GB2618635A - Photocatalytic material for degrading tetracycline in wastewater and preparation method thereof - Google Patents
Photocatalytic material for degrading tetracycline in wastewater and preparation method thereof Download PDFInfo
- Publication number
- GB2618635A GB2618635A GB2216790.2A GB202216790A GB2618635A GB 2618635 A GB2618635 A GB 2618635A GB 202216790 A GB202216790 A GB 202216790A GB 2618635 A GB2618635 A GB 2618635A
- Authority
- GB
- United Kingdom
- Prior art keywords
- zno
- zinc
- preparation
- suspension
- mmol
- Prior art date
- 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.)
- Pending
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- 230000001699 photocatalysis Effects 0.000 title claims abstract description 56
- 239000000463 material Substances 0.000 title claims abstract description 53
- 238000002360 preparation method Methods 0.000 title claims abstract description 35
- 239000004098 Tetracycline Substances 0.000 title claims abstract description 22
- 229960002180 tetracycline Drugs 0.000 title claims abstract description 22
- 229930101283 tetracycline Natural products 0.000 title claims abstract description 22
- 235000019364 tetracycline Nutrition 0.000 title claims abstract description 22
- 150000003522 tetracyclines Chemical class 0.000 title claims abstract description 22
- 239000002351 wastewater Substances 0.000 title claims abstract description 19
- 230000000593 degrading effect Effects 0.000 title claims description 11
- XLOMVQKBTHCTTD-UHFFFAOYSA-N Zinc monoxide Chemical compound [Zn]=O XLOMVQKBTHCTTD-UHFFFAOYSA-N 0.000 claims abstract description 152
- 239000011787 zinc oxide Substances 0.000 claims abstract description 73
- ZNOKGRXACCSDPY-UHFFFAOYSA-N tungsten trioxide Chemical compound O=[W](=O)=O ZNOKGRXACCSDPY-UHFFFAOYSA-N 0.000 claims abstract description 47
- 239000000725 suspension Substances 0.000 claims abstract description 46
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims abstract description 33
- 239000002073 nanorod Substances 0.000 claims abstract description 28
- GGCZERPQGJTIQP-UHFFFAOYSA-N sodium;9,10-dioxoanthracene-2-sulfonic acid Chemical compound [Na+].C1=CC=C2C(=O)C3=CC(S(=O)(=O)O)=CC=C3C(=O)C2=C1 GGCZERPQGJTIQP-UHFFFAOYSA-N 0.000 claims abstract description 26
- 230000015572 biosynthetic process Effects 0.000 claims abstract description 25
- 238000001027 hydrothermal synthesis Methods 0.000 claims abstract description 25
- 238000003786 synthesis reaction Methods 0.000 claims abstract description 23
- 239000003795 chemical substances by application Substances 0.000 claims abstract description 22
- 239000002808 molecular sieve Substances 0.000 claims abstract description 21
- URGAHOPLAPQHLN-UHFFFAOYSA-N sodium aluminosilicate Chemical compound [Na+].[Al+3].[O-][Si]([O-])=O.[O-][Si]([O-])=O URGAHOPLAPQHLN-UHFFFAOYSA-N 0.000 claims abstract description 21
- WNROFYMDJYEPJX-UHFFFAOYSA-K aluminium hydroxide Chemical compound [OH-].[OH-].[OH-].[Al+3] WNROFYMDJYEPJX-UHFFFAOYSA-K 0.000 claims abstract description 16
- 238000009210 therapy by ultrasound Methods 0.000 claims abstract description 13
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims abstract description 11
- 239000008119 colloidal silica Substances 0.000 claims abstract description 11
- LPSKDVINWQNWFE-UHFFFAOYSA-M tetrapropylazanium;hydroxide Chemical compound [OH-].CCC[N+](CCC)(CCC)CCC LPSKDVINWQNWFE-UHFFFAOYSA-M 0.000 claims abstract description 11
- 239000000203 mixture Substances 0.000 claims abstract description 10
- 229920000036 polyvinylpyrrolidone Polymers 0.000 claims abstract description 10
- 239000001267 polyvinylpyrrolidone Substances 0.000 claims abstract description 10
- 235000013855 polyvinylpyrrolidone Nutrition 0.000 claims abstract description 10
- 239000000758 substrate Substances 0.000 claims description 32
- 150000003751 zinc Chemical class 0.000 claims description 27
- 239000003125 aqueous solvent Substances 0.000 claims description 22
- HZAXFHJVJLSVMW-UHFFFAOYSA-N 2-Aminoethan-1-ol Chemical compound NCCO HZAXFHJVJLSVMW-UHFFFAOYSA-N 0.000 claims description 20
- 229910019142 PO4 Inorganic materials 0.000 claims description 20
- 239000010452 phosphate Substances 0.000 claims description 20
- NBIIXXVUZAFLBC-UHFFFAOYSA-K phosphate Chemical compound [O-]P([O-])([O-])=O NBIIXXVUZAFLBC-UHFFFAOYSA-K 0.000 claims description 19
- VKYKSIONXSXAKP-UHFFFAOYSA-N hexamethylenetetramine Chemical compound C1N(C2)CN3CN1CN2C3 VKYKSIONXSXAKP-UHFFFAOYSA-N 0.000 claims description 14
- 239000002243 precursor Substances 0.000 claims description 14
- ONDPHDOFVYQSGI-UHFFFAOYSA-N zinc nitrate Chemical compound [Zn+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O ONDPHDOFVYQSGI-UHFFFAOYSA-N 0.000 claims description 11
- XNWFRZJHXBZDAG-UHFFFAOYSA-N 2-METHOXYETHANOL Chemical compound COCCO XNWFRZJHXBZDAG-UHFFFAOYSA-N 0.000 claims description 10
- 238000003756 stirring Methods 0.000 claims description 10
- JIAARYAFYJHUJI-UHFFFAOYSA-L zinc dichloride Chemical compound [Cl-].[Cl-].[Zn+2] JIAARYAFYJHUJI-UHFFFAOYSA-L 0.000 claims description 10
- 235000010299 hexamethylene tetramine Nutrition 0.000 claims description 8
- 239000004312 hexamethylene tetramine Substances 0.000 claims description 7
- ZOIORXHNWRGPMV-UHFFFAOYSA-N acetic acid;zinc Chemical compound [Zn].CC(O)=O.CC(O)=O ZOIORXHNWRGPMV-UHFFFAOYSA-N 0.000 claims description 6
- 238000002156 mixing Methods 0.000 claims description 6
- SQGYOTSLMSWVJD-UHFFFAOYSA-N silver(1+) nitrate Chemical compound [Ag+].[O-]N(=O)=O SQGYOTSLMSWVJD-UHFFFAOYSA-N 0.000 claims description 6
- 239000004246 zinc acetate Substances 0.000 claims description 6
- 235000013904 zinc acetate Nutrition 0.000 claims description 6
- 230000032683 aging Effects 0.000 claims description 5
- 239000011592 zinc chloride Substances 0.000 claims description 5
- 235000005074 zinc chloride Nutrition 0.000 claims description 5
- WHMDKBIGKVEYHS-IYEMJOQQSA-L Zinc gluconate Chemical compound [Zn+2].OC[C@@H](O)[C@@H](O)[C@H](O)[C@@H](O)C([O-])=O.OC[C@@H](O)[C@@H](O)[C@H](O)[C@@H](O)C([O-])=O WHMDKBIGKVEYHS-IYEMJOQQSA-L 0.000 claims description 4
- CANRESZKMUPMAE-UHFFFAOYSA-L Zinc lactate Chemical compound [Zn+2].CC(O)C([O-])=O.CC(O)C([O-])=O CANRESZKMUPMAE-UHFFFAOYSA-L 0.000 claims description 4
- LFVGISIMTYGQHF-UHFFFAOYSA-N ammonium dihydrogen phosphate Chemical compound [NH4+].OP(O)([O-])=O LFVGISIMTYGQHF-UHFFFAOYSA-N 0.000 claims description 4
- 229910000387 ammonium dihydrogen phosphate Inorganic materials 0.000 claims description 4
- 239000011248 coating agent Substances 0.000 claims description 4
- 238000000576 coating method Methods 0.000 claims description 4
- 238000003618 dip coating Methods 0.000 claims description 4
- 235000019837 monoammonium phosphate Nutrition 0.000 claims description 4
