CN111807475A - Titanium-based diamond-doped lead dioxide electrode and catalytic degradation technology thereof for bentazon - Google Patents

Titanium-based diamond-doped lead dioxide electrode and catalytic degradation technology thereof for bentazon Download PDF

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Publication number
CN111807475A
CN111807475A CN201910284654.4A CN201910284654A CN111807475A CN 111807475 A CN111807475 A CN 111807475A CN 201910284654 A CN201910284654 A CN 201910284654A CN 111807475 A CN111807475 A CN 111807475A
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electrode
electrodeposition
diamond
titanium
preparing
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江波
孙彤
宫怡凡
倪聪聪
刘奕捷
高佳楠
蔡利民
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Qingdao University of Technology
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Qingdao University of Technology
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/467Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
    • C02F1/4672Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electrooxydation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104Devices therefor; Their operating or servicing
    • C02F1/46109Electrodes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104Devices therefor; Their operating or servicing
    • C02F1/46109Electrodes
    • C02F2001/46133Electrodes characterised by the material
    • C02F2001/46138Electrodes comprising a substrate and a coating
    • C02F2001/46142Catalytic coating
    • 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
    • C02F2101/34Organic compounds containing oxygen
    • 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
    • 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
    • C02F2101/40Organic compounds containing sulfur

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  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Electrochemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Electrodes For Compound Or Non-Metal Manufacture (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

The invention discloses a titanium-based diamond-doped lead dioxide electrode and a technology for catalyzing and degrading bentazon by using the same. The preparation method comprises the steps of taking a titanium plate as a substrate, dissolving tin salt and antimony salt according to a certain proportion to form coating liquid, forming tin-antimony oxide through coating and thermal decomposition to serve as a middle layer, preparing diamond-modified beta-PbO 2 on the lead oxide middle layer by adopting an electrodeposition technology, and using doped nano-diamond particles as catalytic active sites to improve the electrocatalysis of an electrode. The lead oxide electrode modified by diamond obtained by the invention is compact and uniform, has small particle size and larger catalytic active area. Meanwhile, the surface active layer has strong adhesive force and is not easy to fall off; the surface is smooth and firm, can resist acid and alkali corrosion, and has good catalytic activity and service life. In addition, the method has the advantages of simple process conditions, low cost and stable performance of the obtained product, is suitable for industrial production, can be widely applied to the field of sewage treatment by an electrocatalytic oxidation technology, and has a far-reaching market prospect.

