CN113060801A - Electrochemical device for treating cyanide-containing wastewater and preparation method and application thereof - Google Patents

Electrochemical device for treating cyanide-containing wastewater and preparation method and application thereof Download PDF

Info

Publication number
CN113060801A
CN113060801A CN202110334829.5A CN202110334829A CN113060801A CN 113060801 A CN113060801 A CN 113060801A CN 202110334829 A CN202110334829 A CN 202110334829A CN 113060801 A CN113060801 A CN 113060801A
Authority
CN
China
Prior art keywords
cyanide
tio
containing wastewater
electrochemical device
graphite felt
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
Application number
CN202110334829.5A
Other languages
Chinese (zh)
Inventor
张亚莉
潘玉博
尉鹏海
黄耀国
贾云
陈琳琳
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Shandong University of Technology
Original Assignee
Shandong University of Technology
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Shandong University of Technology filed Critical Shandong University of Technology
Priority to CN202110334829.5A priority Critical patent/CN113060801A/en
Publication of CN113060801A publication Critical patent/CN113060801A/en
Pending legal-status Critical Current

Links

Images

Classifications

    • 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
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • C02F1/32Treatment of water, waste water, or sewage by irradiation with ultraviolet light
    • 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
    • C02F2001/46133Electrodes characterised by the material
    • C02F2001/46138Electrodes comprising a substrate and a coating
    • 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
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • C02F2101/18Cyanides
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds

Landscapes

  • Chemical & Material Sciences (AREA)
  • Water Supply & Treatment (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Electrochemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Health & Medical Sciences (AREA)
  • Toxicology (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

The invention belongs to the technical field of wastewater treatment, and particularly relates to an electrochemical device for treating cyanide-containing wastewater, and a preparation method and application thereof. The electrochemical device for treating cyanide-containing wastewater comprises a power supply, an anode, a cathode and a container, wherein the power supply is respectively connected with the anode and the cathode, the anode and the cathode are both arranged in the container, and the anode is coated with TiO2The cathode of the graphite felt is a metal sheet. In the invention, TiO is mixed with2Coating gel on porous graphite felt, calcining to obtain electrode, coating TiO2The graphite felt is used as an anode, the metal sheet is used as a cathode, an external power supply is built into an electrochemical device for treating the cyanide-containing wastewater, a new idea is provided for the treatment of the cyanide-containing wastewater,can recover metal zinc and copper while decomposing organic matters, and has high treatment efficiency.