- CQLFBEKRDQMJLZ-UHFFFAOYSA-M silver acetate Chemical compound [Ag+].CC([O-])=O CQLFBEKRDQMJLZ-UHFFFAOYSA-M 0.000 claims description 4
- 229940071536 silver acetate Drugs 0.000 claims description 4
- WGIWBXUNRXCYRA-UHFFFAOYSA-H trizinc;2-hydroxypropane-1,2,3-tricarboxylate Chemical compound [Zn+2].[Zn+2].[Zn+2].[O-]C(=O)CC(O)(CC([O-])=O)C([O-])=O.[O-]C(=O)CC(O)(CC([O-])=O)C([O-])=O WGIWBXUNRXCYRA-UHFFFAOYSA-H 0.000 claims description 4
- 229960000314 zinc acetate Drugs 0.000 claims description 4
- 229960001939 zinc chloride Drugs 0.000 claims description 4
- 239000011746 zinc citrate Substances 0.000 claims description 4
- 235000006076 zinc citrate Nutrition 0.000 claims description 4
- 229940068475 zinc citrate Drugs 0.000 claims description 4
- 239000011670 zinc gluconate Substances 0.000 claims description 4
- 235000011478 zinc gluconate Nutrition 0.000 claims description 4
- 229960000306 zinc gluconate Drugs 0.000 claims description 4
- 239000011576 zinc lactate Substances 0.000 claims description 4
- 235000000193 zinc lactate Nutrition 0.000 claims description 4
- 229940050168 zinc lactate Drugs 0.000 claims description 4
- NWONKYPBYAMBJT-UHFFFAOYSA-L zinc sulfate Chemical compound [Zn+2].[O-]S([O-])(=O)=O NWONKYPBYAMBJT-UHFFFAOYSA-L 0.000 claims description 4
- 229960001763 zinc sulfate Drugs 0.000 claims description 4
- 229910000368 zinc sulfate Inorganic materials 0.000 claims description 4
- 229910001961 silver nitrate Inorganic materials 0.000 claims description 3
- 239000001488 sodium phosphate Substances 0.000 claims description 3
- 229910000162 sodium phosphate Inorganic materials 0.000 claims description 3
- RYFMWSXOAZQYPI-UHFFFAOYSA-K trisodium phosphate Chemical compound [Na+].[Na+].[Na+].[O-]P([O-])([O-])=O RYFMWSXOAZQYPI-UHFFFAOYSA-K 0.000 claims description 3
- 241000206607 Porphyra umbilicalis Species 0.000 claims 1
- 230000015556 catabolic process Effects 0.000 abstract description 7
- 238000006731 degradation reaction Methods 0.000 abstract description 7
- 229910021502 aluminium hydroxide Inorganic materials 0.000 abstract 1
- 239000007900 aqueous suspension Substances 0.000 abstract 1
- 238000000034 method Methods 0.000 abstract 1
- 125000002467 phosphate group Chemical class [H]OP(=O)(O[H])O[*] 0.000 abstract 1
- 239000000243 solution Substances 0.000 description 25
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 13
- 230000000052 comparative effect Effects 0.000 description 9
- 239000013078 crystal Substances 0.000 description 9
- 239000008367 deionised water Substances 0.000 description 8
- 229910021641 deionized water Inorganic materials 0.000 description 8
- 229910000161 silver phosphate Inorganic materials 0.000 description 8
- 229910001868 water Inorganic materials 0.000 description 8
- 238000012360 testing method Methods 0.000 description 6
- 229910021536 Zeolite Inorganic materials 0.000 description 5
- 239000002131 composite material Substances 0.000 description 5
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 5
- 239000002135 nanosheet Substances 0.000 description 5
- 239000010457 zeolite Substances 0.000 description 5
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 4
- 239000011521 glass Substances 0.000 description 4
- 238000013033 photocatalytic degradation reaction Methods 0.000 description 4
- 239000000047 product Substances 0.000 description 4
- 239000011701 zinc Substances 0.000 description 4
- 239000007864 aqueous solution Substances 0.000 description 3
- 230000003197 catalytic effect Effects 0.000 description 3
- 238000006243 chemical reaction Methods 0.000 description 3
- 238000009826 distribution Methods 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 238000002474 experimental method Methods 0.000 description 3
- 230000006798 recombination Effects 0.000 description 3
- 238000005215 recombination Methods 0.000 description 3
- 238000012546 transfer Methods 0.000 description 3
- 229910052724 xenon Inorganic materials 0.000 description 3
- FHNFHKCVQCLJFQ-UHFFFAOYSA-N xenon atom Chemical compound [Xe] FHNFHKCVQCLJFQ-UHFFFAOYSA-N 0.000 description 3
- CSCPPACGZOOCGX-UHFFFAOYSA-N Acetone Chemical compound CC(C)=O CSCPPACGZOOCGX-UHFFFAOYSA-N 0.000 description 2
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 2
- 239000008186 active pharmaceutical agent Substances 0.000 description 2
- 238000003795 desorption Methods 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 230000018109 developmental process Effects 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 230000004298 light response Effects 0.000 description 2
- 244000144972 livestock Species 0.000 description 2
- JMANVNJQNLATNU-UHFFFAOYSA-N oxalonitrile Chemical group N#CC#N JMANVNJQNLATNU-UHFFFAOYSA-N 0.000 description 2
- 239000007800 oxidant agent Substances 0.000 description 2
- 239000011148 porous material Substances 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 238000001179 sorption measurement Methods 0.000 description 2
- 229940072172 tetracycline antibiotic Drugs 0.000 description 2
- 238000004506 ultrasonic cleaning Methods 0.000 description 2
- WSFSSNUMVMOOMR-UHFFFAOYSA-N Formaldehyde Chemical compound O=C WSFSSNUMVMOOMR-UHFFFAOYSA-N 0.000 description 1
- 208000027954 Poultry disease Diseases 0.000 description 1
- 238000002835 absorbance Methods 0.000 description 1
- 238000005054 agglomeration Methods 0.000 description 1
- 238000004220 aggregation Methods 0.000 description 1
- 239000012298 atmosphere Substances 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 239000003054 catalyst Substances 0.000 description 1
- 238000006555 catalytic reaction Methods 0.000 description 1
- 239000007795 chemical reaction product Substances 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 238000004132 cross linking Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 201000010099 disease Diseases 0.000 description 1
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 description 1
- 239000012153 distilled water Substances 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 231100000584 environmental toxicity Toxicity 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- XDDAORKBJWWYJS-UHFFFAOYSA-N glyphosate Chemical compound OC(=O)CNCP(O)(O)=O XDDAORKBJWWYJS-UHFFFAOYSA-N 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 238000009830 intercalation Methods 0.000 description 1
- 230000002687 intercalation Effects 0.000 description 1
- 230000001678 irradiating effect Effects 0.000 description 1
- 230000031700 light absorption Effects 0.000 description 1
- 230000007246 mechanism Effects 0.000 description 1
- 239000002105 nanoparticle Substances 0.000 description 1
- 239000011941 photocatalyst Substances 0.000 description 1
- 238000013032 photocatalytic reaction Methods 0.000 description 1
