CN108246317A - A kind of recyclable ferroselenium composite nano materials and its application in rhodamine B degradation waste water - Google Patents
A kind of recyclable ferroselenium composite nano materials and its application in rhodamine B degradation waste water Download PDFInfo
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- CN108246317A CN108246317A CN201810025239.2A CN201810025239A CN108246317A CN 108246317 A CN108246317 A CN 108246317A CN 201810025239 A CN201810025239 A CN 201810025239A CN 108246317 A CN108246317 A CN 108246317A
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- ferroselenium
- composite nano
- nano materials
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- rhodamine
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- 239000002131 composite material Substances 0.000 title claims abstract description 32
- 239000002086 nanomaterial Substances 0.000 title claims abstract description 31
- PYWVYCXTNDRMGF-UHFFFAOYSA-N rhodamine B Chemical compound [Cl-].C=12C=CC(=[N+](CC)CC)C=C2OC2=CC(N(CC)CC)=CC=C2C=1C1=CC=CC=C1C(O)=O PYWVYCXTNDRMGF-UHFFFAOYSA-N 0.000 title abstract description 26
- 229940043267 rhodamine b Drugs 0.000 title abstract description 25
- 230000015556 catabolic process Effects 0.000 title abstract description 21
- 238000006731 degradation reaction Methods 0.000 title abstract description 21
- 239000002351 wastewater Substances 0.000 title abstract description 9
- 239000000463 material Substances 0.000 claims abstract description 8
- 239000003054 catalyst Substances 0.000 claims abstract description 5
- BUGBHKTXTAQXES-UHFFFAOYSA-N Selenium Chemical compound [Se] BUGBHKTXTAQXES-UHFFFAOYSA-N 0.000 claims description 29
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 18
- 229910052711 selenium Inorganic materials 0.000 claims description 17
- 239000011669 selenium Substances 0.000 claims description 17
- 150000002505 iron Chemical class 0.000 claims description 15
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 12
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 claims description 11
- 150000008044 alkali metal hydroxides Chemical class 0.000 claims description 11
- IKDUDTNKRLTJSI-UHFFFAOYSA-N hydrazine monohydrate Substances O.NN IKDUDTNKRLTJSI-UHFFFAOYSA-N 0.000 claims description 11
- XEEYBQQBJWHFJM-UHFFFAOYSA-N iron Substances [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 10
- 235000013855 polyvinylpyrrolidone Nutrition 0.000 claims description 10
- 229920000036 polyvinylpyrrolidone Polymers 0.000 claims description 10
- 239000001267 polyvinylpyrrolidone Substances 0.000 claims description 10
- NWZSZGALRFJKBT-KNIFDHDWSA-N (2s)-2,6-diaminohexanoic acid;(2s)-2-hydroxybutanedioic acid Chemical compound OC(=O)[C@@H](O)CC(O)=O.NCCCC[C@H](N)C(O)=O NWZSZGALRFJKBT-KNIFDHDWSA-N 0.000 claims description 9
- WMFOQBRAJBCJND-UHFFFAOYSA-M Lithium hydroxide Chemical compound [Li+].[OH-] WMFOQBRAJBCJND-UHFFFAOYSA-M 0.000 claims description 6
- 229910001854 alkali hydroxide Inorganic materials 0.000 claims description 6
- HUCVOHYBFXVBRW-UHFFFAOYSA-M caesium hydroxide Chemical compound [OH-].[Cs+] HUCVOHYBFXVBRW-UHFFFAOYSA-M 0.000 claims description 6
- 238000010438 heat treatment Methods 0.000 claims description 6
- 238000003756 stirring Methods 0.000 claims description 6
- 239000002244 precipitate Substances 0.000 claims description 5
- 229910021577 Iron(II) chloride Inorganic materials 0.000 claims description 4
- NMCUIPGRVMDVDB-UHFFFAOYSA-L iron dichloride Chemical compound Cl[Fe]Cl NMCUIPGRVMDVDB-UHFFFAOYSA-L 0.000 claims description 4
- 229910052603 melanterite Inorganic materials 0.000 claims description 4
- 238000002360 preparation method Methods 0.000 claims description 4
- BAUYGSIQEAFULO-UHFFFAOYSA-L iron(2+) sulfate (anhydrous) Chemical compound [Fe+2].[O-]S([O-])(=O)=O BAUYGSIQEAFULO-UHFFFAOYSA-L 0.000 claims description 3
- 229910000359 iron(II) sulfate Inorganic materials 0.000 claims description 3
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 claims 1
- 240000007594 Oryza sativa Species 0.000 claims 1
- 235000007164 Oryza sativa Nutrition 0.000 claims 1
- 229910052783 alkali metal Inorganic materials 0.000 claims 1
- 150000001340 alkali metals Chemical class 0.000 claims 1
- 235000013339 cereals Nutrition 0.000 claims 1
- 150000001875 compounds Chemical class 0.000 claims 1
- 229910052739 hydrogen Inorganic materials 0.000 claims 1
- 239000001257 hydrogen Substances 0.000 claims 1
- 235000009566 rice Nutrition 0.000 claims 1
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 description 33
- 239000000243 solution Substances 0.000 description 32