Description

Electrochemical device for treating cyanide-containing wastewater and preparation method and application thereof
Technical Field
The invention belongs to the technical field of wastewater treatment, and particularly relates to an electrochemical device for treating cyanide-containing wastewater, and a preparation method and application thereof.
Background
Cyanide is a highly toxic chemical and is commonly used in various industrial processes including electroplating, gold and silver extraction, coal processing, nylon production and smelting. Due to the widespread use of cyanide in industry, large quantities of cyanide ions are often generated in industrial waste water. Gold, silver and other metals are extracted from ores by cyanide, and these processes are considered to be the most productive processes of cyanide waste water. Cyanide can be present not only in these industrial waste waters as free ions (CN-) but also bound to metal ions due to its strong binding force to metals. When cyanide comes into contact with dissolved metal ions, metal-cyanide complexes are formed. Although the cyanidation method is effective in extracting gold and silver, metal substances such as copper and zinc are dissolved in the ore. Therefore, cyanide wastewater must be treated to minimize the risk to health and the environment.
In recent years, the environmental protection problem is more and more emphasized, and higher environmental protection requirements are put forward for enterprises. The alkaline chlorination process is a commonly used method for treating cyanide-containing wastewater at present, but the method has the defect of generating cyanogen gas. In addition, the process uses a large amount of caustic soda and sodium hypochlorite, which causes serious corrosion to pipelines and equipment. To date, particularly from the viewpoint of large-scale industrial application, there has been no method capable of satisfying the requirements of the conventional cyanide wastewater treatment process, and therefore, the development of a new process for treating a large amount of cyanide-containing wastewater is urgent. One of the effective methods for purifying water pollutants and other toxic substances is the photocatalytic process, and most photocatalysts are metal oxides of semiconductor materials. Many photocatalysts such as ZnO and WO have been synthesized3、CdS、ZrO2、SnO2、BiVO4、TiO2And the like, and has higher photocatalytic activity. TiO 22It is best known for its high photocatalytic activity, good photostability, nontoxicity, repeated use without loss of activityA photocatalyst. But nano TiO2The particles have small particle size and high surface energy, and are easy to agglomerate, so that the effective surface area is reduced, and the catalytic efficiency is further reduced. Mixing nanometer TiO2The carrier surface is loaded on the carrier surface, which is an effective method for improving the dispersity and increasing the specific surface area. Some porous materials are often used as supports, such as silica gel, alumina, zeolite molecular sieves, clays, activated carbon. The carrier can be TiO with stronger oxidation-reduction performance2Provides an environment with higher substrate concentration, and improves the photocatalytic efficiency by enriching degraded substrate molecules. Whether nano TiO is used alone2Or nano TiO2The carrier is supported on a carrier, and the carrier is present in a powder state in a solution, and the solution needs to be filtered, and the metal is adsorbed on the catalytic material, and the metal ions adsorbed on the material need to be resolved, so that the carrier can be used continuously.
Chinese patent CN 108675382A discloses a TiO-based material2Integrated catalytic system of nanotube photocatalyst and degradation treatment method thereof based on TiO2Integrated catalytic system of nanotube photocatalyst comprising TiO2Nanotube, visible light source or sunlight, electric catalytic unit, and oxygen pump; the electrocatalytic device is made of TiO2The nanotube is an anode, the fibrous graphite felt is a cathode, and the anode and the cathode are both inserted into the organic wastewater and are respectively connected to the anode and the cathode of the voltage-stabilized power supply; the visible light source or the sunlight correspondingly irradiates the anode; fe is added into the organic wastewater2+The oxygenation pump is located at the cathode. By reacting with TiO2Applying external bias to the nanotube to form an external electric field environment to form TiO2The combination of photocatalysis and electrocatalysis, and further introduces Fenton reaction to form TiO2The integrated catalytic system with the synergistic effect of the mutual coupling of the visible light catalytic reaction, the electrocatalytic reaction and the Fenton reaction of the nanotube greatly improves the degradation efficiency of toxic refractory organic pollutants. In the patent, Ti-N alloy sheet is taken as an anode, organic solution containing a boron source is taken as electrolyte to carry out electrochemical anodic oxidation reaction, and N and B are doped into TiO2Soaking the N, B co-doped titanium dioxide nanotube in PdCl2The PdO loaded N, B co-doped titanium dioxide nanotube photocatalyst is prepared by drying and calcining in the solution, the preparation process is complex, the economic cost is high, palladium is loaded on the surface of the titanium dioxide nanotube in a PdO form, and Fe is required to be added in the treatment process2+Oxidized into Fe by hydrogen peroxide3+And hydroxyl radicals, and can further oxidize and decompose organic substances.
