DOI:
10.1039/C6RA17230J
(Paper)
RSC Adv., 2016,
6, 82024-82032
Preparation and characterization of PbO2 electrodes modified with polyvinyl alcohol (PVA)
Received
5th July 2016
, Accepted 24th August 2016
First published on 25th August 2016
Abstract
Novel PbO2 electrodes were successfully synthesized with polyvinyl alcohol (PVA) modification through electro-deposition technology. The morphology and crystalline structure of the electrodes were characterized by SEM and XRD, respectively. In addition, X-ray photoelectron spectroscopy (XPS), cyclic voltammetry (CV), electrochemical impedance spectroscopy (EIS) and accelerated life stability testing were also carried out to analyze the chemical state, electrochemical performances and stability of the electrodes. The results showed that PVA could refine the grain size and increase the oxygen evolution potential (OEP). After PVA modification, the predominant phase of the PbO2 electrodes was unchanged and all were pure β-PbO2. Besides, for modified electrodes, the electrode film impedance reduced and the proportion of adsorbed hydroxyl oxygen (Oad) on the electrode increased, implying the fast charge transfer and excellent degradation efficiency for organics. In the process of dye oxidation, the PbO2-2.0 vt% electrode showed the highest electrocatalytic activity for ARG degradation due to its highest OEP and massive Oad. Moreover, the accelerated service life tests revealed that the PbO2-2.0 vt% electrode exhibited the highest stability and the accelerated service life was 329.5 h, which was more than 3 times longer than that of the PbO2-0 vt% electrode (96 h).
1. Introduction
Electro-catalytic oxidation technology (EOT) is becoming an attractive approach for wastewater treatment on account of its high efficiency, easy control, versatility, and environmental friendliness.1,2 In the process of electro-catalytic oxidation, the electrode is the core which strongly affects the efficiency of organic pollutant oxidation.3,4 Therefore, it is very important to develop a novel electrode material with high catalytic activity and stability. So far, many kinds of electrodes have been studied, including graphite, Pt, boron doped diamond (BDD), RuO2, IrO2, SnO2 and PbO2, etc.5–11 Among these electrodes, Ti/PbO2 was considered to be a more promising and attractive electrode in wastewater treatment processes due to its low cost, ease of preparation, high OEP and long service lifetime.12–14 However, the fragile PbO2 coating is easily to peel off and dissolved in the process of electrolysis, which could lead to the reduction of the electrocatalytic activity and stability of electrode as well as cause the secondary water pollution.15–17 Hence, it is necessary to modify the PbO2 electrode to meet the standards of industrial electrodes.
Doping is a frequently-used and effective way to modify PbO2 electrode for improving its performance. Lots of foreign materials have been adopted, such as metallic element (Bi,18 Co,19 Fe,20 Ce,21 Cu22), non-metallic element (F19,23,24), redox ion ([Fe(CN)6]3− (ref. 13)) and compounds (TiO2,25 clay,26 carbon nanotubes,27 fluorine resin (FR),15 Polypyrrole (PPy)28 and polytetrafluoroethylene (PTFE)29), etc. The results show that the modified PbO2 electrode exhibits excellent electrocatalytic ability and stable performance. Alcohols can also be used as modifiers for electrodes. Alcohols addition can affect the rate of metal ions migration and crystallization. Recently, to the best of my knowledge, there are two reports about the alcohols modified PbO2 electrode. Xu et al.30 studied the effect of ethylene glycol (EG) modification on the electrochemical properties of PbO2 electrode. Yang et al.31 reported that the PbO2 electrode was modified with polyethylene glycol (PEG). Based on the two reports, it could be concluded that after the modification by alcohols, the electrodes both have excellent electro-catalytic activity and stability.
Polyvinyl alcohol (PVA) is an important chemical raw material and has been widely used for many applications including textile, paper, adhesives, adhesives, and so on.32 In addition, PVA is also a kind of nonionic surfactant and used in the production of emulsifier and dispersant. Adding proper amount of surfactant into the electroplating solution can effectively improve the morphology of the coating and the performance of the electrode.33 Meanwhile, PVA is nontoxic to organisms and is the only known xenobiotic carbon chain polymer to biodegrade at high molecular masses.34 Therefore, using PVP to modify the PbO2 electrode would be very interesting and promising. But at present, to the best of our knowledge, studies of polyvinyl alcohol (PVA)-doped PbO2 electrode have not been previously reported.