- 244000144977 poultry Species 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 229910052709 silver Inorganic materials 0.000 description 1
- 239000012265 solid product Substances 0.000 description 1
- 238000013112 stability test Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000006228 supernatant Substances 0.000 description 1
- 229910052721 tungsten Inorganic materials 0.000 description 1
- 238000009827 uniform distribution Methods 0.000 description 1
- 229910052725 zinc Inorganic materials 0.000 description 1
- 229910021511 zinc hydroxide Inorganic materials 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
- 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
- B01J35/39—Photocatalytic properties
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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
- B01J27/14—Phosphorus; Compounds thereof
- B01J27/186—Phosphorus; Compounds thereof with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
- B01J27/188—Phosphorus; Compounds thereof with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium with chromium, molybdenum, tungsten or polonium
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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
- 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
-
- 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
- B01J29/00—Catalysts comprising molecular sieves
- B01J29/04—Catalysts comprising molecular sieves having base-exchange properties, e.g. crystalline zeolites
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- B01J29/00—Catalysts comprising molecular sieves
- B01J29/04—Catalysts comprising molecular sieves having base-exchange properties, e.g. crystalline zeolites
- B01J29/06—Crystalline aluminosilicate zeolites; Isomorphous compounds thereof
- B01J29/40—Crystalline aluminosilicate zeolites; Isomorphous compounds thereof of the pentasil type, e.g. types ZSM-5, ZSM-8 or ZSM-11, as exemplified by patent documents US3702886, GB1334243 and US3709979, respectively
- B01J29/48—Crystalline aluminosilicate zeolites; Isomorphous compounds thereof of the pentasil type, e.g. types ZSM-5, ZSM-8 or ZSM-11, as exemplified by patent documents US3702886, GB1334243 and US3709979, respectively containing arsenic, antimony, bismuth, vanadium, niobium tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
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- B—PERFORMING OPERATIONS; TRANSPORTING
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- B01J29/00—Catalysts comprising molecular sieves
- B01J29/82—Phosphates
- B01J29/84—Aluminophosphates containing other elements, e.g. metals, boron
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- B01J35/20—Catalysts, in general, characterised by their form or physical properties characterised by their non-solid state
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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
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- B01J35/30—Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
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- B01J37/00—Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
- B01J37/34—Irradiation by, or application of, electric, magnetic or wave energy, e.g. ultrasonic waves ; Ionic sputtering; Flame or plasma spraying; Particle radiation
- B01J37/341—Irradiation by, or application of, electric, magnetic or wave energy, e.g. ultrasonic waves ; Ionic sputtering; Flame or plasma spraying; Particle radiation making use of electric or magnetic fields, wave energy or particle radiation
- B01J37/344—Irradiation by, or application of, electric, magnetic or wave energy, e.g. ultrasonic waves ; Ionic sputtering; Flame or plasma spraying; Particle radiation making use of electric or magnetic fields, wave energy or particle radiation of electromagnetic wave energy
- B01J37/346—Irradiation by, or application of, electric, magnetic or wave energy, e.g. ultrasonic waves ; Ionic sputtering; Flame or plasma spraying; Particle radiation making use of electric or magnetic fields, wave energy or particle radiation of electromagnetic wave energy of microwave energy
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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
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
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- B—PERFORMING OPERATIONS; TRANSPORTING
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- B01J2229/00—Aspects of molecular sieve catalysts not covered by B01J29/00
- B01J2229/10—After treatment, characterised by the effect to be obtained
- B01J2229/18—After treatment, characterised by the effect to be obtained to introduce other elements into or onto the molecular sieve itself
- B01J2229/186—After treatment, characterised by the effect to be obtained to introduce other elements into or onto the molecular sieve itself not in framework positions
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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
- 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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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/34—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
- C02F2103/343—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the pharmaceutical industry, e.g. containing antibiotics
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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
- C02F2305/00—Use of specific compounds during water treatment
- C02F2305/08—Nanoparticles or nanotubes
-
- 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
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/30—Wastewater or sewage treatment systems using renewable energies
- Y02W10/37—Wastewater or sewage treatment systems using renewable energies using solar energy
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- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Materials Engineering (AREA)
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Abstract
A method for preparation of a photocatalytic material for the degradation of tetracycline in wastewater. Zinc oxide nanorods are placed into an aqueous suspension comprising tungsten trioxide, polyvinyl pyrrolidone. A silver salt is then added to the suspension followed by a phosphate salt. A second aqueous mixture comprising aluminium hydroxide, sodium hydroxide, tetrapropylammonium hydroxide and colloidal silica is aged between 75 and 95 ℃ for between 8 and 24 h to obtain a molecular sieve synthesis agent. The molecular synthesis agent is added to the zinc oxide nanorod suspension and mixed using an ultrasonic treatment, the mixture is then subjected to a microwave hydrothermal reaction at 120 to 180 ℃ for 10 to 120 mins to obtain the photocatalytic material.