- 239000000047 product Substances 0.000 description 16
- 238000006243 chemical reaction Methods 0.000 description 7
- 238000002474 experimental method Methods 0.000 description 6
- 239000007788 liquid Substances 0.000 description 5
- 230000003647 oxidation Effects 0.000 description 5
- 238000007254 oxidation reaction Methods 0.000 description 5
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 4
- 238000000034 method Methods 0.000 description 4
- 230000035484 reaction time Effects 0.000 description 4
- 238000004064 recycling Methods 0.000 description 4
- 238000005516 engineering process Methods 0.000 description 3
- 239000002091 nanocage Substances 0.000 description 3
- 238000006555 catalytic reaction Methods 0.000 description 2
- 230000003750 conditioning effect Effects 0.000 description 2
- 230000000593 degrading effect Effects 0.000 description 2
- 229910052742 iron Inorganic materials 0.000 description 2
- SZVJSHCCFOBDDC-UHFFFAOYSA-N iron(II,III) oxide Inorganic materials O=[Fe]O[Fe]O[Fe]=O SZVJSHCCFOBDDC-UHFFFAOYSA-N 0.000 description 2
- 150000002978 peroxides Chemical class 0.000 description 2
- 239000000843 powder Substances 0.000 description 2
- 238000001556 precipitation Methods 0.000 description 2
- 241000549556 Nanos Species 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 230000000711 cancerogenic effect Effects 0.000 description 1
- 231100000357 carcinogen Toxicity 0.000 description 1
- 239000003183 carcinogenic agent Substances 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000010790 dilution Methods 0.000 description 1
- 239000012895 dilution Substances 0.000 description 1
- 239000000975 dye Substances 0.000 description 1
- 238000004043 dyeing Methods 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 230000004630 mental health Effects 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 238000007639 printing Methods 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 239000006228 supernatant Substances 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
- 238000009941 weaving Methods 0.000 description 1
Classifications
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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
- B01J27/02—Sulfur, selenium or tellurium; Compounds thereof
- B01J27/057—Selenium or tellurium; Compounds thereof
- B01J27/0573—Selenium; Compounds thereof
-
- 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
- B01J35/00—Catalysts, in general, characterised by their form or physical properties
- B01J35/20—Catalysts, in general, characterised by their form or physical properties characterised by their non-solid state
- B01J35/23—Catalysts, in general, characterised by their form or physical properties characterised by their non-solid state in a colloidal state
-
- 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
- B01J35/00—Catalysts, in general, characterised by their form or physical properties
- B01J35/30—Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
- B01J35/33—Electric or magnetic properties
-
- 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
- B01J35/00—Catalysts, in general, characterised by their form or physical properties
- B01J35/40—Catalysts, in general, characterised by their form or physical properties characterised by dimensions, e.g. grain size
-
- 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
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/722—Oxidation by peroxides
-
- 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
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/725—Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
-
- 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
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/34—Organic compounds containing oxygen
-
- 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
- C02F2101/38—Organic compounds containing nitrogen
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- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Materials Engineering (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Catalysts (AREA)
- Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
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Abstract
The present invention relates to a kind of recyclable ferroselenium composite nano materials and its applications in rhodamine B degradation waste water, the ferroselenium composite nano materials of the present invention, it can be used as Fenton catalyst to be used for rhodamine B degradation, after the material circulation uses 5 times, it is catalyzed to the degradation rate of RhB still greater than 90%.
