CN113145145A - Cobalt phosphate catalyst capable of efficiently activating PMS (permanent magnet synchronous motor), and preparation method and application thereof - Google Patents

Cobalt phosphate catalyst capable of efficiently activating PMS (permanent magnet synchronous motor), and preparation method and application thereof Download PDF

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Publication number
CN113145145A
CN113145145A CN202110365431.8A CN202110365431A CN113145145A CN 113145145 A CN113145145 A CN 113145145A CN 202110365431 A CN202110365431 A CN 202110365431A CN 113145145 A CN113145145 A CN 113145145A
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cobalt
phosphate
pollutants
pms
cobalt phosphate
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曲晋
马秀峰
于中振
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Beijing University of Chemical Technology
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Beijing University of Chemical Technology
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J27/00Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
    • B01J27/14Phosphorus; Compounds thereof
    • B01J27/185Phosphorus; Compounds thereof with iron group metals or platinum group metals
    • B01J27/1853Phosphorus; Compounds thereof with iron group metals or platinum group metals with iron, cobalt or nickel
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B25/00Phosphorus; Compounds thereof
    • C01B25/16Oxyacids of phosphorus; Salts thereof
    • C01B25/26Phosphates
    • C01B25/37Phosphates of heavy metals
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/722Oxidation by peroxides
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/725Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01PINDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
    • C01P2002/00Crystal-structural characteristics
    • C01P2002/70Crystal-structural characteristics defined by measured X-ray, neutron or electron diffraction data
    • C01P2002/72Crystal-structural characteristics defined by measured X-ray, neutron or electron diffraction data by d-values or two theta-values, e.g. as X-ray diagram
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01PINDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
    • C01P2004/00Particle morphology
    • C01P2004/01Particle morphology depicted by an image
    • C01P2004/03Particle morphology depicted by an image obtained by SEM
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/308Dyes; Colorants; Fluorescent agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/38Organic compounds containing nitrogen

Abstract

The invention relates to a cobalt phosphate catalyst capable of efficiently activating PMS (permanent magnet synchronous motor), a preparation method and application thereof. The preparation method is simple, green and environment-friendly, and can efficiently and quickly realize pollutant degradation.