At present, it is demanded to provide an electrochemical device for treating cyanide-containing wastewater, which can decompose organic substances and recover metals at the same time and has high treatment efficiency.
Disclosure of Invention
The invention aims to provide an electrochemical device for treating cyanide-containing wastewater, which has simple structure, convenient operation, high treatment efficiency and capability of simultaneously decomposing organic matters and recovering metals; the invention also provides a preparation method and application of the electrochemical device for treating the cyanide-containing wastewater.
The electrochemical device for treating cyanide-containing wastewater comprises a power supply, an anode, a cathode and a container, wherein the power supply is respectively connected with the anode and the cathode, the anode and the cathode are both arranged in the container, and the anode is coated with TiO2The cathode of the graphite felt is a metal sheet.
The metal sheet is a copper sheet or a platinum sheet.
The container is a cylindrical container.
The preparation method of the electrochemical device for treating cyanide-containing wastewater comprises the following steps:
(1) mixing butyl titanate, absolute ethyl alcohol and diethanol amine to obtain a first mixed solution; adding concentrated nitric acid into water to adjust the pH value to obtain a second mixed solution, dropwise adding the second mixed solution into the first mixed solution, stirring and aging to obtain TiO2Gelling;
(2) inserting graphite felt into TiO2Soaking in gel, pulling out at constant speed, drying, roasting, and coating for the first time; repeating the coating after cooling to obtain the coated TiO2The graphite felt of (4);
(3) will coat TiO2The graphite felt and the metal sheet are put into a container and coated with TiO2The graphite felt and the metal sheet are respectively connected with the anode and the cathode of a power supply to assemble the electrochemical device for treating the cyanide-containing wastewater.
The molar ratio of the butyl titanate, the water, the absolute ethyl alcohol, the diethanolamine to the concentrated nitric acid in the step (1) is 0.8-1:0.8-1:8-10:0.8-1: 0.05-0.15.
The pH value in the step (1) is 2.5-3.5.
The dropping speed in the step (1) is 1-5 drops/second.
The stirring time in the step (1) is 0.5-2 h.
The aging described in the step (1) is aging in air.
The aging time in the step (1) is 24-36 hours.
The dipping time in the step (2) is 10-30 min.
The constant pulling speed in the step (2) is 1-3mm per second.
The graphite felt in the step (2) has the width of 1.5cm, the height of 12cm and the thickness of 3 mm.
The graphite felt in the step (2) is a hard graphite felt.
The roasting temperature in the step (2) is 350-500 ℃.
The repetition times in the step (2) are 3-9 times.
The electrochemical device for treating cyanide-containing wastewater is applied by firstly placing cyanide-containing wastewater in a container and then coating TiO2The graphite felt and the metal sheet are inserted into the cyanide-containing wastewater and coated with TiO2The graphite felt and the metal sheet are respectively connected with the anode and the cathode of a power supply, and finally, the graphite felt and the metal sheet are electrified under the illumination condition, so that the graphite felt and the metal sheet are obtained.
The voltage of the power supply is 10-30V.
The electrifying time is 2-7 hours.
The illumination condition is visible light illumination or ultraviolet light illumination, the light wavelength is 365-.
The electrochemical device for treating the cyanide-containing wastewater is applied to placing the cyanide-containing wastewater in a cylindrical containerWill be coated with TiO2The graphite felt and the metal sheet are vertically put into a container and coated with TiO2The graphite felt and the metal sheet are parallel to each other and coated with TiO2The graphite felt and the metal sheet are respectively connected with a power supply anode and a power supply cathode, and the concentrations of cyanide and copper-zinc metal in the cyanide-containing wastewater are analyzed after the graphite felt and the metal sheet are electrified under the illumination condition, so that the treatment effect is calculated.
The cyanide concentration in the cyanide-containing wastewater is 1-100ppm, the copper concentration is 10-30ppm, and the zinc concentration is 10-30 ppm; the cylindrical container is a glass container with a diameter of 5cm and a height of 10 mm.
The coated TiO2The spacing between the graphite felt and the metal sheet was 2 cm.
In the invention, TiO is mixed with2Coating gel on porous graphite felt, calcining to obtain electrode, coating TiO2The graphite felt is used as an anode, the metal sheet is used as a cathode, and an external power supply is built into an electrochemical device for treating cyanide-containing wastewater, thereby providing a new idea for the treatment of the cyanide-containing wastewater.
The principle of the invention is as follows:
