CN102531108A - Lead dioxide electrode, production method thereof, application of lead dioxide electrode to quickly decoloring azo dyes and method for quickly decoloring azo dyes by using lead dioxide electrode - Google Patents

Lead dioxide electrode, production method thereof, application of lead dioxide electrode to quickly decoloring azo dyes and method for quickly decoloring azo dyes by using lead dioxide electrode Download PDF

Info

Publication number
CN102531108A
CN102531108A CN2012100065149A CN201210006514A CN102531108A CN 102531108 A CN102531108 A CN 102531108A CN 2012100065149 A CN2012100065149 A CN 2012100065149A CN 201210006514 A CN201210006514 A CN 201210006514A CN 102531108 A CN102531108 A CN 102531108A
Authority
CN
China
Prior art keywords
titanium plate
lead dioxide
dioxide electrode
mol
electrode
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
CN2012100065149A
Other languages
Chinese (zh)
Inventor
李琴
张秋
安浩
崔皓
钱言
李保菊
翟建平
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.)
Nanjing University
Original Assignee
Nanjing University
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 Nanjing University filed Critical Nanjing University
Priority to CN2012100065149A priority Critical patent/CN102531108A/en
Publication of CN102531108A publication Critical patent/CN102531108A/en
Pending legal-status Critical Current

Links

Images

Landscapes

  • Electrodes For Compound Or Non-Metal Manufacture (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

The invention discloses a lead dioxide electrode, a production method thereof, an application of the lead dioxide electrode to quickly decoloring azo dyes and a method for quickly decoloring azo dyes by using the lead dioxide electrode, wherein the electrode is obtained after polishing, alkali washing, acid washing, electrolyzing and calcinating a titanium plate. Under the condition that the current is constant, the produced modified lead dioxide electrode is utilized to decolor the azo dyes through controlling current density, conduction time and other factors. The method does not bring other chemical substances in, and does not cause secondary pollution, and has the advantages of temperate reaction condition, convenience for operation and the like. After a power supply is connected, the azo dyes can be effectively decolored within a short time, the decoloring efficiency is high, and the speed is fast.

Description

A kind of lead dioxide electrode, its preparation method and application and method in azoic dyestuff decolours fast
 