Description
PHOTOCATALYTIC MATERIAL FOR DEGRADING TETRACYCLINE IN
WASTEWATER AND PREPARATION METHOD THEREOF
TECHNICAL FIELD
100011 The present disclosure relates to the technical field of photocatalytic materials, in particular to a photocatalytic material for degrading tetracycline in wastewater and a preparation method thereof
BACKGROUND
100021 Tetracycline antibiotics play an important role in the treatment of human diseases and livestock and poultry diseases and in promoting the growth of livestock and poultry, and are widely used in the medical industry and animal husbandry. As one of the main producing areas of tetracycline active pharmaceutical ingredients (APIs) in China, Ningxia plays an extremely important role in the development of tetracycline antibiotics in China.
100031 However, due to a stable nature, tetracycline is difficult to degrade in the natural environment and has ecotoxicity, posing a threat to the ecological environment. Therefore, it has become a highly important problem in the development of local economic sustainable line to deal with the residual tetracycline in pharmaceutical wastewater.
100041 To this end, those skilled in the art have proposed a technology based on photocatalytic degradation of tetracycline in wastewater. The photocatalytic degradation technology can conduct reactions at a room temperature, and has reaction products of water and carbon dioxide without secondary pollution, which integrates environmental protection and cost-effectiveness. Therefore, this technology has a bright future in environmental governance. A commonly used photocatalytic material in the prior art is carbon nitride, but the carbon nitride has a poor photocatalytic degradation effect on tetracycline, and is difficult to recover, easily leading to secondary pollution. Therefore, it is quite necessary to find a novel photocatalytic technology.
100051 In order to solve the above problems, the present disclosure proposes a photocatalytic material for degrading tetracycline in wastewater and a preparation method thereof
SUMMARY
100061 In order to solve the above deficiencies in the prior art, the present disclosure provides a photocatalytic material for degrading tetracycline in wastewater and a preparation method thereof In the present disclosure, the photocatalytic material has a high visible light response, and can efficiently degrade the tetracycline in wastewater under visible light.
100071 In the present disclosure, the photocatalytic material for degrading tetracycline in wastewater and the preparation method thereof are achieved by the following technical solutions: [0008] A first objective of the present disclosure is to provide a preparation method of a photocatalytic material for degrading tetracycline in wastewater, including the following steps: [0009] immersing a zinc oxide (ZnO) nanorod array into a suspension A, adding a silver salt, mixing well by stirring, adding a phosphate and mixing well by stirring to obtain a uniform suspension B; [00101 dispersing aluminum hydroxide, sodium hydroxide, and tetrapropylammonium hydroxide evenly in an aqueous solvent, adding colloidal silica and mixing well, and subjecting an obtained mixture to aging at 75°C to 95°C for 8 h to 24 h to obtain a molecular sieve synthesis agent; [0011] adding the molecular sieve synthesis agent to the suspension B to conduct an ultrasonic treatment, and conducting a microwave hydrothermal reaction at 120°C to 180°C for 10 mm to 120 min to obtain the photocatalytic material; where [0012] the suspension A is prepared from tungsten trioxide, polyvinylpyrrolidone, and the aqueous solvent.
[0013] Further, the molecular sieve synthesis agent and the suspension B have a volume ratio of 1:(1-3).
[0014] Further, in the molecular sieve synthesis agent, the aluminum hydroxide, the sodium hydroxide, the tetrapropylammonium hydroxide, and the aqueous solvent have a dosage ratio of 0.3 mmol: (7-8) mmol: (1-2) mL. (1-1 5) mL; and [0015] the colloidal silica and the aluminum hydroxide have a mass ratio of (25-30):1.
[0016] Further, in the suspension A, the tungsten trioxide, the polyvinylpyrrolidone, and the aqueous solvent have a dosage ratio of 1 mmol: 0.1 g: (20-40) mL [0017] Further, the silver salt is selected from the group consisting of silver acetate and silver nitrate; and [0018] the phosphate is selected from the group consisting of sodium phosphate and ammonium dihydrogen phosphate.
[0019] Further, the silver salt and the suspension A have a dosage ratio of (10-20) mmol: 100 mL; and [0020] the silver salt and the phosphate have a molar ratio of (2-4):1.
[0021] Further, the stirring after adding the silver salt is conducted at 150 r/min to 250 r/min for 20 min to 40 min; and [0022] the stirring after adding the phosphate is conducted at 50 r/min to 150 r/min for 30 min to 60 min 100231 Further, the ZnO nanorod array is prepared by the following steps: [0024] dispersing a zinc salt A and hexamethylenetetramine uniformly in the aqueous solvent to obtain a uniform ZnO precursor solution for later use; [0025] dispersing a zinc salt B and ethanolamine uniformly in 2-methoxyethanol to form a seed layer solution; immersing a cleaned substrate into the seed layer solution to prepare a ZnO seed layer on the substrate, to obtain a substrate with the ZnO seed layer on a surface; and [0026] immersing the substrate with the ZnO seed layer on a surface in the ZnO precursor solution, and conducting a hydrothermal reaction to obtain the ZnO nanorod array; where [0027] the zinc salt A and the zinc salt B each are any one selected from the group consisting of zinc nitrate, zinc chloride, zinc sulfate, zinc acetate, zinc citrate, zinc gluconate, and zinc lactate.
[0028] Further, the zinc salt A, the hexamethylenetetramine, and the aqueous solvent have a dosage ratio of 1 mmol: 1 mmol: (20-40) ml; and [0029] the zinc salt B, the ethanolamine, and the 2-methoxyethanol have a dosage ratio of (0.5-2) mmol: 1 mmol: (30-60) ml.
[0030] Further, the microwave hydrothermal reaction is conducted at 2.45 Gliz and 800 W. [0031] A second objective of the present disclosure is to provide a photocatalytic material prepared by the preparation method.