Description
Technical field
The invention belongs to field of nanometer material technology, and in particular to a kind of recyclable ferroselenium composite nano materials and its
Application in rhodamine B degradation waste water.
Background technology
Rhodamine B (Rhodamine B, RhB) is a kind of artificial synthesized organic dyestuff, industry (as weaving, printing and dyeing,
Process hides etc.) in be widely used, produce the higher industrial wastewater of the content of a large amount of rhodamine Bs.RhB is a kind of carcinogen,
It such as cannot effectively remove, it will threaten the physical and mental health of the mankind.It is generally removed in waste water using Fenton oxidation method at present
Rhodamine B, Fenton oxidation method is using Fe2+And H2O2OH is generated, it, being capable of Quick Oxidation since OH oxidabilities are strong
A variety of organic matters for being difficult to aoxidize in sewage, but traditional Fenton oxidation technology is that Fe need to be added in system2+And H2O2,
Because of the Fe in system2+It is not easily recycled, it is impossible to reuse and effluent color dilution is higher, be restricted its application, therefore, compel to be essential
It develops one kind to be easily recycled, green, the efficient Fenton catalyst that can be recycled.
Invention content
The present invention provides a kind of ferroselenium composite nano materials (i.e. the nano ferriferrous oxide of selenium doping), it is characterised in that institute
The preparation method for stating ferroselenium composite nano materials includes the following steps:
(1) it is soluble in water by divalent iron salt, polyvinylpyrrolidone, 80-90 DEG C is heated to, obtains solution A;
(2) selenium powder is added in hydrazine hydrate, heating stirring to selenium powder is completely dissolved to obtain solution B;
(3) after in the solution A for obtaining the solution B addition step (1) that step (2) obtains, alkali metal hydroxide is added in
Solution is kept for 80-90 DEG C, after being stirred to react 3-5h, is centrifuged, is washed, is dry that dark brown precipitation, as described ferroselenium are answered
Close nano material (i.e. the nano ferriferrous oxide of selenium doping).
The preferred FeSO of divalent iron salt described in step (1)4·7H2O、FeSO4、FeCl2、Fe(NO3)2In one kind or several
Kind;Divalent iron salt:Polyvinylpyrrolidone:The mass ratio of water is 1:0.1-0.2:15-20;
Containing 10-15mg selenium in a concentration of every milliliter of hydrazine hydrate of selenium in step (2) solution B, i.e., per 10-15 mg selenium powders
Use 1mL hydrazine hydrates;
Alkali metal hydroxide preferred NaOH, KOH, LiOH, CsOH, alkali hydroxide soln described in step (3)
A concentration of 4-5mol/L, the dosage of alkali hydroxide soln is 5-10 times of divalent iron salt quality;The dosage of solution B is
Every gram of divalent iron salt uses 1mL solution Bs;The grain size of the ferroselenium composite nano materials is 50-100nm.
Another embodiment of the present invention provides the preparation method of the nano ferriferrous oxide of above-mentioned selenium doping, and feature exists
In including the following steps:
(1) it is soluble in water by divalent iron salt, polyvinylpyrrolidone, 80-90 DEG C is heated to, obtains solution A;
(2) selenium powder is added in hydrazine hydrate, heating stirring to selenium powder is completely dissolved to obtain solution B;
(3) after in the solution A for obtaining the solution B addition step (1) that step (2) obtains, alkali metal hydroxide is added in
Solution is kept for 80-90 DEG C, after being stirred to react 3-5h, is centrifuged, is washed, is dry that dark brown precipitation, as described selenium adulterate
Nano ferriferrous oxide.