Technical field
The invention belongs to the environmental pollution improvement field, relate to a kind of method of electrochemical catalytic oxidation, specifically be a kind of lead dioxide electrode, its preparation method and utilizing electrochemical catalytic oxidation to make the azoic dyestuff application in the decolouring fast.
Background technology
Waste water from dyestuff is the main source that textile industry water pollutes; Has " three high one is low " obvious characteristic; Be characteristics such as colourity is high, toxicity is high, salinity is high, BOD/COD is low; Thereby be difficult to by biological degradation, not only can't use traditional biochemical process that it is effectively removed, also might cause the paralysis of biochemical system.
Azo dyes is the staple commodities classification of dyestuff, in dyestuff, uses the most extensively, and nearly 2/3 is azo dyes in the dyestuff that on market, circulates.As one of which, contain one or more aromatic ring structures, azo dyes character is very stable, and very easily decomposes the generation carcinogenic aromatic amine under the anaerobic environment, is one of current waste water from dyestuff that pollutes very seriously, demands urgently administering of China.
The treatment technology of waste water from dyestuff mainly contains Coagulation Method, advanced oxidation processes, absorption method, membrane separation process and electrochemical process etc. at present.These method general technology long flow paths, treating processes is slow, and intermediate product is many, causes secondary pollution easily, and cost is also relatively more expensive.
In recent years, utilized electrochemical catalytic oxidation technical finesse organic waste water to become the domestic and international research focus.A lot of about the relevant report of utilizing electrode materials catalyzed oxidation phenolic wastewater at present; Also fewer about the application and the report of degraded azo class waste water, this mainly is owing to fail to develop the electrode materials that has effective catalytic effect for the complicated pollutent of this class formation of dyestuff.Therefore, many investigators are just attempting to prepare the electrode that baroque pollutent is also had extremely strong catalytic capability, wherein to boron-doped diamond, PbO 2Modification etc. classical electrode is present research focus.
Summary of the invention
Technical problem to be solved by this invention provides a kind of modification lead dioxide electrode and preparation method thereof, the application that this electrode can effectively decolour to azo dyes fast.
A kind of lead dioxide electrode material of the present invention, it is prepared from following steps:
1) the titanium plate is polished, make titanium plate surface demonstrate the light grey gloss of homogeneous;
2) the titanium plate after will polishing carries out alkali cleaning, removes the pollutent on titanium plate surface;
3) the titanium plate after the alkali cleaning carries out pickling, removes the TiO on titanium plate surface 2
4) the titanium plate after step 3) is handled is made anode, Pt is a negative electrode, with 0.5 ~ 2 wt%NaF, 1 ~ 5 wt%Na 2SO 4, 5 ~ 20 wt% polyoxyethylene glycol and ultrapure water be configured to electrolytic solution, the constant voltage etching is 1 ~ 3 hour under 15 ~ 25 V conditions, then in retort furnace in 500 ~ 550 ℃ of calcinings 1.5 ~ 3 hours down;
5) with Pt be anode, the titanium plate after step 4) is handled is made negative electrode, 0.5 ~ 1.5 mol/L (NH 4) 2SO 4Be electrolytic solution, the constant voltage energising is 0.1 ~ 10 minute under 1.5 ~ 2 V conditions;
6) titanium plate that will be after step 5) is handled is at 1 ~ 2 mol/L CuSO 4Under 35 ~ 45 ℃ of conditions, adopt pulse current method to handle in the solution 5 ~ 15 minutes;
7) with above-mentioned steps 6) titanium plate after handling is as anode, and copper coin is a negative electrode, and electrolytic solution is by 0.05 ~ 0.5 mol/L HNO 3, 0.1 ~ 1.5 mol/L Pb (NO 3) 2, 0.01 ~ 0.1 mol/L NaF and 0.1 ~ 1 wt% PDDA mix, at constant current 5 ~ 40 mA/cm 2, 50 ~ 90 ℃, handle after 30 ~ 90 minutes, use the deionized water thorough washing totally promptly to get the modification lead dioxide electrode.
Step 2) process of alkali cleaning is that the titanium plate after the polishing is immersed 40 ~ 60 wt% NaOH solution, and the pollutent on titanium plate surface is removed in 60 ~ 80 ℃ of following alkali cleanings 2 ~ 4 hours.
The process of step 3) pickling is that the titanium plate after the alkali cleaning immerses in 10 ~ 20 wt% oxalic acid solutions in 60 ~ 95 ℃ of following pickling 2 ~ 4 hours.
The process of step 6) pulse current method is: handle 5 ~ 15 ms with the cathode pulse of-50 ~-80 mA earlier, handle 0.5 ~ 2 ms with the anodic pulse of 60 ~ 80 mA again, then lax 0.5 ~ 5 s repeats above-mentioned steps then.
The present invention also provides the application of this lead dioxide electrode material in azo dyes decolours fast.
Lead dioxide electrode material of the present invention makes the azoic dyestuff method of decolouring fast in electrochemical catalytic oxidation, the steps include: that the modification plumbic oxide with preparation is an anode, constant current 50 ~ 500 mA/cm 2Under the condition, place phenolic wastewater, the quick decolouring of switching on and realizing azoic dyestuff in 0.5 ~ 5 hour.
Spacing is 10 millimeters between above-mentioned anode and cathode.
Modification plumbic oxide of the present invention is an anode, at traditional P bO 2Add tensio-active agent polydiene propyl-dimethyl amine hydrochlorate (PDDA) in the electrode synthetic electrolytic solution; Through the control hydrothermal synthesizing condition; To improve the homogeneity of electrode surface plumbic oxide size distribution, increase electrode specific surface area, it is active to improve electrode catalyst.Through controlled step 7) temperature can so that to mainly be the strong β-PbO of catalytic activity 2, improve the electrode catalyst performance
The present invention compared with prior art has the following advantages: the chromophoric group that (1) can be destroyed azo dyes fast, can decolour fast and effectively.(2) life-span of the electrode that uses longer, whole removal device is simple, easy to operate, has advantages such as the life-span is long, easy and simple to handle.(3) not additional other chemical substances of introducing have been avoided secondary pollution when reducing cost.(4) only need simple passing through control current density and conduction time, can realize effective decolouring azo dyes.
Description of drawings:
Fig. 1 is electrode materials of the present invention decolorizing effect to 50 mg/L Kn-B when the different electric flow density,
Fig. 2 is that electrode materials is at current density 150 mA/cm 2The time to the decolorizing effect of different starting point concentration Kn-B.
Embodiment:
Below in conjunction with embodiment the present invention is described further.
1, the preparation method of electrode materials
Embodiment 1:
1) successively the titanium plate is polished with thickness sand paper respectively, make titanium plate surface demonstrate the light grey gloss of homogeneous.
2) the titanium plate after will polishing immerses 40 wt% NaOH solution, and the pollutents such as grease on titanium plate surface are removed in 80 ℃ of following alkali cleanings 2 hours.
3) the titanium plate after the alkali cleaning immerses in the oxalic acid solution of 15 wt% in 90 ℃ of following pickling 2 hours, removes titanium plate surface TiO 2
4) make anode with the titanium plate after the pickling, the Pt electrode is a negative electrode, and electrolytic solution is by 0.8 wt%NaF, 1.6 wt%Na 2SO 4, 10 wt% polyoxyethylene glycol and 87.6 wt% ultrapure waters form, the constant voltage etching is 1 hour under 25 V conditions, then in retort furnace in 500 ℃ of calcinings 3 hours down.
5) be anode with the Pt electrode, the titanium plate after the calcining is made negative electrode, 1 mol/L (NH 4) 2SO 4Be electrolytic solution, the constant voltage energising is 20 seconds under 1.5 V conditions.
6) titanium plate that will be after step 5) is handled is at 1 mol/L CuSO 4Under 45 ℃ of conditions, adopt pulse current method in the solution: cathode pulse (70 mA, 10 ms), anodic pulse (70 mA, 1 ms), lax (0 mA, 1 s) handled 5 minutes.
7) with above-mentioned steps 6) titanium plate after handling is as anode, and copper coin is a negative electrode, with 0.05 mol/L HNO 3, 0.5 mol/L Pb (NO 3) 2, 0.04 mol/L NaF and 0.45 wt% PDDA mixing solutions be as electrolytic solution, at constant current 25 mA/cm 2, 80 ℃, handled 40 minutes.
Above-mentioned anode and cathode interelectrode distance is 10 millimeters.
 