[0032] Compared with the prior art, the present disclosure has the following beneficial effects: [0033] In the present disclosure, a layer of dense ZnO (ZnO) nanorod array is formed on a ZnO seed crystal through a hydrothermal reaction. The ZnO nanorod array as a seed crystal is immersed in a suspension A prepared by tungsten trioxide, polyvinylpyrrolidone, and an aqueous solvent, such that substances in the suspension A (such as the tungsten trioxide) can be uniformly distributed inside and around the ZnO nanorod array. Sequentially; a silver salt and a phosphate are added into the suspension A and mixed uniformly to form a uniform suspension B. During the stirring, a part of the silver salt and phosphate may form A831304 crystal nuclei on a surface of the ZnO nanorod array, thus changing hydrophilicity of the ZnO nanorod array surface. In addition, the crystal nucleus of Ag3PO4 is formed in an aqueous solution containing tungsten trioxide, such that the tungsten trioxide can effectively protect the crystal nucleus of Ag51304 to stably exist in the aqueous solution, which is helpful for the formation of a ZnO-Ag3PO4-W03 composite in a later stage of the hydrothermal reaction. By the ultrasonic treatment, components in the molecular sieve synthesis agent are uniformly dispersed around the ZnO-Ag3PO4-W03 composite; and after the microwave hydrothermal reaction, the ZnO-A834'04-W03 composite can be rapidly encapsulated in pores of a zeolite with a hierarchically porous MFI nanosheet structure (ZSM-5) during gradual formation of the zeolite with a hierarchically porous MFI nanosheet structure, thereby obtaining the photocatalytic material of the present disclosure. Through mutual cross-linking or intercalation between the components, a heterogeneous interface is formed between the components and a recombination efficiency of electron-hole pairs in the material is reduced, thereby improving a visible light absorption properties of the material and thereby improving a photocatalytic efficiency of the material.
100341 In the present disclosure, the catalytic material has ZnO/Ag3PO4/W03 ternary nanoclusters. In the ZnO/Ag11304/W03 ternary nanoclusters, the ECB of WO3 (0.61 eV-vs-NHE) is more negative than that of E-(02/H202) (0.68 eV-vs-NHE), such that excited electrons are finally captured by 02 molecules adsorbed on a surface of the ZnO-Ag3PO4-W03 nanoclusters to generate H202, and the H202 provides OH by accepting electrons. In addition, the ECB of WO; is more positive than that of E (02/02) (-0.33 eV vs NEE), and dissolved 02 molecules cannot be directly oxidized to 02-by the excited electrons; meanwhile, the EVB (2.64 eV vs NHE) of Ag31304 is more positive than that of E (01110H) (1.99 eV vs NEE), and holes generated in the Ag3PO4 can oxidize H20/0H-to form OH radicals. Therefore, the ZnO/Ag31304/W03 ternary nanoclusters enable the catalytic material of the present disclosure to help improve photo-induced charge transfer, suppress a charge recombination rate, and promote generation of more oxidants (OH and holes). In addition, the ZnO/Ag31304/W03 ternary nanoclusters are encapsulated in the zeolite with a hierarchically porous MFI nanosheet structure, so as to avoid the self-agglomeration of ZnO-Ag31304-W03, such that the ZnO-Ag31304-W03 ternary nanoclusters exist uniformly and stably. Thus, a stability of properties of the photocatalytic material is ensured, thereby further improving a photocatalytic activity.
[0035] In the present disclosure, the photocatalytic material has a high visible light response, and can efficiently degrade the tetracycline in wastewater under visible light. In addition, the photocatalytic material is fixed on a glass substrate to participate in a catalytic reaction, which does not dissolve in water to cause secondary pollution to water, and is convenient for recycling.
BRIEF DESCRIPTION OF THE DRAWINGS
[0036] FIG. 1 shows a schematic diagram of element distribution in a photocatalytic material of Example 1; [0037] FIG. 2 shows a test result of a degradation efficiency of tetracycline by the photocatalytic material of the present disclosure; and [0038] FIG. 3 shows a test result of a stability of a photocatalytic performance of the photocatalytic material of Example 1.
DETAILED DESCRIPTION OF THE EMBODIMENTS
100391 The technical solutions in the examples of the present disclosure will be clearly and completely described below with reference to the accompanying drawings in the examples of the
present disclosure.
[0040] Example 1
100411 In this example, a preparation method of a photocatalytic material for degrading tetracycline in wastewater included the following steps: [0042] 1) Preparation of a substrate with a ZnO seed layer on a surface: 100431 a zinc salt B and ethanolamine were uniformly dispersed in 2-methoxyethanol to form a seed layer solution; 50 mL of the seed layer solution was coated on a substrate by a dip-coating method to form a ZnO seed layer, to obtain a substrate with the ZnO seed layer on a surface; where 100441 the zinc salt B, the ethanolamine, and the 2-methoxyethanol had a dosage ratio of 1 mmol: 1 mmol: 40 ml; and [0045] the zinc salt B was zinc nitrate.
[0046] 2) Preparation of a ZnO precursor solution: [0047] according to a dosage ratio of 1 mmol: 1 mmol: 30 ml, a zinc salt A and hexamethylenetetramine were uniformly dispersed in an aqueous solvent, and an obtained mixture was magnetically stirred at 60°C to form a homogeneous ZnO precursor solution; where [0048] the zinc salt A was zinc acetate.
[0049] 3) Preparation of a ZnO nanorod array: [0050] the substrate with the ZnO seed layer on a surface was immersed in the ZnO precursor solution, followed by conducting a hydrothermal reaction at 98°C for 4 h, a product was cooled to a room temperature, filtered, washed with deionized water 3 times, and air-dried naturally to obtain the ZnO nanorod array; where reaction mechanisms were as follows: 100511 (CH2)6N4+H2 0 ->HCHO+NTL. H20 (1) [0052] NH3 H20->INH4-+OH-(2) [0053] Zn(NO3)2+2NH4OH->Zn(OH)2,1+2NE4IN-03 (3) [0054] Zn(OH)2+4NE140H->Zn(NH3)42++20H-+4H20 (4) [0055] Zn(NH3),42++01-1--,Zn04,+4NH3+H20 (5).
[0056] A ZnO seed layer was prepared on the substrate, the ZnO seed layer was placed in the ZnO precursor solution, and a very uniform ZnO nanorod array was obtained through a hydrothermal reaction.