The preferred FeSO of divalent iron salt described in step (1)4·7H2O、FeSO4、FeCl2、Fe(NO3)2In one kind or several
Kind;Divalent iron salt:Polyvinylpyrrolidone:The mass ratio of water is 1:0.1-0.2:15-20;
Containing 10-15mg selenium in a concentration of every milliliter of hydrazine hydrate of selenium in step (2) solution B, i.e., per 10-15 mg selenium powders
Use 1mL hydrazine hydrates;
Alkali metal hydroxide preferred NaOH, KOH, LiOH, CsOH, alkali hydroxide soln described in step (3)
A concentration of 4-5mol/L, the dosage of alkali hydroxide soln is 5-10 times of divalent iron salt quality;The dosage of solution B is
Every gram of divalent iron salt uses 1mL solution Bs;The grain size of the nano ferriferrous oxide of the selenium doping is 50-100nm.
Another embodiment of the present invention provides (the i.e. oxidation of nanometer four three of selenium doping of above-mentioned ferroselenium composite nano materials
Iron) application as Fenton catalyst.Above-mentioned ferroselenium composite nano materials (i.e. the nano ferriferrous oxide of selenium doping) can follow
Ring uses 5 times.
The method that another embodiment of the present invention provides rhodamine B in a kind of degrading waste water, it is characterised in that including such as
Lower step:Above-mentioned ferroselenium composite nano materials and peroxide are added in into waste water.The dosage of ferroselenium composite nano materials is every
Waste water is risen using 0.6-3.6g ferroseleniums composite nano materials, it is preferable to use 1.8g ferroselenium composite nano materials;Peroxide is preferred
Hydrogen peroxide, the dosage of hydrogen peroxide use 1.5-4.0g hydrogen peroxide, it is preferable to use 3.0g hydrogen peroxide for every liter of waste water.Ferroselenium of the present invention
In composite nano materials degrading waste water the preferred pH of rhodamine B be 1.0-5.0, further preferably 5.0.
Hydrogen peroxide of the present invention be commercially available common hydrogen peroxide, content of hydrogen peroxide 30%.
Compared with prior art, the advantage of the invention is that:(1) the invention discloses a kind of novel ferroselenium composite Nanos
Material (i.e. the nano ferriferrous oxide of selenium doping), being used as Fenton catalyst, the material has for rhodamine B degradation
After recycling 5 times, it is catalyzed to the degradation rate of RhB still greater than 90%;(2) above-mentioned ferroselenium composite Nano provided by the invention
Material is in catalysis efficiency and recycles on number better than (such as the Chinese patent Shen of other ferriferrous oxide materials in the prior art
Please number:201610080860.X, 201611144384.X, the records such as 201610310844.5 ferriferrous oxide material).
Description of the drawings
The SEM figures of Fig. 1 products A
The XRD diagram of Fig. 2 products A
Influence of Fig. 3 product A usage amounts to rhodamine B degradation rate
Influence of Fig. 4 hydrogen peroxide usage amount to rhodamine B degradation rate
Influences of Fig. 5 pH to rhodamine B degradation efficiency
Fig. 6 reaction temperatures influence the degradation rate of rhodamine B
Product A-D, Fe-G-3, Fe under Fig. 7 optimum experimental conditions3O4Nanocages are to the degradation rate of rhodamine B
Fig. 8 products A, which recycles 5 degradation rates to rhodamine B, to be changed
Specific embodiment
For the ease of a further understanding of the present invention, examples provided below has done more detailed description to it.But
It is that these embodiments only are not used for limiting the scope of the present invention or implementation principle, reality of the invention for being better understood from inventing
The mode of applying is not limited to the following contents.
Embodiment 1
(1) by FeSO4·7H2O (10g), polyvinylpyrrolidone (1g), are dissolved in water (150g), are heated to 80-90 DEG C,
Obtain solution A;
(2) selenium powder (100mg) is added in hydrazine hydrate (10mL), heating stirring to selenium powder is completely dissolved to obtain solution B;
(3) after in the solution A for obtaining the solution B addition step (1) that step (2) obtains, the NaOH for adding in 4 mol/L is molten
Liquid (100g) is kept for 80-90 DEG C, after being stirred to react 3h, is centrifuged, is washed, is dry that dark brown precipitates 2.6g, as described
Ferroselenium composite nano materials (abbreviation product A).