Therefore, in the present work, polyvinyl alcohol (PVA) was adopted to modify the PbO2 electrode by electrochemical deposition. The morphology, crystalline structure and electrochemical performances were characterized. Acid red G (ARG, C18H13N3Na2O8S2, CAS number: 3734-67-6) was chosen as the model pollutant for electro-catalytic oxidation to evaluate electrochemical activity of the electrodes. Besides, Pb element leaching of PbO2 electrodes was studied during electrolysis process to evaluate the safety. Furthermore, the accelerated life test was also carried out to assess its stability.
2. Experimental
2.1. Materials and reagents
All chemicals (analytical grade) were obtained from Sinopharm Chemical Reagent Xi'an Co., Ltd and used without further purification. Pure (>99.6%) titanium plates with 0.5 mm thickness were purchased from BaoTi Co., Ltd. and used as the substrate. Deionized water with conductance of 18 MΩ cm was prepared by an EPED-40TF water purification laboratory system (Yipuyida Technology development Ltd., Nanjing, China).
2.2. Electrode preparation
Ti plates (3 cm × 5 cm × 0.5 mm) were used as the electrode substrate. The pre-treatment of Ti plates and the fabrication of the Sb–SnO2 inner layer (brush coating-thermal deposition method) were carried out according to our previous work.13,22 The surface β-PbO2 layer was deposited on the Ti/Sb–SnO2 surface through the electrochemical deposition method. The electro-deposition solution contained 0.5 mol L−1 Pb(NO3)2, 0.1 mol L−1 Cu(NO3)2, 0.01 mol L−1 NaF, 0.1 mol L−1 HNO3 and the solution dissolved different volume fractions of PVA (0 vt%, 1.0 vt%, 2.0 vt% and 5.0 vt%, marked as PbO2-0 vt%, PbO2-1.0 vt%, PbO2-2.0 vt% and PbO2-5.0 vt%, respectively). The pretreated Ti/Sb–SnO2 was used as anode in electro-deposition solution (65 °C) for 120 min under the current density of 10 mA cm−1. The copper sheet with the same size was adopted as the counter cathode. The average amount of PbO2 coating on the electrode surface is 91.6 ± 0.3 mg cm−2 exclusive of PbO2-5.0 vt% (PbO2-5.0 vt%: 83.5 mg cm−2).
PVA (Type 1799) was dissolved as follows: firstly, adding 2 g PVA slowly to a beaker filled with 100 mL deionized water (25 °C). The beaker would be sealed which could reduce the water evaporation. Secondly, the solution was fully swollen at room temperature (25 °C) for 12 h and performed at a heating rate of 5 °C min−1 from 25 °C to 90 °C. Thirdly, the solution was kept at 90 °C for 3 h, until the tiny particles in the solution disappeared. Finally, the solution was filtered through 80 mesh of stainless steel to remove impurities and prepared for PbO2 electrodes modification.
2.3. Characterization analysis
The morphology and crystal structure of PbO2 electrodes are analyzed by scanning electron microscopy (SEM, JEOL, JSM-6390A) and X'pert PRO MRD diffractometer (XRD, PAN alytical, Holland) using Cu Kα source (λ = 0.15416 nm). The chemical states of O on the electrodes were analyzed by the X-ray photoelectron spectroscopy (XPS) performed on Axis Ultra spectrometer (Al Kα radiation; 1486.6 eV). Binding energy of the C 1s peak (284.8 eV) was used as the reference for calibration.
Electrochemical properties were tested on the CHI660D electrochemical workstation (Shanghai Chenhua Instrument Co. Ltd., China) in a standard three-electrode cell (25 °C). The fresh PbO2 electrodes were served as the working electrode. Copper sheets were acted as the counter electrode and Ag/AgCl (sat KCl) was acted as the reference electrode. The electrolyte was 0.5 mol L−1 Na2SO4 solution. Cyclic voltammetry (CV) measurements were performed between 0 and 2.5 V with a sweep rate of 50 mV s−1. Electrochemical impedance spectroscopy (EIS) measurements were carried out in a range of 105 Hz to 0.1 Hz at a potential of 0 V (vs. Ag/AgCl) with a sine wave of 5 mV amplitude.