[0057] 4) Preparation of a suspension B: [0058] according to a dosage ratio of 1 mmol 01 g: 30 mL, W03 and polyvinylpyrrolidone were uniformly distributed in deionized water by an ultrasonic treatment to obtain a suspension A; where the polyvinylpyrrolidone could enhance an adhesiveness of the suspension A, thereby improving adhesion or coating of the W03 on a surface of ZnO or Ag3PO4; [0059] the ZnO nanorod array was immersed in the suspension A, such that a part of the W03 in the suspension A could enter an interior or gap of the ZnO nanorod array, so as to form a ZnO/W03 composite structure in the ZnO nanorod array; other tungsten trioxide was evenly distributed around the ZnO nanorod array, and the W03 distributed in the suspension A could prevent the subsequent Ag3PO4 crystal nuclei from dissolving in water; as a result, the Ag31304 crystal nuclei were stably exist in the aqueous solution, which was helpful for a catalyst stability of the photocatalytic material during use; and [0060] a silver salt was added, and stirred at 200 r/min for 30 min, a phosphate was added, and stirred at 100 r/min for 40 min to form a uniform suspension B; during the stirring, after a part of the silver salt and phosphate met, the Ag3PO4 crystal nuclei were formed on a surface of the ZnO nanorod array; meanwhile, a part of W03 in the suspension B could be coated on the surface of the ZnO nanorod array together with the A83PO4 crystal nuclei to form ZnO/A83PO4/W03 clusters; where [0061] the silver salt was silver acetate; [0062] the phosphate was ammonium dihydrogen phosphate; [0063] the silver salt and the suspension A had a dosage ratio of 15 mmol 100 m L and [0064] the silver salt and the phosphate had a molar ratio of 3:1.
[0065] 5) Microwave hydrothermal synthesis of the photocatalytic material: [0066] aluminum hydroxide, sodium hydroxide, and tetrapropylammonium hydroxide were dispersed evenly in an aqueous solvent, colloidal silica was added and mixed well, and an obtained mixture was subjected to aging at 85°C for 12 h to obtain a molecular sieve synthesis agent; where [0067] the aluminum hydroxide, the sodium hydroxide, the tetrapropylammonium hydroxide, and the aqueous solvent had a dosage ratio of 0.3 mmol: 7.6 mmol: 1.6 ml: 1.2 mL; and [0068] the colloidal silica and the aluminum hydroxide had a mass ratio of 27:1; and [0069] the suspension B was added dropwise to the molecular sieve synthesis agent, and components in the molecular sieve synthesis agent were uniformly dispersed in the surrounding of ZnO/Ag3PO4/W03 clusters by an ultrasonic treatment for 30 min, and a microwave hydrothermal reaction was conducted at 160°C for 30 min; during the microwave hydrothermal reaction, with the rapid transfer of temperature, zeolite with a hierarchically porous MN nanosheet structure was gradually formed around the ZnO/A83PO4/W03 clusters, thereby rapidly encapsulating the ZnO/A83PO4/W03 clusters in pores of the zeolite with a hierarchically porous MFI nanosheet structure (ZSM-5), avoiding self-aggregation of the ZnO/Ag3PO4/W03 clusters; after the reaction, a collected solid product was alternately washed three times with absolute ethanol and deionized water, and then dried at 85°C to obtain the photocatalytic material.
[0070] Example 2
100711 In this example, a preparation method of a photocatalytic material for degrading tetracycline in wastewater included the following steps: 100721 1) Preparation of a substrate with a ZnO seed layer on a surface: [0073] a zinc salt B and ethanolamine were dispersed uniformly in 2-methoxyethanol to form a seed layer solution; a cleaned substrate was immersed into the seed layer solution to prepare a ZnO seed layer on the substrate, to obtain a substrate with the ZnO seed layer on a surface; where [0074] the zinc salt B, the ethanolamine, and the 2-methoxyethanol had a dosage ratio of 0.5 mmol: 1 mmol: 30 ml; and 100751 the zinc salt B was zinc acetate.
[0076] 2) Preparation of a ZnO precursor solution: [0077] according to a dosage ratio of 1 mmol: 1 mmol: 20 ml, a zinc salt A and hexamethylenetetramine were uniformly dispersed in an aqueous solvent, and an obtained mixture was magnetically stirred at 60°C to form a homogeneous ZnO precursor solution; where [0078] the zinc salt A was zinc chloride.
[0079] 3) Preparation of a ZnO nanorod array: 100801 the substrate with the ZnO seed layer on a surface was immersed in the ZnO precursor solution, followed by conducting a hydrothermal reaction at 90°C for 5 h, a product was cooled to a room temperature, filtered, washed with deionized water 3 times, and air-dried naturally to obtain the ZnO nanorod array.
100811 4) Preparation of a suspension B 100821 according to a dosage ratio of 1 mmol: 0.1 g: 20 mL, tungsten trioxide and polyvinylpyrrolidone were uniformly distributed in deionized water by an ultrasonic treatment to obtain a suspension A; and 100831 the ZnO nanorod array was immersed into the suspension A, a silver salt was added, and stirred at 150 r/min for 20 min, a phosphate was added, and stirred at 50 r/min for 30 min to obtain a uniform suspension B; where 100841 the silver salt was silver nitrate; [0085] the phosphate was ammonium dihydrogen phosphate; 100861 the silver salt and the suspension A had a dosage ratio of lOmmol 100 mL and 100871 the silver salt and the phosphate had a molar ratio of 2:1.
100881 5) Microwave hydrothermal synthesis of the photocatalytic material: [0089] aluminum hydroxide, sodium hydroxide, and tetrapropylammonium hydroxide were dispersed evenly in an aqueous solvent, colloidal silica was added and mixed well, and an obtained mixture was subjected to aging at 75°C for 24 h to obtain a molecular sieve synthesis agent; where [0090] the aluminum hydroxide, the sodium hydroxide, the tetrapropylammonium hydroxide, and the aqueous solvent had a dosage ratio of 0.3 mmol: 7 mmol: 1 ml. 1 mL; and [0091] the colloidal silica and the aluminum hydroxide had a mass ratio of 25:1; and [0092] the suspension B was added dropwise to the molecular sieve synthesis agent to conduct an ultrasonic treatment for 10 mm, and a microwave hydrothermal reaction was conducted at 120°C for 120 min to obtain the photocatalytic material.
[0093] Example 3
[0094] In this example, a preparation method of a photocatalytic material for degrading tetracycline in wastewater included the following steps: [0095] 1) Preparation of a substrate with a ZnO seed layer on a surface: [0096] a zinc salt B and ethanolamine were dispersed uniformly in 2-methoxyethanol to form a seed layer solution; a cleaned substrate was immersed into the seed layer solution to prepare a ZnO seed layer on the substrate, to obtain a substrate with the ZnO seed layer on a surface; where [0097] the zinc salt B, the ethanolamine, and the 2-methoxyethanol had a dosage ratio of 2 mmol 1 mmol: 60 ml; and 100981 the zinc salt B was any one selected from the group consisting of zinc nitrate, zinc chloride, zinc sulfate, zinc acetate, zinc citrate, zinc gluconate, and zinc lactate.