Embodiment 2
(1) by FeCl2(10g), polyvinylpyrrolidone (2g), is dissolved in water (200g), is heated to 80-90 DEG C, obtain molten
Liquid A;
(2) selenium powder (150mg) is added in hydrazine hydrate (10mL), heating stirring to selenium powder is completely dissolved to obtain solution B;
(3) after in the solution A for obtaining the solution B addition step (1) that step (2) obtains, the KOH for adding in 5 mol/L is molten
Liquid (50g) is kept for 80-90 DEG C, after being stirred to react 5h, is centrifuged, is washed, is dry that dark brown precipitates 5.8g, as described
Ferroselenium composite nano materials (abbreviation product B).
Embodiment 3
(1) by FeSO4·7H2O (10g), polyvinylpyrrolidone (1g), are dissolved in water (150g), are heated to 80-90 DEG C,
Obtain solution A;
(2) selenium powder (50mg) is added in hydrazine hydrate (10mL), heating stirring to selenium powder is completely dissolved to obtain solution B;
(3) after in the solution A for obtaining the solution B addition step (1) that step (2) obtains, the NaOH for adding in 4 mol/L is molten
Liquid (100g) is kept for 80-90 DEG C, after being stirred to react 3h, is centrifuged, is washed, is dry that dark brown precipitates 2.4g, abbreviation product
C。
Embodiment 4
(1) by FeSO4·7H2O (10g), polyvinylpyrrolidone (1g), are dissolved in water (150g), are heated to 80-90 DEG C,
Add in the NaOH solution (100g) of 4mol/L, kept for 80-90 DEG C, after being stirred to react 3h, centrifuge, washing, dry black
Precipitate 2.5g, abbreviation product D.
5 rhodamine B degradation experiment of embodiment
(1) dosage of ferroselenium composite nano materials of the present invention, hydrogen peroxide, the influence of pH, temperature to degradation rate
Experimental method:Rhodamine B solution (10mg/L) 100mL is moved into the conical flask of 250mL, with hydrochloric acid conditioning solution
Acidity is separately added into test sample and suitable hydrogen peroxide, is vibrated on shaking table, takes supernatant liquor at regular intervals, measures
Remain rhodamine B concentration.
1. investigate the usage amount of ferroselenium composite nano materials of the present invention
Experiment condition:Hydrogen peroxide usage amount be 2.5g/L, pH 5.0,30 DEG C, reaction time 15min of reaction temperature, selenium
The usage amount of iron composite nano materials (product A) is respectively 0.6g/L, 1.2g/L, 1.8g/L, 2.4g/L, 3.0g/L, 3.6g/
L。
The degradation rate (Fig. 3) of rhodamine B.
2. investigate the usage amount of hydrogen peroxide
Experiment condition:The usage amount of product A is 1.8g/L, pH 5.0, and 30 DEG C, reaction time 15min of reaction temperature is double
Oxygen water usage amount is respectively 1.5g/L, 2.0g/L, 2.5g/L, 3.0g/L, 3.5g/L, 4.0 g/L.
The degradation rate (Fig. 4) of rhodamine B.
3. investigate pH
Experiment condition:The usage amount of product A be 1.8g/L, hydrogen peroxide usage amount be 3.0g/L, 30 DEG C of reaction temperature, instead
15min between seasonable adjusts pH value 1 to 9, the degradation rate (Fig. 5) of rhodamine B.
4. investigate reaction temperature
The usage amount of product A be 1.8g/L, hydrogen peroxide usage amount be 3.0g/L, pH 5.0, reaction time 15min, instead
It is 20 DEG C, 30 DEG C, 40 DEG C, 50 DEG C to answer temperature, influence (Fig. 6) of the temperature to degradation efficiency.
(2) under the optimum experimental condition obtained in (1):Test sample usage amount is 1.8g/L, and hydrogen peroxide usage amount is
3.0g/L, pH 5.0,30 DEG C of reaction temperature under conditions of reaction time 15min, take 6 parts of rhodamine B solution (10mg/ respectively
L) 100mL is moved into the conical flask of 250mL, with hydrochloric acid conditioning solution pH 5.0, is separately added into appropriate product A-D, Fe-G-3 and (is pressed
According to Chinese Patent Application No.:201610080860.X it is prepared by embodiment 1), Fe3O4Nanocages are (according to Chinese Patent Application No.:
It is prepared by 201611144384.X embodiments 1) and suitable hydrogen peroxide, it is vibrated on shaking table, takes upper strata clear at regular intervals
Liquid measures residual rhodamine B concentration (Fig. 7).