Embodiment 2:
1) successively the titanium plate is polished with thickness sand paper respectively, make titanium plate surface demonstrate the light grey gloss of homogeneous.
2) the titanium plate after will polishing immerses 60 wt% NaOH solution, and the pollutents such as grease on titanium plate surface are removed in 60 ℃ of following alkali cleanings 4 hours.
3) the titanium plate after the alkali cleaning immerses in the oxalic acid solution of 10 wt% in 60 ℃ of following pickling 2 hours, removes titanium plate surface TiO 2
4) make anode with the titanium plate after the pickling, the Pt electrode is a negative electrode, and electrolytic solution is by 0.5wt%NaF, 1wt%Na 2SO 4, 5wt% polyoxyethylene glycol and 93.5 wt% ultrapure waters form, the constant voltage etching is 3 hours under the 15V condition, then in retort furnace in 550 ℃ of calcinings 1.5 hours down.
5) be anode with the Pt electrode, the titanium plate after the calcining is made negative electrode, 0.5 mol/L (NH 4) 2SO 4Be electrolytic solution, the constant voltage energising is 20 seconds under 1.5 V conditions.
6) titanium plate that will be after step 5) is handled is at 2 mol/L CuSO 4Under 35 ℃ of conditions, adopt pulse current method in the solution: cathode pulse (50 mA, 5 ms), anodic pulse (60 mA, 0.5 ms), lax (0 mA, 0.5 s) handled 15 minutes.
7) with above-mentioned steps 6) titanium plate after handling is as anode, and copper coin is a negative electrode, with 0. 05 mol/L HNO 3, 0.1mol/L Pb (NO 3) 2, 0.01mol/L NaF and 0.1wt% PDDA mixing solutions be as electrolytic solution, at constant current 5 mA/cm 2, 50 ℃, handled 90 minutes.
Above-mentioned anode and cathode interelectrode distance is 10 millimeters.
 