in the electrolytic process H2Decomposition of O will produce O2。TiO2After irradiation with light, TiO2The electrons in the valence band are excited into the conduction band to form negatively charged highly active electrons e-Simultaneously, a positively charged hole h is formed in the valence band+Electron-hole pairs are formed. Electronic quilt O2Trapped, changed to O2 -. The hole combines with the OH-to form OH. The electrons are separated from the holes, and the holes diffuse to the catalyst surface. CN in solution-、[Cu(CN)3]2-、[Zn(CN)4]2-Moves to the surface of the anode under the action of an electric field and oxidizes CN under the action of a cavity-Is CN, is further oxidized into CNO under the action of hydroxyl radical, [ Cu (CN)3]2Oxidation by cavitation of the end product to Cu2+With a cyano radical, [ Zn (CN) ]4]2Oxidation by holes to Zn2+And a cyano radical. CNO further oxidized to NO2、CO2、H2O。Cu2+、Zn2+Reduced to metal deposit at the cathode.
The anode reaction is as follows:
Figure BDA0002997032400000041
TiO2+Av→e-+A+
OH-+h+→OH·
Figure BDA0002997032400000042
CN-+h+→·CN
[Cu(CN)3]2-+h+→[Cu(CN)2]-+·CN
[Cu(CN)2]-+h+→Cu(CN)+·CN
Cu(CN)+2h+→Cu2++·CN
[Zn(CN)4]2-+4h+→Zn2++4·CN
CN·+2OH·→H2O+·OCN
·OCN+2·OH+O2→O-N-O+CO2+H2O
the cathode reaction is as follows:
Zn2++2e=ZnCn2++2e=Cu
the invention has the following beneficial effects:
the invention utilizes a gel sol method to prepare titanium gel, adopts a stretching method to coat the gel on the surface of a graphite felt, obtains an anode after calcination, and takes a metal sheet as a cathode. When the cyanide-containing wastewater is treated, oxygen does not need to be introduced, and the oxygen generated in the electrolytic process is utilized to directly capture the nano TiO in the illumination process2The generated photo-generated electrons prevent the photo-generated electrons from being combined with holes. The holes oxidize cyanide in the cyanide-containing wastewater to decompose the cyanide, so that copper ions and zinc ions are released, and meanwhile, under the action of electric field force, the copper ions and the zinc ions obtain electrons at the cathode and are deposited at the cathode in a metal form. The anode of the invention is preparedThe process is simple, the metal zinc and copper can be recovered while the organic matters are decomposed, and the treatment efficiency is high.
Drawings
Fig. 1 is a schematic diagram of the principle of the present invention.
Detailed Description
The present invention is further described below with reference to examples.
Example 1
An electrochemical device for treating cyanide-containing wastewater comprises a power supply, an anode, a cathode and a container, wherein the power supply is respectively connected with the anode and the cathode, the anode and the cathode are both arranged in the container, and the anode is coated with TiO2The cathode of the graphite felt is a metal sheet.
The metal sheet is a copper sheet.
The container is a cylindrical container.
The preparation method of the electrochemical device for treating the cyanide-containing wastewater comprises the following steps:
(1) adding butyl titanate, absolute ethyl alcohol and diethanol amine into a flask, and stirring for 20min to obtain a first mixed solution; adding water into a beaker, adding concentrated nitric acid, and adjusting the pH value to 3 to obtain a second mixed solution; dripping the second mixed solution into the flask at the speed of 1 drop/s, stirring for 1h to obtain light yellow transparent sol, and aging for 2 days to obtain TiO2Gelling; the molar ratio of the butyl titanate, the water, the absolute ethyl alcohol, the diethanolamine to the concentrated nitric acid is 1:1:10:1: 0.08;
(2) inserting a hard graphite felt into the TiO2Soaking in gel for 30min, uniformly pulling out at a height of 2mm per second, drying, roasting at 400 deg.C in a muffle furnace, and coating for the first time; cooling and then inserting TiO2In the gel, carrying out secondary coating; the coating was repeated 5 times to obtain a coated TiO2The graphite felt of (4);
(3) will coat TiO2The graphite felt and the metal sheet are put into a container and coated with TiO2The graphite felt and the metal sheet are respectively connected with the anode and the cathode of a power supply to assemble the electrochemical device for treating the cyanide-containing wastewater.
The application of the electrochemical device for treating the cyanide-containing wastewater is that the cyanide-containing wastewater (the total cyanide concentration is 7)1ppm, copper concentration 26ppm and zinc concentration 14ppm) was placed in a cylindrical container and the coated TiO was again placed2The graphite felt and the metal sheet are inserted into the cyanide-containing wastewater and coated with TiO2The spacing between the graphite felt and the metal sheet was 2 cm. Coating TiO2The graphite felt and the metal sheet are respectively connected with an anode and a cathode of a power supply, the concentrations of cyanide and copper and zinc in the cyanide-containing wastewater are analyzed after the power supply is electrified for 5 hours under the irradiation of visible light, the removal rates of the cyanide, the copper and the zinc are respectively 92%, 97% and 95%, and the copper and the zinc are deposited on the copper sheet in a metal form.
Example 2