[0099] 2) Preparation of a ZnO precursor solution: [0100] according to a dosage ratio of 1 mmol: 1 mmol: 40 ml, a zinc salt A and hexamethylenetetramine were uniformly dispersed in an aqueous solvent, and an obtained mixture was magnetically stirred at 60°C to form a homogeneous ZnO precursor solution; where [0101] the zinc salt A was any one selected from the group consisting of zinc nitrate, zinc chloride, zinc sulfate, zinc acetate, zinc citrate, zinc gluconate, and zinc lactate.
[0102] 3) Preparation of a ZnO nanorod array: [0103] the substrate with the ZnO seed layer on a surface was immersed in the ZnO precursor solution, followed by conducting a hydrothermal reaction at 98°C for 4 h, a product was cooled to a room temperature, filtered, washed with deionized water 3 times, and air-dried naturally to obtain the ZnO nanorod array.
[0104] 4) Preparation of a suspension B [0105] according to a dosage ratio of 1 mmol: 0.1 g: 40 mL, tungsten trioxide and polyvinylpyrrolidone were uniformly distributed in deionized water by an ultrasonic treatment to obtain a suspension A; and [0106] the ZnO nanorod array was immersed into the suspension A, a silver salt was added, and stirred at 250 r/min for 40 min, a phosphate was added, and stirred at 150 r/min for 60 min to obtain a uniform suspension B; where [0107] the silver salt was silver acetate; 101081 the phosphate was sodium phosphate; [0109] the silver salt and the suspension A had a dosage ratio of 20mmol 100 mL and [0110] the silver salt and the phosphate had a molar ratio of 4:1.
[01111 5) Microwave hydrothermal synthesis of the photocatalytic material: [0112] aluminum hydroxide, sodium hydroxide, and tetrapropylammonium hydroxide were dispersed evenly in an aqueous solvent, colloidal silica was added and mixed well, and an obtained mixture was subjected to aging at 95°C for 8 h to obtain a molecular sieve synthesis agent; where [0113] the aluminum hydroxide, the sodium hydroxide, the tetrapropylammonium hydroxide, and the aqueous solvent had a dosage ratio of 0.3 mmol: 8 mmol: 2 ml: L5 mL; and [0114] the colloidal silica and the aluminum hydroxide had a mass ratio of 30:1; and [0115] the suspension B was added dropwise to the molecular sieve synthesis agent to conduct an ultrasonic treatment for 50 min, and a microwave hydrothermal reaction was conducted at 180°C for 10 min to obtain the photocatalytic material.
[0116] Comparative Example 1 [0117] This comparative example differed from Example 1 only in that: [0118] in this comparative example, after the molecular sieve synthesis agent was added dropwise to the suspension B, the microwave hydrothermal reaction was directly conducted without the ultrasonic treatment.
[0119] Comparative Example 2 [0120] This comparative example differed from Example 1 only in that: 101211 In this comparative example, no molecular sieve synthesis agent was added, and the suspension B was directly subjected to the microwave hydrothermal reaction after the ultrasonic treatment.
[0122] It should be noted that, in the above examples of the present disclosure, the substrate was an FTO conductive glass of 50 mmx15 mm 2.2 mm, and a cleaning treatment thereof was as follows: the FTO conductive glass was immersed in anhydrous ethanol to conduct ultrasonic cleaning for 10 min, and then immersed in acetone, and then immersed in deionized water to conduct ultrasonic cleaning for 10 min, and then dried with a hair dryer to obtain a cleaned FTO conductive glass. [0123] It should also be noted that, in the present disclosure, there was no special limitation on specific microwave conditions in the microwave hydrothermal reaction. Optionally, the microwave hydrothermal reaction was conducted at 2.45 GHz and 800 W. [0124] In the present disclosure, the W03 was synthesized by a hydrothermal method: [0125] 0.004 mol of WCI6 was uniformly dispersed in 80 mL of absolute ethanol, a resulting solution was transferred into a 100 mL Teflon-lined autoclave, and then kept at 160°C for 24 h; after cooling to a room temperature, a filter residue was collected by filtration, and washed with distilled water and absolute ethanol for several times in sequence to remove impurities on a surface of the filter residue; the filter residue was dried in an oven at 60°C for 12 h, and a dried product was sintered at 500°C for 1 h to obtain W03 nanoparticles.
[0126] In the present disclosure, the ZnO seed layer was prepared on the substrate by the following steps: [0127] A cleaned substrate was hung on a dip coater at a room temperature, the substrate was immersed in the seed layer solution and allowed to stand for 1 min, and dip coating was conducted at 200 mm/min; a coated substrate was dried in a constant-temperature drying oven at 85°C, and the dip coating was repeated 7 times to form 7 layers of coating on a surface of the substrate; the coated substrate was completely dried, and placed in a muffle furnace to anneal at 350°C for 30 min in an air atmosphere, such that an amorphous coating on the substrate formed a crystalline nano-ZnO seed layer to obtain a substrate with the ZnO seed layer.
[0128] Experimental part [0129] (I) Element distribution test [0130] In order to verify that the photocatalytic material prepared by the present disclosure was indeed a composite, the photocatalytic material of Example I was taken as an example, and an element distribution test was conducted. The results were shown in FIG. 1, and it was seen that elements (Si, 0, Zn, W, and Ag) in the photocatalytic material of Example 1 were uniformly distributed, [0131] (II) Photocatalytic degradation test [0132] In the present disclosure, tetracycline was prepared into a solution of 20 mg/L as wastewater to be treated; the photocatalytic materials of Examples 1 to 3 and Comparative Examples 1 and 2 each were used as a photocatalyst; a 300 W xenon lamp was used as a light source to simulate sunlight exposure conditions.
[0133] The specific test conditions were as follows: [0134] 30 mg of the photocatalytic materials of Examples Ito 3 and Comparative Examples 1 and 2 were separately added to 100 mL of the wastewater to be treated, mixed uniformly, and reacted in the dark for 30 min; after reaching adsorption and desorption equilibrium, a photocatalytic reaction was conducted under irradiation of the 300 W xenon lamp for 60 min; samples were sampled and centrifuged at 10,000 r/min for 10 min, each supernatant was collected and detected on a UV-Vis spectrophotometer to calculate a removal efficiency of tetracycline. The results were shown in FIG. 2. [0135] As was seen from FIG. 2, the degradation effects of Comparative Examples 1 and 2 were much lower than those of Examples 1 to 3, indicating that during the preparation process, the molecular sieve synthesis agent and the ultrasonic treatment after adding the molecular sieve synthesis agent each were critical to synthesis of the photocatalytic material of the present disclosure. This might be related to an effect of the two factors on uniform distribution of the components in the photocatalytic material.