Embodiment 3:
1) successively the titanium plate is polished with thickness sand paper respectively, make titanium plate surface demonstrate the light grey gloss of homogeneous.
2) the titanium plate after will polishing immerses 50 wt% NaOH solution, and the pollutents such as grease on titanium plate surface are removed in 70 ℃ of following alkali cleanings 3 hours.
3) the titanium plate after the alkali cleaning immerses in the oxalic acid solution of 20 wt% in 95 ℃ of following pickling 4 hours, removes titanium plate surface TiO 2
4) make anode with the titanium plate after the pickling, the Pt electrode is a negative electrode, and electrolytic solution is by 2 wt%NaF, 5 wt%Na 2SO 4, 20 wt% polyoxyethylene glycol and 73 wt% ultrapure waters form, the constant voltage etching is 2 hours under 25 V conditions, then in retort furnace in 550 ℃ of calcinings 3 hours down.
5) be anode with the Pt electrode, the titanium plate after the calcining is made negative electrode, 1.5 mol/L (NH 4) 2SO 4Be electrolytic solution, the constant voltage energising is 10 minutes under the 2V condition.
6) titanium plate that will be after step 5) is handled is at 2 mol/L CuSO 4Under 45 ℃ of conditions, adopt pulse current method in the solution: cathode pulse (80 mA, 15 ms), anodic pulse (80 mA, 2 ms), lax (0 mA, 5 s) handled 30 minutes.
7) with above-mentioned steps 6) titanium plate after handling is as anode, and copper coin is a negative electrode, with 0.5 mol/L HNO 3, 1.5 mol/L Pb (NO 3) 2, 0.1 mol/L NaF and 1 wt% PDDA mixing solutions be as electrolytic solution, at constant current 40mA/cm 2, 90 ℃, handled 90 minutes.
Above-mentioned anode and cathode interelectrode distance is 10 millimeters.
2, the present invention is an instance with azo dyes HFGR REACTIVE Black HFGR Kn-B also, and the decolorizing effect of this electrode materials to Kn-B waste water is provided.
Embodiment 1:
A) with prepared electrode materials as anode, the Pt electrode is a negative electrode, and 100 mL are contained 50 mg/L HFGR REACTIVE Black HFGRs, 0.25 mol/L Na 2SO 4Simulated wastewater as electrolytic solution, constant current 150 mA/cm under the room temperature 2
B) according to step a), 10 min that switch on respectively, 20 min, 30 min, 40 min, 50 min, 1 h, 1.5 h, 2 h, 3 h.
C) sample of above-mentioned different conduction times is done the colourity analysis respectively, what wherein colorimetric analysis was adopted is spectrophotometry.
D) calculate decolorizing effect, wherein percent of decolourization/%=100% (A 0-A e)/A 0
Embodiment 2:
A) with prepared electrode materials as anode, the Pt electrode is a negative electrode, and 100 mL are contained 100 mg/L HFGR REACTIVE Black HFGRs, 0.25 mol/L Na 2SO 4Simulated wastewater as electrolytic solution, constant current 150 mA/cm under the room temperature 2
B) according to step a), 10 min that switch on respectively, 20 min, 30 min, 40 min, 50 min, 1 h, 1.5 h, 2 h, 3 h.
C) sample of above-mentioned different conduction times is done the colourity analysis respectively, what wherein colorimetric analysis was adopted is spectrophotometry.
D) calculate decolorizing effect, wherein percent of decolourization/%=100% (A 0-A e)/A 0
Fig. 1 is electrode materials of the present invention decolorizing effect to 50 mg/L Kn-B when the different electric flow density, and Fig. 2 is that electrode materials is at current density 150 mA/cm 2The time to the decolorizing effect of different starting point concentration Kn-B.By scheming visible current density at 50 ~ 200 mA/cm 2Between the time, all can realize that current density is big more to the quick decolouring of 50 mg/L Kn-B, decolorization rate is fast more; Along with the increase of current density, it is more and more littler for the promoter action of decolorizing effect to increase current density.When current density is 150 mA/cm 2The time, this electrode materials all can be realized decolouring fast to the Kn-B of starting point concentration 50 ~ 150 mg/L, and starting point concentration is big more, and required bleaching time is long more.In sum, this electrode materials can realized decolouring fast and effectively to the Kn-B dyestuff in the finite concentration scope in the current density range more widely.
More than be thinking of the present invention and implementation method, should be pointed out that for those skilled in the art, under the prerequisite that does not break away from the principle of the invention, can also make some improvement, these improvement also should be regarded as protection scope of the present invention.