An electrochemical device for treating cyanide-containing wastewater comprises a power supply, an anode, a cathode and a container, wherein the power supply is respectively connected with the anode and the cathode, the anode and the cathode are both arranged in the container, and the anode is coated with TiO2The cathode of the graphite felt is a metal sheet.
The metal sheet is a copper sheet.
The container is a cylindrical container.
The preparation method of the electrochemical device for treating the cyanide-containing wastewater comprises the following steps:
(1) adding butyl titanate, absolute ethyl alcohol and diethanol amine into a flask, and stirring for 20min to obtain a first mixed solution; adding water into a beaker, adding concentrated nitric acid, and adjusting the pH value to 3 to obtain a second mixed solution; dripping the second mixed solution into the flask at the speed of 2 drops/s, stirring for 2 hours to obtain light yellow transparent sol, and aging for 2 days to obtain TiO2Gelling; the molar ratio of the butyl titanate, the water, the absolute ethyl alcohol, the diethanol amine and the concentrated nitric acid is 0.8: 0.8: 8: 0.8: 0.05;
(2) inserting a hard graphite felt into the TiO2Soaking in gel for 30min, uniformly pulling out at a height of 1mm per second, drying, roasting at 500 deg.C in a muffle furnace, and coating for the first time; cooling and then inserting TiO2In the gel, carrying out secondary coating; the coating was repeated 5 times to obtain a coated TiO2The graphite felt of (4);
(3) will coat TiO2The graphite felt and the metal sheet are put into a container and coated with TiO2The graphite felt and the metal sheet are respectively connected with the anode and the cathode of a power supply to be assembled for useAn electrochemical device for treating cyanide-containing wastewater.
The electrochemical device for treating cyanide-containing waste water is applied by firstly placing cyanide-containing waste water (total cyanide concentration 71ppm, copper concentration 26ppm and zinc concentration 14ppm) in a cylindrical container and then coating TiO2The graphite felt and the metal sheet are inserted into the cyanide-containing wastewater and coated with TiO2The spacing between the graphite felt and the metal sheet was 2 cm. Coating TiO2The graphite felt and the metal sheet are respectively connected with an anode and a cathode of a power supply, the concentrations of cyanide and copper and zinc in the cyanide-containing wastewater are analyzed after the anode and the cathode are electrified for 7 hours under the irradiation of ultraviolet light, the removal rates of the cyanide, the copper and the zinc are respectively 94.5%, 98% and 99%, and the copper and the zinc are deposited on the copper sheet in a metal form.
Example 3
An electrochemical device for treating cyanide-containing wastewater comprises a power supply, an anode, a cathode and a container, wherein the power supply is respectively connected with the anode and the cathode, the anode and the cathode are both arranged in the container, and the anode is coated with TiO2The cathode of the graphite felt is a metal sheet.
The metal sheet is a copper sheet.
The container is a cylindrical container.
The preparation method of the electrochemical device for treating the cyanide-containing wastewater comprises the following steps:
(1) adding butyl titanate, absolute ethyl alcohol and diethanol amine into a flask, and stirring for 20min to obtain a first mixed solution; adding water into a beaker, and adding concentrated nitric acid to adjust the pH value to 3.5 to obtain a second mixed solution; dripping the second mixed solution into the flask at the speed of 3 drops/s, stirring for 1h to obtain light yellow transparent sol, and aging for 2.5 days to obtain TiO2Gelling; the molar ratio of the butyl titanate, the water, the absolute ethyl alcohol, the diethanol amine and the concentrated nitric acid is 1:1:10:1: 0.15;
(2) inserting a hard graphite felt into the TiO2Soaking in gel for 20min, uniformly pulling out at a height of 3mm per second, drying, roasting in a muffle furnace at 350 deg.C, and coating for the first time; cooling and then inserting TiO2In the gel, carrying out secondary coating; the coating was repeated 5 times to obtain a coated TiO2The graphite felt of (4);
(3) will be provided withCoating TiO2The graphite felt and the metal sheet are put into a container and coated with TiO2The graphite felt and the metal sheet are respectively connected with the anode and the cathode of a power supply to assemble the electrochemical device for treating the cyanide-containing wastewater.
The electrochemical device for treating cyanide-containing waste water is applied by firstly placing cyanide-containing waste water (total cyanide concentration is 75ppm, copper concentration is 30ppm, and zinc concentration is 16ppm) in a cylindrical container and then coating TiO2The graphite felt and the metal sheet are inserted into the cyanide-containing wastewater and coated with TiO2The spacing between the graphite felt and the metal sheet was 2 cm. Coating TiO2The graphite felt and the metal sheet are respectively connected with an anode and a cathode of a power supply, the concentrations of cyanide and copper and zinc in the cyanide-containing wastewater are analyzed after the anode and the cathode are electrified for 7 hours under the irradiation of visible light, the removal rates of the cyanide, the copper and the zinc are respectively 98%, 99% and 100%, and the copper and the zinc are deposited on the copper sheet in a metal form.