The accelerated lifetime test was carried out at an anode current density of 500 mA cm−2 using an electrochemical workstation (LK3000A, Tianjin Lanlike, China). The electrolyte was 3 mol L−1 H2SO4 (35 °C ± 2 °C). The working electrode was considered as deactivation when the cell voltage reached to 10 V.
2.4. Electro-catalytic oxidation of ARG
Electro-catalytic oxidation of ARG was conducted in an undivided electrolytic cell under constant current density of 15 mA cm−2 equipped with a magnetic stirrer. The volume of dye solution was 200 mL and the initial ARG concentration was 100 mg L−1. 0.1 mol L−1 Na2SO4 was used as the supporting electrolyte. The PbO2 anodes have an area of 18 cm2 and copper sheet with the same area was used as the cathode. The gap between the electrodes was 1 cm. Electrolysis were carried out at room temperature for 120 min and the liquid samples were withdrawn from the electrolytic cell every 15 min. The dye concentrations were measured by UV-vis absorption (Agilent 8453, Agilent) at the characteristic wavelengths of 505 nm and COD values (mg L−1) of the samples were determined by CSB/COD Reactor (ET 125 SC). The decolorization rate (ηARG) and COD removal rate (ηCOD) in electrochemical oxidation could be calculated as follows:| |
 | (1) |
where A0 and At are the absorbance value in 505 nm of initial sample and electrolysis at the given times t, respectively.| |
 | (2) |
where COD0 and CODt are the initial COD concentration and COD concentration value at given time t, respectively.
The instantaneous current efficiency (ICE) and energy consumption (Ep) were calculated as follows:
| |
 | (3) |
| |
 | (4) |
where COD
t1 and COD
t2 are the chemical oxygen demand at times
t1 and
t2, respectively,
I is the current (A),
F is the Faraday constant (96
![[thin space (1/6-em)]](https://www.rsc.org/images/entities/char_2009.gif)
487 C mol
−1),
U is the cell voltage (V) and
V is the volume of the electrolyte (L).
In order to evaluate the safety performance of the PbO2 electrode in the electrolysis process. The fresh prepared electrode was electrolyzed at 15 mA cm−2 for 120 min in 0.1 mol L−1 Na2SO4 solution. The concentration of Pb element dissolved in electrolyte (no coating detachment was found) was analyzed by inductively coupled plasma atomic emission spectroscopy (ICP-AES, Shimadzu, Japan).
3. Results and discussion
3.1. Surface morphological analysis of PbO2 electrodes
Fig. 1 shows the SEM images of the PbO2 electrodes modified with different PVA volume fractions. From Fig. 1a, it could be observed that the PbO2-0 vt% electrode showed typical pyramid structure (octahedral crystals) with different sizes on the surface. The electrode surface was relatively rough, and there were a number of micro holes distributed on the surface of the coating. The PbO2 grains were randomly arranged and there were not obvious crystal orientation. This structure could easily lead to the infiltration of the electrolyte into the coating, reducing the stability of the electrode.35 In addition, the O2 generated by electrolysis of water would be released from the micro holes and furtherly damaged the coating. As shown in Fig. 1b and d, it could be seen that after PVA adding into the deposition solution, the modified PbO2 electrode still had the pyramid structure, but it was ordered and uniform compared with unmodified electrode. With the increase of the PVA doping amount, the particles of the electrode surface became smaller and smoother. The reasons could be explained as follows: firstly, the surface tension of the plating solution could be reduced by the addition of surfactants (PVA), making the coating smooth and compact. Secondly, PbO2 crystal nucleus would be coated by PVA molecule and inhibited the growth and aggregation of PbO2 grains. Therefore, the particle size of PbO2 crystals decreased. Thirdly, the addition of PVA increased the viscosity of electroplating solution, reducing the migration rate of Pb ions and making the current density distribute on the electrode uniformly. Therefore, the electrode coating became compacted and smooth. The special structure could suppress the infiltration of the electrolyte into the coating layer and prolong the service life of the electrode.