Claims (10)

1. lead dioxide electrode is characterized in that being prepared from following steps:
1) the titanium plate is polished, make titanium plate surface demonstrate the light grey gloss of homogeneous;
2) the titanium plate after will polishing carries out alkali cleaning, removes the pollutent on titanium plate surface;
3) the titanium plate after the alkali cleaning carries out pickling, removes the TiO on titanium plate surface 2
4) the titanium plate after step 3) is handled is made anode, Pt is a negative electrode, with 0.5 ~ 2 wt%NaF, 1 ~ 5 wt%Na 2SO 4, 5 ~ 20 wt% polyoxyethylene glycol and ultrapure water be configured to electrolytic solution, the constant voltage etching is 1 ~ 3 hour under 15 ~ 25 V conditions, then in retort furnace in 500 ~ 550 ℃ of calcinings 1.5 ~ 3 hours down;
5) with Pt be anode, the titanium plate after step 4) is handled is made negative electrode, 0.5 ~ 1.5 mol/L (NH 4) 2SO 4Be electrolytic solution, the constant voltage energising is 0.1 ~ 10 minute under 1.5 ~ 2 V conditions;
6) titanium plate that will be after step 5) is handled is at 1 ~ 2 mol/L CuSO 4Under 35 ~ 45 ℃ of conditions, adopt pulse current method to handle in the solution 5 ~ 30 minutes;
7) with above-mentioned steps 6) titanium plate after handling is as anode, and copper coin is a negative electrode, and electrolytic solution is by 0.05 ~ 0.5 mol/L HNO 3, 0.5 ~ 1.5 mol/L Pb (NO 3) 2, 0.01 ~ 0.1 mol/L NaF and 0.1 ~ 1 wt% PDDA mix, at constant current 5 ~ 40 mA/cm 2, 50 ~ 90 ℃, handle after 30 ~ 90 minutes, use the deionized water thorough washing totally promptly to get the modification lead dioxide electrode.
2. lead dioxide electrode according to claim 1 is characterized in that step 2) process of alkali cleaning is that the titanium plate after the polishing is immersed 40 ~ 60 wt% NaOH solution, the pollutent on titanium plate surface is removed in 60 ~ 80 ℃ of following alkali cleanings 2 ~ 4 hours.
3. lead dioxide electrode according to claim 1 and 2, the process that it is characterized in that the step 3) pickling are that the titanium plate after the alkali cleaning immerses in 10 ~ 20 wt% oxalic acid solutions in 60 ~ 95 ℃ of following pickling 2 ~ 4 hours.
4. lead dioxide electrode according to claim 1 and 2; The process that it is characterized in that the step 6) pulse current method is: handle 5 ~ 15 ms with the cathode pulse of-50 ~-80 mA earlier; Handle 0.5 ~ 2 ms with the anodic pulse of 60 ~ 80 mA again, then lax 0.5 ~ 5 s repeats above-mentioned steps then.
5. the preparation method of a lead dioxide electrode is characterized in that may further comprise the steps:
1) the titanium plate is polished, make titanium plate surface demonstrate the light grey gloss of homogeneous;
2) the titanium plate after will polishing carries out alkali cleaning, removes the pollutent on titanium plate surface;
3) the titanium plate after the alkali cleaning carries out pickling, removes the TiO on titanium plate surface 2
4) the titanium plate after step 3) is handled is made anode, Pt is a negative electrode, with 0.5 ~ 2wt%NaF, 1 ~ 5 wt%Na 2SO 4, 5 ~ 20 wt% polyoxyethylene glycol and ultrapure water be configured to electrolytic solution, the constant voltage etching is 1 ~ 3 hour under 15 ~ 25 V conditions, then in retort furnace in 500 ~ 550 ℃ of calcinings 1.5 ~ 3 hours down;
5) with Pt be anode, the titanium plate after step 4) is handled is made negative electrode, 0.5 ~ 1.5 mol/L (NH 4) 2SO 4Be electrolytic solution, the constant voltage energising is 0.1 ~ 10 minute under 1.5 ~ 2 V conditions;
6) titanium plate that will be after step 5) is handled is at 1 ~ 2 mol/L CuSO 4Under 35 ~ 45 ℃ of conditions, adopt pulse current method to handle in the solution 5 ~ 15 minutes;
7) with above-mentioned steps 6) titanium plate after handling is as anode, and copper coin is a negative electrode, and electrolytic solution is by 0.05 ~ 0.5 mol/L HNO 3, 0.1 ~ 1.5 mol/L Pb (NO 3) 2, 0.01 ~ 0.1 mol/L NaF and 0.1 ~ 1 wt% PDDA mix, at constant current 5 ~ 40 mA/cm 2, 50 ~ 90 ℃, handle after 30 ~ 90 minutes, use the deionized water thorough washing totally promptly to get the modification lead dioxide electrode.
6. the preparation method of lead dioxide electrode according to claim 5 is characterized in that step 2) process of alkali cleaning is that the titanium plate after the polishing is immersed 40 ~ 60 wt% NaOH solution, the pollutent on titanium plate surface is removed in 60 ~ 80 ℃ of following alkali cleanings 2 ~ 4 hours.
7. according to the preparation method of claim 5 or 6 described lead dioxide electrodes, the process that it is characterized in that the step 3) pickling is that the titanium plate after the alkali cleaning immerses in 10 ~ 20 wt% oxalic acid solutions in 60 ~ 95 ℃ of following pickling 2 ~ 4 hours.
8. according to the preparation method of claim 5 or 6 described lead dioxide electrodes; The process that it is characterized in that the step 6) pulse current method is: handle 5 ~ 15 ms with the cathode pulse of-50 ~-80 mA earlier; Handle 0.5 ~ 2 ms with the anodic pulse of 60 ~ 80 mA again; Then lax 0.5 ~ 5 s repeats above-mentioned steps then.
9. the application of the described lead dioxide electrode of claim 1 in azo dyes decolours fast.
10. a lead dioxide electrode makes the azoic dyestuff method of decolouring fast in electrochemical catalytic oxidation, and it is characterized in that step is: the modification plumbic oxide with preparation is an anode, constant current 50 ~ 500 mA/cm 2Under the condition, place phenolic wastewater, the quick decolouring of switching on and realizing azoic dyestuff in 0.5 ~ 5 hour.
CN2012100065149A 2012-01-11 2012-01-11 Lead dioxide electrode, production method thereof, application of lead dioxide electrode to quickly decoloring azo dyes and method for quickly decoloring azo dyes by using lead dioxide electrode Pending CN102531108A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2012100065149A CN102531108A (en) 2012-01-11 2012-01-11 Lead dioxide electrode, production method thereof, application of lead dioxide electrode to quickly decoloring azo dyes and method for quickly decoloring azo dyes by using lead dioxide electrode