Description

Cobalt phosphate catalyst capable of efficiently activating PMS (permanent magnet synchronous motor), and preparation method and application thereof
Technical Field
The invention belongs to the technical field of inorganic catalysis, and particularly relates to a cobalt phosphate catalyst capable of efficiently activating PMS, and a preparation method and application thereof.
Background
The waste water often contains high concentration of toxic and non-degradable dyes, which threatens human health. Common wastewater treatment methods are biological processes, filtration and coagulation/flocculation/precipitation, etc., which have good effects on removing pollutants, but are energy intensive, costly, non-competitive in the face of large wastewater treatment demands, and may cause secondary pollution due to excessive use of chemicals.
In recent years, the sulfate-based advanced oxidation process (SR-AOP) has received much attention, has entered the field of vision, and has been successfully applied to the degradation of pollutants. Because the Peroxymonosulfate (PMS) can be activated to generate high-activity free radicals such as sulfate free radicals and hydroxyl free radicals, the peroxymonosulfate can oxidize and decompose refractory water pollutants.
A cobalt-based catalyst has been studied and reported in large quantities as a catalyst effective for activating PMS. The floriform CoSiOx catalyst with controllable morphology is prepared by the Marsupena marshal and the like, a large number of cobalt hydroxyl groups exist on the surface, the generation rate of free radicals is accelerated in the PMS activation process, the degradation rate is improved, and the excellent degradation rate is shown for various dyes.
Among the studies of various cobalt-based catalysts, the studies of cobalt phosphate have been focused on the direction of energy storage, such as sodium ion batteries, supercapacitors, etc., and there have been few studies and reports related thereto as a catalyst for activating PMS.
Disclosure of Invention
The invention aims to provide a cobalt phosphate catalyst capable of efficiently activating PMS, and a preparation method and application thereof. The prepared cobalt phosphate is used as a catalyst for efficiently activating the Peroxymonosulfate (PMS), and can effectively accelerate degradation of pollutants such as dye pollutants, antibiotics and the like in a water body by the Peroxymonosulfate (PMS). The preparation method is simple, green and environment-friendly, and can efficiently and quickly realize pollutant degradation.
In order to achieve the purpose, the technical scheme adopted by the invention is as follows:
a preparation method of a cobalt phosphate catalyst capable of efficiently activating PMS comprises the following steps:
(1) respectively preparing a cobalt nitrate solution and a phosphate solution, slowly dropping the cobalt nitrate solution into the phosphate solution under the stirring state, and uniformly stirring;
(2) and transferring the mixture into a hydrothermal kettle, carrying out hydrothermal reaction, washing and drying to obtain a cobalt phosphate nanosheet product.
In a preferred embodiment of the present invention, in step (1), the phosphate is sodium dihydrogen phosphate or ammonium phosphate; the molar concentration ratio of the cobalt nitrate to the phosphate solution is 10 (10-15).
In a preferred embodiment of the present invention, in the step (1), the stirring time is 30 to 60 minutes.
In a preferred embodiment of the present invention, in the step (2), the temperature of the hydrothermal reaction is 120-180 ℃; the hydrothermal time is 6-12 hours; more preferably, the hydrothermal time is 6 hours.
The invention also provides the cobalt phosphate catalyst prepared by the preparation method, and the cobalt phosphate nanosheet is of a cobalt phosphate nanosheet structure.
The invention also protects the cobalt phosphate catalyst used for accelerating the degradation of pollutants such as dye pollutants, antibiotics and the like in water by a Peroxymonosulfate (PMS) system.
In a preferred embodiment of the present invention, the cobalt phosphate catalyst concentration is in the range of 0.1 to 0.5 mol L-1The concentration range of the PMS is 0.1-0.5 mol L-1And the pollutant degradation concentration ranges from 20 ppm to 100 ppm.
In a preferred embodiment of the invention, the dye contaminants are Methylene Blue (MB), Methylene Orange (MO), gold orange ii (oii), rhodamine b (rhb), Malachite Green (MG); the antibiotic pollutants are Norfloxacin (NOR), Ofloxacin (OFR) and ibuprofen.
Compared with the prior art, the invention has the beneficial effects that: the cobalt phosphate nanosheet product is prepared by a one-step hydrothermal method and is used as a cobalt phosphate catalyst for efficiently activating PMS, so that the preparation method is simple, green and environment-friendly; in the degradation process, the cobalt phosphate catalyst can effectively activate PMS, accelerate the speed of degrading pollutants such as dye pollutants, antibiotics and the like in a water body by a Peroxymonosulfate (PMS) system, realize the removal rate of more than 95% of high-concentration dye pollutants within 3 minutes of reaction time, realize the removal rate of more than 99% of other pollutants such as high-concentration antibiotics and the like within 6 minutes of reaction time, show excellent degradation rate, greatly widen the application field of the cobalt phosphate catalyst, and is suitable for wide popularization and application.
Drawings
The following is further described with reference to the accompanying drawings:
FIG. 1 is a flow chart of the preparation process of example 1;
FIG. 2 is an X-ray powder diffractogram of cobalt phosphate provided in example 1;
FIG. 3 is an SEM electron micrograph of cobalt phosphate provided in example 1;
FIG. 4 shows that the cobalt phosphate catalyst provided in example 1 activates PMS to accelerate the degradation of various dye contaminants;
FIG. 5 shows that the cobalt phosphate catalyst provided in example 1 activates PMS to accelerate the degradation of contaminants such as antibiotics.
Detailed Description
The process of the present invention is illustrated below by means of specific examples, but the present invention is not limited thereto.
The experimental methods described in the following examples are all conventional methods unless otherwise specified; the reagents and materials are commercially available, unless otherwise specified.
Example 1:
