807408A CN 201510851367 A CN201510851367 A CN 201510851367A CN 106807408 A CN106807408 A CN 106807408A
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- China
- Prior art keywords
- catalyst
- application
- activity
- organic dye
- degradation
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- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J27/00—Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
- B01J27/06—Halogens; Compounds thereof
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/308—Dyes; Colorants; Fluorescent agents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2305/00—Use of specific compounds during water treatment
- C02F2305/10—Photocatalysts
Abstract
The invention discloses a kind of Ce (IO3)4Application, the application example of this compound is provided first., used as catalyst, can degrade organic dye pollutant under the room temperature condition of complete lucifuge for it.Ce(IO3)4The catalytic degradation rhodamine B under the conditions of complete lucifuge(RhB)And methyl orange(MO)The activity of dyestuff, hence it is evident that higher than the commodity titanium dioxide under radiation of visible light(P25)Photochemical catalyst.Ce (IO of the present invention3)4During catalytic degradation dyestuff, it is higher to be not required to illumination, activity, and its preparation method is simple, preparation condition gentle, is conducive to popularization and application.
Description
Technical field
The invention belongs to technical field of environment pollution control, it is related to Ce (IO3)4Compound exists as a kind of new catalyst
Application in degradating organic dye pollutant.
Background technology
With the increase of population, global printing and dyeing industry size constantly expands, a large amount of organic dyestuff of industry discharge
Pollutant, it has also become the important sources of whole world water pollution.Photocatalitic Technique of Semiconductor can directly utilize sunshine at room temperature
By dyestuff contaminant efficiently oxidative degradation.Therefore, by photocatalysis technology, sunshine is made full use of to carry out degradation of dye pollutant
It is a beneficial way of Enviromental Pollution Treatment.Because ultraviolet light only accounts for 4% of sunshine gross energy or so, and visible ray is accounted for
46% or so, so it is critical only that using the visible ray in sunshine using solar energy.Therefore, it is seen that the light of photoresponse type is urged
Agent has important application prospect in current field of environmental improvement.However, because the limitation of band structure, along with light high
Raw Carrier recombination rate, it is seen that the activity and durability of photocatalyst for degrading dyestuff contaminant are typically relatively low.
Another beneficial way of degradation of dye pollutant is, not by illumination, catalysis to be used under the room temperature condition of energy-conservation
Agent carries out catalytic degradation.Development high activity, the catalyst of high durability are for dyestuff contaminant under no light, room temperature condition
Degraded, has important practical prospect and learning value in field of environment pollution control.
Many catalyst can show catalysis activity, or even activity high under conditions of having illumination, but this activity
Obtain, usually to this condition of illumination highly dependent upon.If intensity of illumination is very weak, or without illumination, then cannot show to urge
Change activity, this causes that the application of catalyst is restricted.
Ce(IO3)4It is a kind of inorganic compound, although its preparation method and the early document report of composition identification, but mesh
It is preceding not yet to have patent and document report Ce (IO3)4Application study, especially it as catalyst application study.
The content of the invention
Present invention aim at offer Ce (IO3)4Compound provides this first in a kind of new opplication of field of environmental improvement
The application example of compound.
The technical scheme is that:
A kind of Ce (IO3)4Application, Ce (IO3)4It is as catalyst degradation organic dye pollutant, the step of concrete application:
(1)With organic dye pollutant as substrate, with Ce (IO3)4For catalyst carries out catalytic degradation;
(2)Ce(IO3)4The activity rating of catalyst:The degradation rate of organic dye pollutant is determined, it is degradable required with its
Time weigh its catalysis activity;
Above-mentioned Ce (IO3)4Application, described organic dye pollutant is preferably rhodamine B(RhB)Or methyl orange(MO),
Described catalytic degradation, temperature is 10-25 DEG C, and illumination condition is complete lucifuge or natural light irradiation.
The beneficial effects of the present invention are:
(1)Test result indicate that, Ce (IO3)4Even if catalytic degradation activity under conditions of complete lucifuge, also significantly greater than may be used
The commercial titanium dioxide seen under light irradiation(P25)Photochemical catalyst, solves the problems, such as that existing catalyst activity is low, while solving
The problem of the active heavy dependence illumination condition of existing photochemical catalyst.