Description

Titanium-based diamond-doped lead dioxide electrode and catalytic degradation technology thereof for bentazon
Technical Field
The invention relates to a nano-diamond doped lead dioxide composite electrode for removing bentazone in water by oxidation and a preparation method thereof, in particular to a metal oxide with catalytic activity prepared on a titanium plate by heat deposition and electrodeposition, wherein doped nano-diamond particles can be used as catalytic activity sites so as to promote the electrocatalysis of the electrode, and the bentazone in water is oxidized into inorganic matters by electrocatalysis reaction, belonging to the application field of water treatment technology.
Background
The problem of sewage treatment has been the focus of research. With the development of agricultural technology, more and more pesticides are used for crop production, and most of these pollutants are organic pollutants which, when discharged into water, can cause damage to the ecological environment. In the sewage treatment technology, the electrocatalytic oxidation method has low requirements on equipment, high treatment speed, simple and convenient operation, cleanness, no pollution and easy large-scale application, and is an environment-friendly technology. Has been paid extensive attention in recent years, and is an important development direction in the field of sewage treatment in the future. The nature of the anode electrode material has a critical influence on the efficiency of the electrocatalytic oxidation process.
At present, electrocatalytic oxidation is one of advanced oxidation methods, and has the advantages of no need of adding chemicals, small equipment, suitability for combined use with other methods and the like. The anode of electrocatalytic oxidation can generate hydroxyl free radical (. OH) with strong oxidizability in the sewage treatment process, so that organic matters are converted into small molecular organic acid after ring opening or chain breaking, and even completely oxidized into CO2 and H2O. The process for effectively treating the wastewater as a hardly biodegradable organic matter is very worthy of popularization and popularity. A boron-doped diamond (BDD) film is used as an electrode material in a plurality of electrodes, and the special sp3 bond structure and the electrical conductivity of the BDD film endow the BDD electrode with excellent electrochemical characteristics, such as a wide electrochemical potential window, low background current, good physical and chemical stability, low adsorption characteristic and the like. In addition, the diamond is a physical adsorption to hydroxyl radicals and does not react with the surface of the electrode chemically, so that the radicals generated in the polarization process can catalyze, oxidize and degrade organic matters more efficiently, and oxygen evolution side reactions are less. However, the BDD electrode is expensive in manufacturing cost, and if the BDD electrode is put into wastewater treatment in a large scale, great economic investment is caused, and the profitability of enterprises is influenced. The PbO2 electrode has the advantages of high oxygen evolution potential, good stability, good conductivity, corrosion resistance, low price and the like, and has been used as an anode in industrial production for a long time. However, compared with the BDD electrode, the amount of hydroxyl radicals generated is smaller, and thus PbO2 is less catalytically active than the BDD electrode. In addition, the PbO2 coating has large internal stress, and nascent oxygen generated in the electrolytic process is easy to diffuse to the substrate through the surface layer, so that the substrate is passivated, the coating falls off, and the electrochemical stability and the service life of the electrode are reduced. It was found that the internal stress of the PbO2 electrode can be effectively relieved by adding a small amount of nanoparticles (for example, ZrO2, CeO2 and the like) into the plating solution, but the doping of the nanoparticles can not effectively improve the catalytic activity of the PbO2 electrode at the same time. This patent proposes, utilizes nanometer diamond powder modified lead oxide electrode, can increase the active site on electrode surface on the one hand, and the internal stress of lead oxide cladding material can be alleviated in the doping of nanometer particle on the one hand to improve the stability of electrode, finally prepare out the lead oxide electrode similar with BDD electrode catalytic activity.
Disclosure of Invention
According to the defects of the prior art, the invention provides a preparation method of a nanoparticle modified electrode with low manufacturing cost, high activity and stable chemical properties.
The technical scheme of the invention is as follows: dissolving antimony salt, tin salt, an alcohol solution and an acid solution according to a certain proportion to form a coating solution by taking a titanium plate as a substrate, forming tin-antimony oxide as an intermediate layer by coating and thermal decomposition, and preparing diamond-modified beta-PbO 2 on the intermediate layer by adopting an electrodeposition technology.
Wherein, the preferred scheme is as follows:
the intermediate layer coating liquid comprises the following components: 3-25 mL of isopropanol, 0.1-8 mL of concentrated hydrochloric acid, 0.5-10 g of stannic chloride pentahydrate, and 0.1-8 g of antimony trichloride.
The number of times of coating the intermediate layer is different from 5 times to 10 times.
The high-temperature calcination can be carried out at a temperature of 250 ℃ to 800 ℃ and a time of 10min to 60 min.
The current density of the electrodeposition is 20mA/cm 2-50 mA/cm2, the total electrodeposition time is 0.5-1h, the electrodeposition temperature is 25-100 ℃, the electrode spacing is 2.5cm, and the electrodeposition solution comprises 0.1-1 mol/L Pb (NO3)2, 0.05-2 mol/L HNO3, 0.5-2 g/L NaF and 10-200 mg/L nano-diamond.
The invention has the advantages that:
(1) and the doping of the nano-diamond can increase the active sites on the surface of the electrode by doping with common metal nano-particles, so that the degradation rate of pollutants is accelerated.
(2) The internal stress of the lead oxide coating can be reduced through the doping of the nano particles, so that the stability of the electrode is improved.
(3) The extremely stable chemical property of the diamond nano-particles enables the PbO2 electrode to maintain certain electrocatalytic activity in the long-term use process.
Detailed Description
In order to make the objects, technical solutions and advantages of the embodiments of the present invention clearer, the technical solutions in the embodiments of the present invention are clearly and completely described, and it is obvious that the described embodiments are a part of the embodiments of the present invention, but not all of the embodiments. 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.
Example 1:
and (3) polishing the titanium sheet by using sand paper, carrying out alkali washing to remove oil, carrying out oxalic acid etching, ultrasonically cleaning by using deionized water, and then naturally airing.
3.506g of stannic chloride and 0.261g of antimony trichloride are weighed and dissolved in 20mL of isopropanol, then 1mL of hydrochloric acid is weighed and uniformly mixed with the solution, magnetic stirring is adopted until the solution is uniform and stable, the coating solution is dipped by a writing brush and coated on a titanium mesh, then the titanium mesh is placed in an electrothermal constant-temperature drying oven to be dried for 15min at the temperature of 100 ℃, and then the titanium mesh is roasted for 10min at the temperature of 450 ℃ in a muffle furnace. And then taken out for brushing again. After repeating this for 9 times, the resultant was baked in a muffle furnace at 500 ℃ for 1 hour to obtain an intermediate layer.
The surface active layer of the beta-PbO 2 is obtained by electrodeposition, the electrodeposition solution is 0.5mol/L Pb (NO3)2, 0.1mol/L HNO3 and 0.04mol/L NaF, and the current density is 30mA/cm 2. And carrying out electrodeposition for 0.5h at the temperature of 65 ℃ to obtain the undoped lead dioxide electrode.
The electrode is used as the bentazon in the anodic oxidation water, the initial concentration of the bentazon is 100mg/L, the working area is 24cm2 under the conditions of room temperature and acidic pH value, the reaction is carried out for 240min, and the removal rate of the bentazon reaches about 48%.
Example 2:
the pretreatment of the titanium sheet and the preparation of the intermediate layer were as in example 1, except for the components of the bath. The surface active layer of the beta-PbO 2 is obtained by electrodeposition, the used electrodeposition solution is 0.5mol/L Pb (NO3)2, 0.1mol/L HNO3, 0.04mol/L NaF and 0.5g/L nano-diamond powder, and the used current density is 30mA/cm 2. The temperature is 65 ℃, and the electrodeposition is carried out for 0.5h, thus obtaining the lead dioxide electrode with the doping amount of 0.5 g/L.
The electrode is used as bentazon in anodic oxidation water, the initial concentration of the bentazon is 100mg/L, the working area is 24cm2 under the conditions of room temperature and acidic pH value, the reaction is carried out for 240min, the removal rate of the bentazon reaches about 90%, and the service life of the electrode is prolonged.
Example 3:
titanium sheet pretreatment and intermediate layer preparation methods were as in example 1, except that the components of the electrodeposition bath were electrodeposited to obtain a β -PbO2 surface active layer using 0.5mol/L Pb (NO3)2, 0.1mol/L HNO3, 0.04mol/L NaF, 1g/L nanodiamond powder, and using a current density of 30mA/cm 2. The temperature is 65 ℃, and the electrodeposition is carried out for 0.5h, thus obtaining the lead dioxide electrode with the doping amount of 1 g/L.
The electrode is used as bentazon in anodic oxidation water, the initial concentration of the bentazon is 100mg/L, the working area is 24cm2 under the conditions of room temperature and acidic pH value, the reaction is carried out for 240min, the removal rate of the bentazon reaches about 94%, and the service life of the electrode is prolonged.
Example 4:
titanium sheet pretreatment and intermediate layer preparation methods were as in example 1, except that the components of the electrodeposition bath were electrodeposited to obtain a β -PbO2 surface active layer using 0.5mol/L Pb (NO3)2, 0.1mol/L HNO3, 0.04mol/L NaF, 2g/L nanodiamond powder, and using a current density of 30mA/cm 2. The temperature is 65 ℃, and the electrodeposition is carried out for 0.5h, thus obtaining the lead dioxide electrode with the doping amount of 2 g/L.
The electrode is used as bentazon in anodic oxidation water, the initial concentration of the bentazon is 100mg/L, the working area is 24cm2 under the conditions of room temperature and acidic pH value, the reaction is carried out for 240min, the removal rate of the bentazon reaches about 90%, and the service life of the electrode is prolonged.
Although embodiments of the present invention have been shown and described above, it is understood that the above embodiments are exemplary and should not be construed as limiting the present invention, and that variations, modifications, substitutions and alterations can be made in the above embodiments by those of ordinary skill in the art without departing from the principle and spirit of the present invention.