 |
| | Fig. 1 SEM images of the different PbO2 electrodes ((a) PbO2-0 vt%, (b) PbO2-1.0 vt%, (c) PbO2-2.0 vt%, (d) PbO2-5.0 vt%). | |
3.2. Structure of PbO2 electrodes
The XRD patterns of the PbO2 electrodes are shown in Fig. 2. For PbO2-0 vt% electrode, the crystal structure is pure β-PbO2 and the main diffraction peaks at 25.4°, 32.0°, 36.2° and 49.0° were assigned to the (110), (101), (200) and (211) crystal faces, respectively. After PVA addition, the crystalline orientation of the electrodes did not change greatly and the predominant phases were still β-PbO2. However, the diffraction intensities of (101) and (211) planes for PbO2-1.0 vt% and PbO2-2.0 vt% increased significantly, indicating that the preferred orientation along the (101) and (211) directions. In addition, the diffraction intensities of (110) and (200) planes decreased. Moreover, when the PVA volume fraction increased to 2.0 vt%, the peak of (220) plane disappeared. This phenomenon could be account for the different adsorption and encapsulation of PVA on the different crystal surfaces. The planes of (110), (200) and (220) were suppressed and the planes of (101) and (211) were preferential growth. However, when the PVA volume fraction increased to 5.0 vt%, the intensities of diffraction peaks were all weak compared with other electrodes. After calculated by Debye–Scherrer formula, it could be seen that the average grain sizes of PbO2 crystals decreased with the addition of PVA (Table 1). The average grain sizes of PbO2 crystals were 21.20 nm, 20.91 nm, 19.37 nm and 19.13 nm, respectively, which was consistent with SEM results.
 |
| | Fig. 2 XRD patterns of the different PbO2 electrodes. | |
Table 1 The different parameters of selected PbO2 electrodesa
| |
PbO2-0 vt% |
PbO2-1.0 vt% |
PbO2-2.0 vt% |
PbO2-5.0 vt% |
| OEP represents oxygen evolution potential. |
| Average loading capacity/mg cm−2 |
91.9 |
91.6 |
91.3 |
83.5 |
| Grain size/nm |
21.2 |
20.9 |
19.3 |
19.1 |
| OEP/V |
1.845 |
1.849 |
1.862 |
1.837 |
| Accelerated lifetime/h |
96 |
256.5 |
329.5 |
92.5 |
3.3. Cyclic voltammetry (CV) test
Fig. 3 shows the typical cyclic voltammograms of different PbO2 electrodes in 0.5 mol L−1 Na2SO4 solution at the scan rate of 50 mV s−1. As shown in Table 1, it could be seen that the oxygen evolution potential (OEP) of the unmodified PbO2 electrode was 1.845 V. After the modification of PVA, the OEP increased for PbO2-1.0 vt% (1.849 V) and PbO2-2.0 vt% (1.862 V), respectively. However, when the volume fraction of PVA reached to 5.0 vt%, the OEP decreased to 1.837 V. It was well accepted that electrodes with a high OEP were praised, because the oxygen evolution reaction and energy loss could be suppressed.10,36,37 Therefore, this result implied that the PbO2-2.0 vt% with the highest OEP could exhibit a better performances for organics removal than that of others.
 |
| | Fig. 3 Cyclic voltammograms curves of PbO2 electrodes in 0.5 mol L−1 Na2SO4 solution, scan rate: 50 mV s−1. | |
In addition, the current response (at the section of oxygen evolution) of PbO2-2.0 vt% was the most obvious. Xu et al.38 considered that the high current response in the section of oxygen evolution could promote the water splitting and accelerate the generation rate of HO˙ free radical, which was also advantageous to the degradation of organic matter for PbO2-2.0 vt%.