(2)Ce (IO of the invention3)4Method for preparing catalyst is simple, preparation condition is gentle, is conducive to popularization and application.
Brief description of the drawings
Fig. 1 is Ce (IO prepared by the embodiment of the present invention 13)4The SEM figures of catalyst.
Fig. 2 is Ce (IO prepared by the embodiment of the present invention 13)4The EDS results of catalyst.
Fig. 3 is Ce (IO prepared by the embodiment of the present invention 13)4With the Activity Results figure of P25 photocatalyst for degrading RhB dyestuffs.
Wherein, C0The initial concentration of RhB before being added for catalyst, C is the concentration of RhB under any instant in catalytic process.
Fig. 4 is Ce (IO prepared by the embodiment of the present invention 13)4With the Activity Results figure of P25 photocatalyst for degrading MO dyestuffs.Its
In, C0The initial concentration of MO before being added for catalyst, C is the concentration of MO under any instant in catalytic process.
Specific embodiment
Here is Ce (IO of the present invention3)4With the specific embodiment of application study, following examples are further intended to specifically
The bright present invention, is not intended to limit the present invention.
Embodiment 1
(1)Ce(IO3)4Preparation
By 1 mmol ammonium ceric nitrates((NH4)2Ce(NO3)6)40 mL deionized waters, obtain ceric ammonium nitrate solution.By 4 mmol's
Sodium iodate(NaIO3)40 mL deionized waters are dissolved in, sodium iodide solution is obtained.At room temperature, in the process of stirring sodium iodide solution
In, ammonium ceric nitrate is added dropwise in sodium iodide solution.After completion of dropping, continue to stir 1 h.By gained precipitation deionized water
Wash twice(Every time with the mL of deionized water 50), after centrifugation, the h of oven drying 12 that temperature is 60 DEG C is placed in, obtain final product Ce
(IO3)4Sample.
(2)Ce(IO3)4Sign
The SEM of Fig. 1 schemes visible, Ce (IO3)4Sample has the random pattern of 0.1-10 nm sizes.The EDS of the SEM figures of Fig. 2
Result shows that contained atom Ce, I, O number ratio of sample is close to 1: 4 :12, this explanation Ce (IO3)4Sample is successfully made
It is standby.
(3)Ce(IO3)4The activity rating of catalyst degradation MO dyestuff contaminants
By gained Ce (IO3)4Sample is degraded substrate with RhB or MO, carries out catalytically active assessment, and by its Activity Results with
P25 photochemical catalysts are contrasted.
①Ce(IO3)4The active testing of catalytic degradation RhB
By the Ce (IO of 150 mg3)4Catalyst is placed in the RhB solution that 100 mL concentration are 10 mg/L(It is contained in the spacious of 400 mL
Mouth beaker)In, in the stirring at room temperature of complete lucifuge.Sampled in different time points respectively, supernatant is taken after centrifugation, will be upper
Clear liquid dilution obtains sample.Use ultraviolet specrophotometer(General analysis TU1810, Beijing Puxi General Instrument Co., Ltd)Survey
Determine absorbance of the sample at 554 nm.The RhB concentration of sample is calculated finally according to concentration-absorbance standard curve.
②Ce(IO3)4The active testing of catalytic degradation MO
By the Ce (IO of 150 mg3)4Catalyst is placed in the MO solution that 100 mL concentration are 10 mg/L(It is contained in the spacious of 400 mL
Mouth beaker)In, in the stirring at room temperature of complete lucifuge.Sampled in different time points respectively, supernatant is taken after centrifugation, will be upper
Clear liquid dilution obtains sample.Use ultraviolet specrophotometer(General analysis TU1810, Beijing Puxi General Instrument Co., Ltd)Survey
Determine absorbance of the sample at 465 nm.The MO concentration of sample is calculated finally according to concentration-absorbance standard curve.