Claims (8)

1. The technology is characterized in that soluble antimony and tin salt are dissolved in an alcohol solvent to prepare a middle layer precursor coating solution, an Sb-SnO2 middle layer is prepared by a coating-drying-thermal sintering method, a beta-PbO 2 catalyst layer is electroplated by an electrodeposition method, a certain amount of nano-diamond powder is added into the electrodeposition solution, and finally the diamond nano-doped modified lead oxide electrode is obtained.
2. A method for preparing the electrode of claim 1, wherein the anode used for electrodeposition is a titanium sheet, a titanium mesh, graphite, stainless steel, a platinum sheet, or the like.
3. The method for preparing the electrode according to claim 1, wherein a brush pen is used for dipping antimony and tin coating liquid, the pretreated titanium plate is coated for 5-10 times, the drying temperature is 80-100 ℃, the calcining temperature is 400-600 ℃, and the time can be varied from 10-60 min.
4. A method for preparing the electrode according to claim 1, wherein the electrolyte solution is an organic substance selected from the group consisting of nitrate, sulfate, sulfamate, tetrahydrofuran, and benzene.
5. The method for preparing the electrode according to claim 1, wherein the concentration of the nanodiamond in the electrodeposition solution is 0.5 to 2 mol/L.
6. The size of the nano diamond is different from 20-50 nm.
7. A method for preparing the electrode according to claim 1, wherein the concentration of boric acid is varied from 0.1 to 0.5 mol/L.
8. An electrodeposition condition as set forth in claim one wherein: the deposition temperature is 60-70 ℃, the current density is 20-40 mA/cm2, the deposition time is 0.5-1h, the stirring speed is about 300-500 r/min in the electrodeposition process, the distance between the polar plates is 1.5-5cm, and the pH value is 1-3.
CN201910284654.4A 2019-04-10 2019-04-10 Titanium-based diamond-doped lead dioxide electrode and catalytic degradation technology thereof for bentazon Pending CN111807475A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115477371A (en) * 2022-09-05 2022-12-16 湖南新锋科技有限公司 Diamond-lead oxide doped coupling electrode and preparation method and application thereof

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CN108301013A (en) * 2018-02-14 2018-07-20 中氧科技(广州)有限公司 A kind of preparation method for the modified anode of lead dioxide generating ozone

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Publication number Priority date Publication date Assignee Title
CN108301013A (en) * 2018-02-14 2018-07-20 中氧科技(广州)有限公司 A kind of preparation method for the modified anode of lead dioxide generating ozone

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115477371A (en) * 2022-09-05 2022-12-16 湖南新锋科技有限公司 Diamond-lead oxide doped coupling electrode and preparation method and application thereof
CN115477371B (en) * 2022-09-05 2023-12-22 湖南新锋科技有限公司 Doped diamond-lead oxide coupling electrode and preparation method and application thereof

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Application publication date: 20201023