3.4. Electrochemical impedance spectroscopy (EIS)
Fig. 4 shows the EIS Nyquist plots of freshly prepared PbO2 electrodes in 0.5 mol L−1 Na2SO4 solutions and the simulated data is shown in Table 2. The Nyquist plots for all electrodes fit the equivalent circuit Rs(RfQ) very well. And Rs, Rf and Q represent the solution resistance, electrode film resistance and the constant phase element (CPE), respectively. From this figure, it could be seen that arc diameter of electrodes decreased with the increase of the volume fraction of PVA, revealing that the PVA addition could reduce the electrode film resistance and accelerate the electron transfer. As shown in Table 2, the PbO2-2.0 vt% showed the smallest Rf (42.47 Ω cm−2), which was lower than that of PbO2-0 vt% (102.1 Ω cm−2). In addition, the PbO2-2.0 vt% also showed the largest CPE value (0.000523 Ω−1 sn cm−2) compared with other electrodes, reflecting a high specific area and more active sites on the electrode.39
 |
| | Fig. 4 The fitted curves of PbO2 electrodes in EIS and equivalent circuit model (the inset). | |
Table 2 Simulated data of each parameter (EIS)
| |
Rs/Ω cm−2 |
Rf/Ω cm−2 |
Q/Ω−1 sn cm−2 |
n |
| PbO2-0 vt% |
3.272 |
102.1 |
0.000245 |
0.695 |
| PbO2-1.0 vt% |
3.410 |
82.21 |
0.000262 |
0.601 |
| PbO2-2.0 vt% |
2.909 |
42.47 |
0.000523 |
0.684 |
| PbO2-5.0 vt% |
3.821 |
87.39 |
0.000191 |
0.701 |
3.5. Electrochemical oxidation for ARG
Fig. 5 shows the performance of the PbO2 electrodes for ARG degradation. From Fig. 5a, it could be clearly seen that the decolorization rates all reached more than 90% after 120 min electrolysis. The highest decolorization rate was obtained on PbO2-2.0 vt% and decolorization rate could reach 89.3% within 60 min, which was higher than that of PbO2-0 vt% (72.4%). After the kinetic fitting, we found that the removal of ARG was according to the first order kinetics (the inset). The rate constants (k) for PbO2-0 vt%, PbO2-1.0 vt%, PbO2-2.0 vt% and PbO2-5.0 vt% were 2.52 × 10−2 min−1, 3.63 × 10−2 min−1, 4.69 × 10−2 min−1 and 2.87 × 10−2 min−1, respectively. And the corresponding t1/2 values were 33 min, 25 min, 23 min and 29 min, respectively (Table 3). As shown in Fig. 5b, the PbO2-2.0 vt% possessed the highest COD removal rate value of 66.8% within 60 min, which was higher than that of others. Meanwhile, the PbO2-2.0 vt% also showed the highest ICE (34.5%) and lowest Ep (0.041 kW h gCOD−1) than those of the other PbO2 electrodes. The best performance for ARG degradation at PbO2-2.0 vt% could be ascribed to the high oxygen evolution potential, good electric conductivity and high specific area. These properties were helpful to generate more HO˙ free radicals and remove ARG at low energy consumption.40
 |
| | Fig. 5 Performance of the PbO2 electrodes for ARG degradation. (a) ARG decolorization rate; (b) COD removal rate. | |
Table 3 The kinetics for the electrochemical degradation of ARG (electrolysis time: 120 min)
| Electrode |
Rate constantsa (k, 10−2 min−1) |
Half-lives (t1/2, min) |
R2 |
ICEb (%) |
Epc (kW h gCOD−1) |
| Pseudo-first-order rate constant of electrochemical degradation. The values of ICE was obtained at the time of 50% COD removal. The values of Ep was obtained at the time of 50% COD removal. |
| PbO2-0 vt% |
2.52 |
33 |
0.991 |
24.8 |
0.057 |
| PbO2-1.0 vt% |
3.63 |
25 |
0.993 |
32.0 |
0.044 |
| PbO2-2.0 vt% |
4.69 |
23 |
0.990 |
34.5 |
0.041 |
| PbO2-5.0 vt% |
2.87 |
29 |
0.988 |
28.1 |
0.050 |
After ICP-AES detection, we found that the concentration of dissolved Pb element in the electrolyte decreased after the PVA modification (Table 4). This result could be explained as that after PVA modification, the morphology became smooth, compact and the grain sizes became smaller, which could slow down the erosion rate of electrolyte on the PbO2 coating. As shown in Table 4, it could be seen that the concentration of Pb element for PbO2-0 vt%, PbO2-1.0 vt%, PbO2-2.0 vt% and PbO2-5.0 vt% were 0.023 mg L−1, 0.011 mg L−1, 0.006 mg L−1 and 0.016 mg L−1, respectively. It could be observed that the PbO2-2.0 vt% had the least amount of Pb dissolution, implying the best safety performance in application.