3. the active testing of P25 photocatalytic degradations RhB
The P25 of 150 mg is placed in the RhB solution that 100 mL concentration are 10 mg/L(It is contained in the uncovered beaker of 400 mL)In,
Lucifuge stirs 40 min at room temperature, rhodamine molecule is reached absorption-desorption equilibrium on P25 surfaces.Then 500W xenon lamps are opened
(PLS-SXE300, Beijing Bo Feilai Science and Technology Ltd.s), light of the wavelength less than 420nm, RhB liquid level of solution are filtered off with optical filter
Immediately below xenon lamp, the distance between liquid level and fluorescent tube center are 14 centimetres(Irradiation level is 400 mW/cm2).So process
Preferably illumination condition is to provide for, so as to ensure that P25 can fully show its catalysis activity.Respectively in different time points
Sampling, takes supernatant after centrifugation, supernatant dilution is obtained into sample.Use ultraviolet specrophotometer(General analysis TU1810, Beijing
Pu Xi all purpose instruments Co., Ltd)Determine absorbance of the sample at 554 nm.It is bent finally according to concentration-absorbance standard
Line calculates the RhB concentration of sample.
4. the active testing of P25 photocatalytic degradations MO
The P25 of 150 mg is placed in the MO solution that 100 mL concentration are 10 mg/L(It is contained in the uncovered beaker of 400 mL)In, room
The lower lucifuge of temperature stirs 40 min, rhodamine molecule is reached absorption-desorption equilibrium on P25 surfaces.Then 500W xenon lamps are opened
(PLS-SXE300, Beijing Bo Feilai Science and Technology Ltd.s), light of the wavelength less than 420nm, MO liquid level of solution are filtered off with optical filter
Immediately below xenon lamp, the distance between liquid level and fluorescent tube center are 14 centimetres(Irradiation level is 400 mW/cm2).So process
Preferably illumination condition is to provide for, so as to ensure that P25 can fully show its catalysis activity.Respectively in different time points
Sampling, takes supernatant after centrifugation, supernatant dilution is obtained into sample.Use ultraviolet specrophotometer(General analysis TU1810, Beijing
Pu Xi all purpose instruments Co., Ltd)Determine absorbance of the sample at 465 nm.It is bent finally according to concentration-absorbance standard
Line calculates the MO concentration of sample.
As seen from Figure 3, the random time point within 0-80 min, Ce (IO3)4The corresponding C/C of catalyst0Value is all obvious
C/C corresponding less than P25 photochemical catalysts0.From fig. 4, it can be seen that the random time point within 0-70 min, Ce (IO3)4Catalyst
Corresponding C/C0Value is all significantly lower than the corresponding C/C of P25 photochemical catalysts0.Even if this explanation gives P25 photochemical catalysts preferably light
According to condition, and to Ce (IO3)4Carry out lucifuge treatment, Ce (IO3)4The activity of catalyst degradation RhB or MO is also apparently higher than P25 light
Catalyst.Therefore, Ce (IO3)4Catalyst degradation RhB or MO are an energy-conservation, efficient process, in terms of environmental pollution improvement
There is potential application prospect.
Claims (3)
1. a kind of Ce (IO3)4Application, it is characterised in that Ce (IO3)4As catalyst degradation organic dye pollutant, specifically should
With the step of be:
(1)With organic dye pollutant as substrate, with Ce (IO3)4For catalyst carries out catalytic degradation;
(2)Ce(IO3)4The activity rating of catalyst:The degradation rate of organic dye pollutant is determined, it is degradable required with its
Time weigh its catalysis activity.
2. Ce (IO according to claim 13)4Application, it is characterised in that:Described organic dye pollutant is Luo Dan
Bright B or methyl orange.
3. Ce (IO according to claim 13)4Application, it is characterised in that:Described catalytic degradation, temperature is 10-25
DEG C, illumination condition is complete lucifuge or natural light irradiation.
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Cited By (1)
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CN111001312A (en) * | 2019-12-19 | 2020-04-14 | 井冈山大学 | Organic-inorganic hybrid membrane and preparation method thereof |
Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
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CN103922287A (en) * | 2014-04-23 | 2014-07-16 | 山东大学 | Lanthanide series iodate crystal with high photocatalysis activity and preparation method thereof |
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CN103922287A (en) * | 2014-04-23 | 2014-07-16 | 山东大学 | Lanthanide series iodate crystal with high photocatalysis activity and preparation method thereof |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN111001312A (en) * | 2019-12-19 | 2020-04-14 | 井冈山大学 | Organic-inorganic hybrid membrane and preparation method thereof |
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