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2012100065149A CN102531108A (en) 2012-01-11 2012-01-11 Lead dioxide electrode, production method thereof, application of lead dioxide electrode to quickly decoloring azo dyes and method for quickly decoloring azo dyes by using lead dioxide electrode

Publications (1)

Publication Number Publication Date
CN102531108A true CN102531108A (en) 2012-07-04

Family

ID=46339329

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2012100065149A Pending CN102531108A (en) 2012-01-11 2012-01-11 Lead dioxide electrode, production method thereof, application of lead dioxide electrode to quickly decoloring azo dyes and method for quickly decoloring azo dyes by using lead dioxide electrode

Country Status (1)

Country Link
CN (1) CN102531108A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106315772A (en) * 2016-08-17 2017-01-11 浙江工业大学 N-doped lead dioxide electrode and preparation method and application thereof
CN113755872A (en) * 2021-08-27 2021-12-07 西安交通大学 Preparation method of high-stability titanium-based lead dioxide electrode

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS56123388A (en) * 1980-02-29 1981-09-28 Asahi Chem Ind Co Ltd Lead dioxide electrode
US4415411A (en) * 1980-03-04 1983-11-15 The Japan Carlit Co., Ltd. Anode coated with β-lead dioxide and method of producing same
CN101054684A (en) * 2007-02-07 2007-10-17 浙江工业大学 Method of preparing fluorine-containing lead dioxide electrode on titanium basal body
CN101250715A (en) * 2008-03-31 2008-08-27 太原理工大学 Method for manufacturing acid resistant anode
CN101555051A (en) * 2009-05-05 2009-10-14 苏州科技学院 Production method for powder porous lead dioxide electrode used for treating organics in water
CN102190351A (en) * 2010-03-10 2011-09-21 同济大学 Electrode Ce doped PbO2 used for treating waste water and its preparation method
CN102515315A (en) * 2011-12-30 2012-06-27 南京大学 Anode electrode material, preparation method thereof, application and working method of anode electrode material in treating wastewater containing phenol by electrochemical oxidation