Table 4 The concentration of Pb element in the electrolyte (electrolysis time: 120 min)
| Electrode |
PbO2-0 vt% |
PbO2-1.0 vt% |
PbO2-2.0 vt% |
PbO2-5.0 vt% |
| Concentration (mg L−1) |
0.023 |
0.011 |
0.006 |
0.016 |
3.6. X-ray photoelectron spectroscopy (XPS) analysis
In order to further explore the reasons for the good catalytic performance of PbO2-2.0 vt% electrode, the XPS test was carried out for PbO2-0 vt% and PbO2-2.0 vt% (Fig. 6) and XPS data of chemical states of O on the electrode surface is shown in Table 5. Fig. 6a shows the XPS whole spectra for PbO2-0 vt% and PbO2-2.0 vt%. From Fig. 6a, it could be seen that the peaks of Pb, C and O existed in PbO2-0 vt% electrode. As for PbO2-2.0 vt%, the peaks showed no obvious changes, indicating that the structure of PbO2 remained intact after PVA modification. From Fig. 6b and c, there existed two types oxygen on the electrode surface. The peak at around 529 eV was attributed to the lattice oxygen (OL) and the peak at around 531 eV was attributed to adsorbed hydroxyl oxygen (Oad).41 As shown in Table 5, it could be observed that the percentage of the Oad to the total oxygen (OL + Oad) for PbO2-2.0 vt% (76.81%) was higher than that of PbO2-0 vt% (68.95%). Oad was the most active oxygen and could generate more HO˙ free radicals, favoring the organics oxidation.42,43 Therefore, PbO2-2.0 vt% with a higher percentage of the Oad implied a higher performance for ARG removal.
 |
| | Fig. 6 XPS spectra of PbO2 electrode PbO2-0 vt% and PbO2-2.0 vt%. (a) XPS fully scanned spectra; (b) O 1s core level spectrum for PbO2-0 vt%; (c) O 1s core level spectrum for PbO2-2.0 vt%. | |
Table 5 XPS data of chemical states of O on the electrode surfacea
| Electrode |
Binding energy (eV) |
ε% |
η |
| O 1s (OL) |
O 1s (Oad) |
Oad/(Oad + OL)100% |
(Oad/OL) |
| Oad: adsorbed hydroxyl oxygen; OL: lattice oxygen. |
| PbO2-0 vt% |
529.06 |
531.82 |
68.95 |
2.22 |
| PbO2-2 vt% |
529.01 |
531.02 |
76.81 |
3.31 |
3.7. Electrochemical stability test
Stability is an important index to evaluate the quality of electrodes. Therefore, the stabilities of the PbO2 electrodes were investigated through accelerated service life tests (Fig. 7). It was clearly seen that the cell potential of the selected electrodes maintained relatively stable below the cell potential of around 4.0 V. Then the cell potential began to rise sharply in a short period of time, leading to deactivation. For PbO2-1.0 vt% and PbO2-2.0 vt%, the service life were 329.5 h and 256.5 h, respectively, which were higher than that of PbO2-0 vt% (96 h). The enhancement of service life could be account for the smooth and compact morphology which could inhibit the infiltration of electrolyte into the coating and the formation of TiO2 passivation layer. In addition, because of the improvement of oxygen evolution potential (OEP) for PbO2-1.0 vt% and PbO2-2.0 vt%, the diffusion of reactive oxygen species into the Ti substrate was also inhibited. Furthermore, the PVA addition could effectively reduce the internal stress of PbO2 coating and improve the bonding strength between coating and substrate. For these reasons, the electrode stability had been greatly improved.
 |
| | Fig. 7 Accelerated life test of selected PbO2 electrodes (H2SO4: 3 mol L−1; current density: 500 mA cm−2). | |
However, when the PVA volume fraction increased to 5.0 vt%, the service life decreased to 92.5 h, which was lower than that (96 h) of PbO2-0 vt%. This result could be interpreted as that PVA addition could increase the viscosity of the electroplating solution and reduce the mass transfer rate of ions. Thus, when adding excess of PVA into the electroplating solution, the migration rate of Pb2+ ion to Ti/Sb–SnO2 substrate would slow down and the average loading capacity of PbO2 coating would decrease (only 83.5 mg cm−2) within a constant time. Therefore, the lower average loading capacity implied that the coating could be consumed in a relatively short period of time, leading to the deactivation of electrode rapidly.