Claims (10)

1. An electrochemical device for treating cyanide-containing wastewater comprises a power supply, an anode, a cathode and a container, and is characterized in that the power supply is respectively connected with the anode and the cathode, the anode and the cathode are both arranged in the container, and the anode is coated with TiO2The cathode of the graphite felt is a metal sheet.
2. The electrochemical device for treating cyanide-containing wastewater according to claim 1, wherein the metal sheet is a copper sheet or a platinum sheet.
3. A method for preparing an electrochemical device for treating cyanide-containing wastewater according to claim 1 or 2, characterized by comprising the steps of:
(1) mixing butyl titanate, absolute ethyl alcohol and diethanol amine to obtain a first mixed solution; adding concentrated nitric acid into water to adjust the pH value to obtain a second mixed solution, dropwise adding the second mixed solution into the first mixed solution, stirring and aging to obtain TiO2Gelling;
(2) inserting graphite felt into TiO2Soaking in gel, pulling out at constant speed, drying, roasting, and coating for the first time; repeating the coating after cooling to obtain a coatingCoated with TiO2The graphite felt of (4);
(3) will coat TiO2The graphite felt and the metal sheet are put into a container and coated with TiO2The graphite felt and the metal sheet are respectively connected with the anode and the cathode of a power supply to assemble the electrochemical device for treating the cyanide-containing wastewater.
4. The method of claim 3, wherein the molar ratio of butyl titanate, water, absolute ethanol, diethanolamine to concentrated nitric acid in step (1) is 0.8-1:0.8-1:8-10:0.8-1: 0.05-0.15.
5. The method for preparing an electrochemical device for the treatment of cyanide-containing wastewater according to claim 3, wherein the pH in the step (1) is 2.5 to 3.5.
6. The method for preparing an electrochemical device for the treatment of cyanide-containing wastewater according to claim 3, wherein the dropping speed in step (1) is 1-5 drops/sec, the stirring time is 0.5-2 hours, and the aging time is 24-36 hours.
7. The method for preparing an electrochemical device for treating cyanide-containing wastewater as claimed in claim 3, wherein the dipping time in step (2) is 10-30min, the constant pulling speed is 1-3mm per second, the calcination temperature is 350-500 ℃, and the repetition times are 3-9 times.
8. Use of an electrochemical device according to claim 1 or 2 for the treatment of cyanide-containing waste water, characterized in that the cyanide-containing waste water is first placed in a container and the TiO-coated water is then applied2The graphite felt and the metal sheet are inserted into the cyanide-containing wastewater and coated with TiO2The graphite felt and the metal sheet are respectively connected with the anode and the cathode of a power supply, and finally, the graphite felt and the metal sheet are electrified under the illumination condition, so that the graphite felt and the metal sheet are obtained.
9. The use of an electrochemical device according to claim 8 for the treatment of cyanide-containing wastewater, characterized in that the voltage of the power supply is 10-30V and the energization time is 2-7 hours.
10. The use of the electrochemical device for treating cyanide-containing wastewater as claimed in claim 8, wherein the illumination condition is visible light illumination or ultraviolet light illumination, the light wavelength is 365-.
CN202110334829.5A 2021-03-29 2021-03-29 Electrochemical device for treating cyanide-containing wastewater and preparation method and application thereof Pending CN113060801A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202110334829.5A CN113060801A (en) 2021-03-29 2021-03-29 Electrochemical device for treating cyanide-containing wastewater and preparation method and application thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202110334829.5A CN113060801A (en) 2021-03-29 2021-03-29 Electrochemical device for treating cyanide-containing wastewater and preparation method and application thereof