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS56123388A (en) * 1980-02-29 1981-09-28 Asahi Chem Ind Co Ltd Lead dioxide electrode
US4415411A (en) * 1980-03-04 1983-11-15 The Japan Carlit Co., Ltd. Anode coated with β-lead dioxide and method of producing same
CN101054684A (en) * 2007-02-07 2007-10-17 浙江工业大学 Method of preparing fluorine-containing lead dioxide electrode on titanium basal body
CN101250715A (en) * 2008-03-31 2008-08-27 太原理工大学 Method for manufacturing acid resistant anode
CN101555051A (en) * 2009-05-05 2009-10-14 苏州科技学院 Production method for powder porous lead dioxide electrode used for treating organics in water
CN102190351A (en) * 2010-03-10 2011-09-21 同济大学 Electrode Ce doped PbO2 used for treating waste water and its preparation method
CN102515315A (en) * 2011-12-30 2012-06-27 南京大学 Anode electrode material, preparation method thereof, application and working method of anode electrode material in treating wastewater containing phenol by electrochemical oxidation

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
《电镀与精饰》 20110531 姚颖悟等 "钛基二氧化铅电极的应用与改性研究进展" 10 第33卷, 第5期 *
姚颖悟等: ""钛基二氧化铅电极的应用与改性研究进展"", 《电镀与精饰》 *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106315772A (en) * 2016-08-17 2017-01-11 浙江工业大学 N-doped lead dioxide electrode and preparation method and application thereof
CN106315772B (en) * 2016-08-17 2019-06-14 浙江工业大学 A kind of N doping lead dioxide electrode and its preparation method and application
CN113755872A (en) * 2021-08-27 2021-12-07 西安交通大学 Preparation method of high-stability titanium-based lead dioxide electrode

Similar Documents

Publication Publication Date Title
Li et al. Fabrication of cerium-doped lead dioxide anode with improved electrocatalytic activity and its application for removal of Rhodamine B
CN101555082B (en) Waste water treatment method and device combining electrochemical degradation and photocatalytic oxidation technologies
Abdel-Aziz et al. Removal of dyes from waste solutions by anodic oxidation on an array of horizontal graphite rods anodes
US11027992B2 (en) Iron-based amorphous electrode material for wastewater treatment and use thereof
CN101508477B (en) Electrochemical oxidation processing method for wastewater containing anthraquinone dye
CN104944511B (en) The method and apparatus that a kind of photoelectrocatalysis removes heavy metal ions in wastewater
Tung et al. Treatment of real printing wastewater with an electrocatalytic process
Liang et al. Improved decolorization of dye wastewater in an electrochemical system powered by microbial fuel cells and intensified by micro-electrolysis
Soni et al. Decolourization and mineralization of Reactive black-5 with transition metal oxide coated electrodes by electrochemical oxidation
Huang et al. Mechanism and excellent performance of graphite felt as anodes in electrochemical system for Microcystis aeruginosa and microcystin-LR removal with no pH limitation nor chemical addition
CN102897875A (en) Cerium-doped lead dioxide electrode, and preparation method and application thereof in quick decolorization and efficient mineralization of basic dyes
CN103121737B (en) Method for electrochemically treating printing and dyeing wastewater
CN102381791A (en) Equipment for treating organic wastewater through joint of electrolyzation and oxidant
CN108585129B (en) Three-dimensional electrode wastewater treatment method and equipment with recovery function
CN110357226A (en) A kind of method of Electrocatalytic Oxidation processing Polyester wastewater
CN102531108A (en) Lead dioxide electrode, production method thereof, application of lead dioxide electrode to quickly decoloring azo dyes and method for quickly decoloring azo dyes by using lead dioxide electrode
CN109110882A (en) A kind of method of electrochemistry removal paraxylene
CN102515315A (en) Anode electrode material, preparation method thereof, application and working method of anode electrode material in treating wastewater containing phenol by electrochemical oxidation
CN202440349U (en) Equipment for treating organic wastewater by electrolysis-oxidant combination
CN102229442B (en) Method for treating printing and dyeing wastewater with rare earth cerium doped titanium-based manganese dioxide electrode
CN1884631A (en) Method and device for cleaning organic matter using electrochemical method
CN106315936B (en) Method for treating bromamine acid wastewater
CN107434280A (en) A kind of Electrochemical Decolorization method of direct dyes waste water
Bai et al. Autotrophic degradation of sulfamethoxazole using sulfate-reducing biocathode in microbial photo-electrolysis system
CN102815768A (en) Electrolytic method of self-cleaning stainless steel electrode and device thereof

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C02 Deemed withdrawal of patent application after publication (patent law 2001)
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20120704