the preparation process is shown in figure 1. Weigh 10 mmol of cobalt nitrate hexahydrate (Co (NO)3)2·6H2O) and 10 mmol of sodium dihydrogen phosphate dihydrate (NaH)2PO4·2H2O) are respectively placed in a beaker, and deionized water is added for dissolution. Under the stirring state, the cobalt nitrate solution is slowly dripped into the sodium dihydrogen phosphate solution by using a dropper, pink purple precipitate is gradually generated, and stirring is continued for 30 minutes until the cobalt nitrate solution is finally changed into purple. And transferring the purple mixed solution to a 100mL polytetrafluoroethylene hydrothermal kettle, and reacting for 6 hours in an oven at 150 ℃. After the reaction is finished, the reaction product is naturally cooled, the product is separated by using a centrifugal mode, and the product is washed for 3 times by using deionized water and ethanol respectively. And drying in an oven at 60 ℃ for 24 hours to obtain the final cobalt phosphate catalyst.
During the degradation process, the concentration of the cobalt phosphate catalyst is 0.2 g L-1PMS concentration of 0.2 g L-1. The dye concentration is 50 ppm, norfloxacin, ofloxacin and ibuprofenThe concentration of the solution was 20 ppm.
As shown in figure 2, the prepared material is verified to be cobalt phosphate nanosheet Co through X-ray powder diffractometer identification3(PO4)2·4H2And O. The morphology of the cobalt phosphate is characterized by using a scanning electron microscope SEM, and as shown in FIG. 3, the prepared cobalt phosphate is in a lamellar shape.
As shown in FIGS. 4-5, at a cobalt phosphate concentration of 0.2 g L-1PMS concentration of 0.2 g L-1Under the condition, the prepared cobalt phosphate nanosheet can effectively activate PMS, rapidly degrade various dyes, antibiotics and the like in the solution, realize the removal rate of more than 95% for dye pollutants in the solution within 3 minutes of reaction time, and realize the removal rate of more than 99% for other pollutants such as antibiotics in the solution within 6 minutes of reaction time.
Example 2:
weigh 10 mmol of cobalt nitrate hexahydrate (Co (NO)3)2·6H2O) and 10 mmol of sodium dihydrogen phosphate dihydrate (NaH)2PO4·2H2O) are respectively placed in a beaker, and deionized water is added for dissolution. Under the stirring state, the cobalt nitrate solution is slowly dripped into the sodium dihydrogen phosphate solution by using a dropper, pink purple precipitate is gradually generated, and stirring is continued for 30 minutes until the cobalt nitrate solution is finally changed into purple. And transferring the purple mixed solution into a 100mL polytetrafluoroethylene hydrothermal kettle, and reacting for 6 hours in an oven at the temperature of 120 ℃. After the reaction is finished, the reaction product is naturally cooled, the product is separated by using a centrifugal mode, and the product is washed for 3 times by using deionized water and ethanol respectively. And drying in an oven at 60 ℃ for 24 hours to obtain the final cobalt phosphate catalyst.
During the degradation process, the concentration of the cobalt phosphate catalyst is 0.2 g L-1PMS concentration of 0.2 g L-1. The dye concentration is 50 ppm, and the concentration of norfloxacin, ofloxacin and ibuprofen solution is 20 ppm. Tests prove that the prepared cobalt phosphate nanosheet can effectively activate PMS, rapidly degrade various dyes, antibiotics and the like in a solution, achieve a removal rate of over 95% for dye pollutants in the solution within 3 minutes of reaction time, and achieve a removal rate of over 99% for other pollutants such as antibiotics in the solution within 6 minutes of reaction time.
Example 3:
weigh 10 mmol of cobalt nitrate hexahydrate (Co (NO)3)2·6H2O) and 10 mmol of sodium dihydrogen phosphate dihydrate (NaH)2PO4·2H2O) are respectively placed in a beaker, and deionized water is added for dissolution. Under the stirring state, the cobalt nitrate solution is slowly dripped into the sodium dihydrogen phosphate solution by using a dropper, pink purple precipitate is gradually generated, and stirring is continued for 30 minutes until the cobalt nitrate solution is finally changed into purple. And transferring the purple mixed solution into a 100mL polytetrafluoroethylene hydrothermal kettle, and reacting for 6 hours in an oven at 180 ℃. After the reaction is finished, the reaction product is naturally cooled, the product is separated by using a centrifugal mode, and the product is washed for 3 times by using deionized water and ethanol respectively. And drying in an oven at 60 ℃ for 24 hours to obtain the final cobalt phosphate catalyst.
During the degradation process, the concentration of the cobalt phosphate catalyst is 0.2 g L-1PMS concentration of 0.2 g L-1. The dye concentration is 50 ppm, and the concentration of norfloxacin, ofloxacin and ibuprofen solution is 20 ppm. Tests prove that the prepared cobalt phosphate nanosheet can effectively activate PMS, rapidly degrade various dyes, antibiotics and the like in a solution, achieve a removal rate of over 95% for dye pollutants in the solution within 3 minutes of reaction time, and achieve a removal rate of over 99% for other pollutants such as antibiotics in the solution within 6 minutes of reaction time.
Example 4:
weigh 10 mmol of cobalt nitrate hexahydrate (Co (NO)3)2·6H2O) and 15 mmol of sodium dihydrogen phosphate dihydrate (NaH)2PO4·2H2O) are respectively placed in a beaker, and deionized water is added for dissolution. Under the stirring state, the cobalt nitrate solution is slowly dripped into the sodium dihydrogen phosphate solution by using a dropper, pink purple precipitate is gradually generated, and stirring is continued for 30 minutes until the cobalt nitrate solution is finally changed into purple. And transferring the purple mixed solution into a 100mL polytetrafluoroethylene hydrothermal kettle, and reacting for 6 hours in an oven at the temperature of 120 ℃. After the reaction is finished, the reaction product is naturally cooled, the product is separated by using a centrifugal mode, and the product is washed for 3 times by using deionized water and ethanol respectively. And drying in an oven at 60 ℃ for 24 hours to obtain the final cobalt phosphate catalyst.
In the degradation process, the concentration of the cobalt phosphate catalyst is 0.2 g L-1, and the concentration of PMS is 0.2 g L-1. The dye concentration is 50 ppm, and the concentration of norfloxacin, ofloxacin and ibuprofen solution is 20 ppm. Tests prove that the prepared cobalt phosphate nanosheet can effectively activate PMS, rapidly degrade various dyes, antibiotics and the like in a solution, achieve a removal rate of over 95% for dye pollutants in the solution within 3 minutes of reaction time, and achieve a removal rate of over 99% for other pollutants such as antibiotics in the solution within 6 minutes of reaction time.
The embodiments described above are some, but not all embodiments of the invention. The detailed description of the embodiments of the present invention is not intended to limit the scope of the invention as claimed, but is merely representative of selected embodiments of the invention. All other embodiments, which can be derived by a person skilled in the art from the embodiments given herein without making any creative effort, shall fall within the protection scope of the present invention.