[0136] (III) Stability test of photocatalytic performance 101371 Taking the photocatalytic material of Example 1 as an example, a photocatalytic performance of the photocatalytic material of the present disclosure was tested.
[0138] 30 mg of the photocatalytic material was placed in 100 mL of the wastewater to be treated, and then vigorously stirred for 30 min in the dark to achieve adsorption and desorption equilibrium.
After irradiating with the 300 W xenon lamp for 30 min, 5 mL of a suspension was aspirated for centrifugal separation, and an absorbance was determined using an UV-Vis spectrophotometer. After the photocatalytic experiment was completed, an obtained suspension was recovered by centrifugal separation, and dried for a next round of the photocatalytic experiment, where the experiment was cycled five times. The degradation rates results of five cycles were shown in FIG. 3.
[0139] It was seen from FIG. 3 that a first degradation efficiency was 68.4%, and a fifth degradation efficiency was 62.3%; after five repetitions, the degradation efficiency of the photocatalytic material of the present disclosure was not much lower than that of the first time, indicating that the photocatalytic material had a high stability and reusability.
[0140] Based on the above examples, in the present disclosure, the catalytic material has ZnO/A83PO4/W03 ternary nanoclusters. In the ZnO/Ag31304/W03 ternary nanoclusters, the ECB of W03 (0.61 eV. vs.NHE) is more negative than that of E*(09/H209) (0.68 eV*vs.NHE), such that excited electrons are finally captured by 09 molecules adsorbed on a surface of the ZnO-Ag3PO4-W0.3 nanoclusters to generate H202, and the H202 provides OH by accepting electrons. In addition, considering that the ECB of W03 is more positive than that of E (09/09) (-0.33 eV vs NEE), such that dissolved 09 molecules cannot be directly oxidized into 09-by the excited electrons. On the other hand, since the EVB (2.64 eV vs NHE) of Ag3PO4 is more positive than that of E (OH-/OH) (1.99 eV vs NTIE), such that holes generated in the Ag3PO4 can oxidize H20/0H-to form OH free radicals. Therefore, the photocatalytic material of the present disclosure can help to improve photo-induced charge transfer, inhibit a charge recombination rate, and promote generation of more oxidants (OH and holes), thereby improving a photocatalytic activity.
[0141] Apparently, the above described examples are merely a part rather than all of the examples of the present disclosure. All other embodiments obtained by those of ordinary skill in the art based on the embodiments of the present disclosure without creative efforts shall fall within the protection scope of the present disclosure.
Claims (10)
- WHAT IS CLAIMED IS: 1. A preparation method of a photocatalytic material for degrading tetracycline in wastewater, comprising the following steps: immersing a zinc oxide (ZnO) nanorod array into a suspension A, adding a silver salt, mixing well by stirring, adding a phosphate, and mixing well by stirring to obtain a uniform suspension B; dispersing aluminum hydroxide, sodium hydroxide, and tetrapropylammonium hydroxide evenly in an aqueous solvent, adding colloidal silica and mixing well, and subjecting an obtained mixture to aging at 75°C to 95°C for 8 h to 24 h to obtain a molecular sieve synthesis agent; and adding the molecular sieve synthesis agent to the suspension B to conduct an ultrasonic treatment, and conducting a microwave hydrothermal reaction at 120°C to 180°C for 10 mm to 120 min to obtain the photocatalytic material; wherein the suspension A is prepared from tungsten trioxide, polyvinylpyrrolidone, and the aqueous solvent.
- 2. The preparation method according to claim 1, wherein the molecular sieve synthesis agent and the suspension B have a volume ratio of 1:(1-3).
- 3. The preparation method according to claim 1, wherein in the molecular sieve synthesis agent, the aluminum hydroxide, the sodium hydroxide, the tetrapropylammonium hydroxide, and the aqueous solvent have a dosage ratio of 0.3 mmol: (7-8) mmol: (1-2) mL. (1-1 5) mL; and the colloidal silica and the aluminum hydroxide have a mass ratio of (25-30): L
- 4. The preparation method according to claim 1, wherein in the suspension A, the tungsten trioxide, the polyvinylpyrrolidone, and the aqueous solvent have a dosage ratio of 1 mmol: 0.1 g: (20-40) mL
- 5. The preparation method according to claim 1, wherein the silver salt is selected from the group consisting of silver acetate and silver nitrate; and the phosphate is selected from the group consisting of sodium phosphate and ammonium dihydrogen phosphate.
- 6. The preparation method according to claim 1, wherein the silver salt and the suspension A have a dosage ratio of (10-20) mmol: 100 mL; and the silver salt and the phosphate have a molar ratio of (2-4):1.
- 7. The preparation method according to claim I, wherein the stirring after adding the silver salt is conducted at 150 r/min to 250 r/min for 20 min to 40 min; and the stirring after adding the phosphate is conducted at 50 r/min to 150 r/min for 30 min to 60 min.
- 8. The preparation method according to claim 1, wherein the ZnO nanorod array is prepared by the following steps: dispersing a zinc salt A and hexamethylenetetramine uniformly in the aqueous solvent to obtain a uniform ZnO precursor solution for later use; dispersing a zinc salt B and ethanolamine uniformly in 2-methoxyethanol to form a seed layer solution; coating the seed layer solution on a substrate to form a ZnO seed layer by a dip-coating method, to obtain a substrate with the ZnO seed laver on a surface; and immersing the substrate with the ZnO seed layer on a surface in the ZnO precursor solution, and conducting a hydrothermal reaction to obtain the ZnO nanorod array; wherein the zinc salt A and the zinc salt B each are any one selected from the group consisting of zinc nitrate, zinc chloride, zinc sulfate, zinc acetate, zinc citrate, zinc gluconate, and zinc lactate.
- 9. The preparation method according to claim 8, wherein the zinc salt A, the hexamethylenetetramine, and the aqueous solvent have a dosage ratio of 1 mmol: 1 mmol: (20-40) ml; and the zinc salt B, the ethanolamine, and the 2-methoxyethanol have a dosage ratio of (0.5-2) mmol: 1 mmol: (30-60) ml.
- 10. A photocatalytic material prepared by the preparation method according to any one of claims Ito 9.
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Crystals, Alam M W et al., "Enhanced Photocatalytic Performance of Ag3PO4/Mn-ZnO Nanocomposite for the Degradation of Tetracycline Hydrochloride", 1156 (14 pp.). * |
International Journal of Energy Research, Vol 43, 2019, Y. Shaveisi et al., "Application of mixture experimental design for photocatalytinc ammonia degradation by sunlight driven WO3-Ag3PO4-ZnO ternary photocatalysts", pages 4879-4897 * |
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