(3) the recycling performance of ferroselenium composite nano materials of the present invention
Under optimum experimental condition, the recycling performance of test product A is carried out after the completion of catalysis reaction with magnet every time
Recycling carries out 5 experiments (Fig. 8) altogether at identical conditions.As seen from the figure, after 5 uses, product A is catalyzed to sieve
The degradation rate of red bright B drops to 91% from 96%, illustrates it with preferable stability and recycles performance, is much better than Fe-G-3
And Fe3O4Nanocages.
Claims (7)
1. a kind of ferroselenium composite nano materials, it is characterised in that the preparation method of the ferroselenium composite nano materials includes following step
Suddenly:
(1) it is soluble in water by divalent iron salt, polyvinylpyrrolidone, 80-90 DEG C is heated to, obtains solution A;
(2) selenium powder is added in hydrazine hydrate, heating stirring to selenium powder is completely dissolved to obtain solution B;
(3) after in the solution A for obtaining the solution B addition step (1) that step (2) obtains, alkali hydroxide soln is added in,
It is kept for 80-90 DEG C, after being stirred to react 3-5h, centrifuges, washs, is dry that dark brown precipitates, as described ferroselenium is compound to be received
Rice material.
2. ferroselenium composite nano materials described in claim 1, it is characterised in that the divalent iron salt described in step (1) is preferred
FeSO4·7H2O、FeSO4、FeCl2、Fe(NO3)2One or more of;Divalent iron salt:Polyvinylpyrrolidone:The quality of water
Than being 1:0.1-0.2:15-20.
3. claim 1-2 any one of them ferroselenium composite nano materials, it is characterised in that selenium is dense in step (2) solution B
It spends to contain 10-15mg selenium in every milliliter of hydrazine hydrate.
4. claim 1-3 any one of them ferroselenium composite nano materials, it is characterised in that alkali metal hydrogen described in step (3)
Oxide preferred NaOH, KOH, LiOH, CsOH, a concentration of 4-5mol/L of alkali hydroxide soln, alkali metal hydroxide
The dosage of object solution is 5-10 times of divalent iron salt quality;The dosage of solution B uses 1mL solution Bs for every gram of divalent iron salt.
5. claim 1-4 any one of them ferroselenium composite nano materials, it is characterised in that the ferroselenium composite nano materials
Grain size be 50-100nm.
6. application of the claim 1-5 any one of them ferroselenium composite nano materials as Fenton catalyst.
7. the preparation method of claim 1-5 any one of them ferroselenium composite nano materials.
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CN104190434A (en) * | 2014-08-22 | 2014-12-10 | 哈尔滨工业大学 | Preparation of Fe3O4-MnO2 composite catalyst and method for removing organic dye in printing and dyeing wastewater by using Fe3O4-MnO2 composite catalyst |
CN106045151A (en) * | 2016-07-08 | 2016-10-26 | 常州大学 | Method for degrading rhodamine B through nanometer Fe3O4/H2O2 synergistically |
CN106571248A (en) * | 2016-10-26 | 2017-04-19 | 信阳师范学院 | Preparation method for electrode material of Se-doped ZnO-SnO2 supercapacitor taking foamed nickel as substrate |
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CN104190434A (en) * | 2014-08-22 | 2014-12-10 | 哈尔滨工业大学 | Preparation of Fe3O4-MnO2 composite catalyst and method for removing organic dye in printing and dyeing wastewater by using Fe3O4-MnO2 composite catalyst |
CN106045151A (en) * | 2016-07-08 | 2016-10-26 | 常州大学 | Method for degrading rhodamine B through nanometer Fe3O4/H2O2 synergistically |
CN106571248A (en) * | 2016-10-26 | 2017-04-19 | 信阳师范学院 | Preparation method for electrode material of Se-doped ZnO-SnO2 supercapacitor taking foamed nickel as substrate |
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