Claims (8)

1. A preparation method of a cobalt phosphate catalyst capable of efficiently activating PMS is characterized by comprising the following steps:
(1) respectively preparing a cobalt nitrate solution and a phosphate solution, slowly dropping the cobalt nitrate solution into the phosphate solution under the stirring state, and uniformly stirring;
(2) and transferring the mixture into a hydrothermal kettle, carrying out hydrothermal reaction, washing and drying to obtain a cobalt phosphate nanosheet product.
2. The production method according to claim 1, wherein in the step (1), the phosphate is sodium dihydrogen phosphate or ammonium phosphate; the molar concentration ratio of the cobalt nitrate to the phosphate solution is 10 (10-15).
3. The production method according to claim 1, wherein in the step (1), the stirring time is 30 to 60 minutes.
4. The method as claimed in claim 1, wherein the temperature of the hydrothermal reaction in step (2) is 120-180 ℃; the hydrothermal time is 6-12 hours; more preferably, the hydrothermal time is 6 hours.
5. The cobalt phosphate catalyst prepared by the preparation method according to any one of claims 1 to 4, wherein the cobalt phosphate nanosheet is of a cobalt phosphate nanosheet structure.
6. The cobalt phosphate catalyst of claim 5, used for accelerating degradation of pollutants such as dye pollutants, antibiotics and the like in a water body by a Peroxymonosulfate (PMS) system.
7. The use of the cobalt phosphate catalyst according to claim 6 for accelerating the degradation of pollutants such as dye pollutants and antibiotics in a water body by a Peroxymonosulfate (PMS) system, wherein the concentration of the cobalt phosphate catalyst is in the range of 0.1-0.5 mol L-1The concentration range of the PMS is 0.1-0.5 mol L-1And the pollutant degradation concentration ranges from 20 ppm to 100 ppm.
8. The cobalt phosphate catalyst according to claim 6 or 7 is used for accelerating the degradation of pollutants such as dye pollutants, antibiotics and the like in a water body by a Peroxymonosulfate (PMS) system, wherein the dye pollutants are Methylene Blue (MB), Methylene Orange (MO), gold orange II (OII), rhodamine B (RhB), Malachite Green (MG); the antibiotic pollutants are Norfloxacin (NOR), Ofloxacin (OFR) and ibuprofen.
CN202110365431.8A 2021-04-06 2021-04-06 Cobalt phosphate catalyst capable of efficiently activating PMS (permanent magnet synchronous motor), and preparation method and application thereof Pending CN113145145A (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114100613A (en) * 2021-11-23 2022-03-01 哈尔滨工业大学(深圳) Use of cobalt titanate materials and catalyst compositions
CN115286047A (en) * 2021-12-17 2022-11-04 伊犁师范大学 NiFe 2 S 4 Material, preparation method and application thereof