Publications (1)

Publication Number Publication Date
CN113060801A true CN113060801A (en) 2021-07-02

Family

ID=76564275

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202110334829.5A Pending CN113060801A (en) 2021-03-29 2021-03-29 Electrochemical device for treating cyanide-containing wastewater and preparation method and application thereof

Country Status (1)

Country Link
CN (1) CN113060801A (en)

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1712130A (en) * 2005-04-30 2005-12-28 中国地质大学(武汉) Manufacture of Ag+-Fe+ dosed TiO2 weakly exciting catalytic luminating film
US20060049064A1 (en) * 2002-11-04 2006-03-09 Andras Horvath Process for electrochemical oxidation of ferrocyanide to ferricyanide
CN106395998A (en) * 2016-10-18 2017-02-15 华东理工大学 Salt-containing wastewater resourceful treatment method
CN110655142A (en) * 2019-10-25 2020-01-07 招远市河西金矿 Method for treating cyanide-containing wastewater by photoelectrocatalysis

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20060049064A1 (en) * 2002-11-04 2006-03-09 Andras Horvath Process for electrochemical oxidation of ferrocyanide to ferricyanide
CN1712130A (en) * 2005-04-30 2005-12-28 中国地质大学(武汉) Manufacture of Ag+-Fe+ dosed TiO2 weakly exciting catalytic luminating film
CN106395998A (en) * 2016-10-18 2017-02-15 华东理工大学 Salt-containing wastewater resourceful treatment method
CN110655142A (en) * 2019-10-25 2020-01-07 招远市河西金矿 Method for treating cyanide-containing wastewater by photoelectrocatalysis

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
YANG ZHANG ET AL.: "Enhanced photocatalytic reaction and mechanism for treating cyanide-containing wastewater by silicon-based nano-titania", 《HYDROMETALLURGY》 *
王立久: "《建筑材料工艺原理》", 31 March 2006, 中国建材工业出版社 *

Similar Documents

Publication Publication Date Title
Li et al. A ClO-mediated photoelectrochemical filtration system for highly-efficient and complete ammonia conversion
Zhang et al. Preparation of Fenton reagent with H2O2 generated by solar light-illuminated nano-Cu2O/MWNTs composites
Lou et al. TiC doped palladium/nickel foam cathode for electrocatalytic hydrodechlorination of 2, 4-DCBA: Enhanced electrical conductivity and reactive activity
CN101798126A (en) Method for treating industrial waste water by means of photoelectrocatalysis
CN1263686C (en) Photoelectrocatalysis and oxidation device for treating organic substance in water
CN102690005A (en) Method for treating organic wastewater through photoelectric catalytic oxidation
US20200165148A1 (en) A method using photocatalytic electrode coupled with microbial fuel cell to promote treatment of coking wastewater
Gai et al. An alternative scheme of biological removal of ammonia nitrogen from wastewater–highly dispersed Ru cluster@ mesoporous TiO2 for the catalytic wet air oxidation of low-concentration ammonia
CN101492199A (en) Method for removing arsenic with platinum doped titanium dioxide photoelectrocatalysis oxidization
CN104628200A (en) Method for treating organic wastewater by photoelectric combined technique
CN102240550A (en) Low-concentration copper-doped titanium dioxide nanotube photocatalyst and preparation method thereof
CN108675382B (en) Based on TiO2Integrated catalytic system of nanotube photocatalyst and degradation treatment method thereof
Zha et al. Treatment of hazardous organic amine wastewater and simultaneous electricity generation using photocatalytic fuel cell based on TiO2/WO3 photoanode and Cu nanowires cathode
CN106395998A (en) Salt-containing wastewater resourceful treatment method
CN113353932A (en) Hierarchical pore charcoal electrocatalyst prepared from pitaya peel and preparation method and application thereof
Chen et al. Efficient degradation of ciprofloxacin by Cu2O/g-C3N4 heterostructures with different morphologies driven under the visible light
CN107188265B (en) Method for treating heavy metal complex wastewater based on UV/chlorine advanced oxidation technology
Kunthakudee et al. Photocatalytic recovery of gold from a non-cyanide gold plating solution as Au nanoparticle-decorated semiconductors
Wei et al. Effect and mechanism of cyanide degradation and Cu/Zn recovery by photoelectro-catalytic oxidation
Candia-Onfray et al. Degradation of contaminants of emerging concern in a secondary effluent using synthesized MOF-derived photoanodes: A comparative study between photo-, electro-and photoelectrocatalysis
CN112723493B (en) Cobaltosic oxide/magnesium oxide-titanium composite electrode, preparation method and application thereof, and treatment method of ammonia nitrogen-containing wastewater
CN113198515A (en) Ternary photocatalyst and preparation method and application thereof
CN113493237A (en) Preparation of modified nano-iron and method for treating high-concentration nitrate wastewater by using modified nano-iron
CN113060801A (en) Electrochemical device for treating cyanide-containing wastewater and preparation method and application thereof
CN102211832B (en) Method for treating cutting fluid wastewater by photocatalytic oxidation

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20210702