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103408124A (en) * 2013-08-05 2013-11-27 东华大学 Method for treating printing and dyeing wastewater through catalytic oxidation
CN105906102A (en) * 2016-06-11 2016-08-31 华南理工大学 Method for degrading organic wastewater by means of lithium cobalt phosphate active hydrogen monosulfate
CN106824198A (en) * 2017-03-10 2017-06-13 中国科学技术大学 Cobalt-based produces VPO catalysts and preparation method thereof and a kind of alkaline hydrogen manufacturing electrolytic cell
CN110102348A (en) * 2019-05-23 2019-08-09 中国科学院上海硅酸盐研究所 A kind of elctro-catalyst of hollow structure and preparation method thereof
CN111036247A (en) * 2019-10-16 2020-04-21 中国石油大学(华东) Cobalt iron oxide-cobalt phosphate electrocatalytic oxygen evolution composite material and preparation method and application thereof

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103408124A (en) * 2013-08-05 2013-11-27 东华大学 Method for treating printing and dyeing wastewater through catalytic oxidation
CN105906102A (en) * 2016-06-11 2016-08-31 华南理工大学 Method for degrading organic wastewater by means of lithium cobalt phosphate active hydrogen monosulfate
CN106824198A (en) * 2017-03-10 2017-06-13 中国科学技术大学 Cobalt-based produces VPO catalysts and preparation method thereof and a kind of alkaline hydrogen manufacturing electrolytic cell
CN110102348A (en) * 2019-05-23 2019-08-09 中国科学院上海硅酸盐研究所 A kind of elctro-catalyst of hollow structure and preparation method thereof
CN111036247A (en) * 2019-10-16 2020-04-21 中国石油大学(华东) Cobalt iron oxide-cobalt phosphate electrocatalytic oxygen evolution composite material and preparation method and application thereof

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
CHENG-ZONG YUAN,ET AL: ""Cobalt phosphate nanoparticles decorated with nitrogen-doped carbon layers as highly active and stable electrocatalysts for the oxygen evolution reaction"", 《J. MATER. CHEM. A》 *
PENG GUO,ET AL: ""In Situ Coupling Reconstruction of Cobalt−Iron Oxide on a Cobalt Phosphate Nanoarray with Interfacial Electronic Features for Highly Enhanced Water Oxidation Catalysis"", 《ACS SUSTAINABLE CHEM. ENG.》 *
ZHI GENG,ET AL: ""Co3(PO4)2/Ag3PO4 with enhanced simulated sunlight photocatalytic activity toward ofloxacin degradation and mechanism insight"", 《J CHEM TECHNOL BIOTECHNOL》 *

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114100613A (en) * 2021-11-23 2022-03-01 哈尔滨工业大学(深圳) Use of cobalt titanate materials and catalyst compositions
CN114100613B (en) * 2021-11-23 2024-03-26 哈尔滨工业大学(深圳) Use of cobalt titanate material and catalyst composition
CN115286047A (en) * 2021-12-17 2022-11-04 伊犁师范大学 NiFe 2 S 4 Material, preparation method and application thereof
CN115286047B (en) * 2021-12-17 2023-09-22 伊犁师范大学 NiFe 2 S 4 Material, preparation method and application thereof

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Application publication date: 20210723