Fig. 8 shows the SEM images and EDX spectrum of the deactivated PbO2 electrodes from Fig. 8a and d, it could be seen that the PbO2 coating still existed. However, compared with morphology of the fresh PbO2-0 vt% and PbO2-5.0 vt%, the typical rectangular pyramid structure of β-PbO2 disappeared and the coating became very loose. After EDX analysis, it was found that there were still a large number of Pb element in the coating (Fig. 8e and h). This result indicated that the deactivation pattern of the two electrodes may be the substrate passivation. Although most of the PbO2 surface coating still existed, the electrode was inactive. For PbO2-1.0 vt% and PbO2-2.0 vt%, the coating have been largely depleted and Ti substrate has been exposed. In addition, more Ti content was detected on the PbO2-1.0 vt% and PbO2-2.0 vt% after EDX analysis, which indicated that the depletion of the coating lead to the inactivation of PbO2-1.0 vt% and PbO2-2.0 vt%. It was known to all, the coating consumption was a much slower process than direct passivation of substrate.44 Therefore, it could also explain the reason for the longer service life of PbO2-1.0 vt% and PbO2-2.0 vt% compared with PbO2-0 vt% and PbO2-5.0 vt%.
 |
| | Fig. 8 SEM images and EDX spectrum of the deactivated PbO2-0 vt% electrode (a and e), PbO2-1.0 vt% (b and f), PbO2-2.0 vt% (c and g) and PbO2-5.0 vt% (d and h). | |
4. Conclusions
This study reported the preparation of PbO2 electrode modified with polyvinyl alcohol (PVA) through electro-deposition technology. The results of SEM and XRD showed that the grain size of the modified electrode decreased and the morphology became compacted and smooth. The PVA addition could effectively improve the oxygen evolution potential (OEP) and reduce the electrode film resistance (Rf). This result showed that the PbO2-2.0 vt% possessed the highest OEP (1.862 V) and lowest Rf (42.47 Ω cm−2). From the electrochemical oxidation performances for ARG degradation, it could be seen that the PbO2-2.0 vt% electrode showed the highest electrocatalytic activity for ARG degradation with the lowest energy consumption (Ep) due to its highest oxygen evolution potential (OEP), good electric conductivity and massive Oad. After the kinetic fitting, the removal of ARG was according to the first order kinetics and the rate constants (k) for PbO2-2.0 vt% was 4.69 × 10−2 min−1, which was 1.86 times higher than that of PbO2-0 vt% (2.52 × 10−2 min−1). In addition, the dissolution reaction of Pb ion was suppressed after the PVA modification, ensuring the safety performance in application. Furthermore, the result of accelerated service life tests showed that the PbO2-2.0 vt% electrode exhibited the highest stability and the accelerated service life was 329.5 h, which was more than 3 times longer than that of PbO2-0 vt% electrode (96 h). Thus, the PbO2-2.0 vt% electrode was considered to be the most optimal electrode in this study.
Acknowledgements
This work was supported by the National Natural Science Foundation of China (Grant No. 21507104).
References
- Y. H. Cui, X. Y. Li and G. Chen, Water Res., 2009, 43, 1968–1976 CrossRef CAS PubMed.
- L. S. Andrade, T. T. Tasso, D. L. da Silva, R. C. Rocha-Filho, N. Bocchi and S. R. Biaggio, Electrochim. Acta, 2009, 54, 2024–2030 CrossRef CAS.
- D. Li, J. Tang, X. Zhou, J. Li, X. Sun, J. Shen, L. Wang and W. Han, Chemosphere, 2016, 149, 49–56 CrossRef CAS PubMed.
- S. Chai, G. Zhao, Y. Wang, Y.-N. Zhang, Y. Wang, Y. Jin and X. Huang, Appl. Catal., B, 2014, 147, 275–286 CrossRef CAS.
- B. Cercado-Quezada, M.-L. Delia and A. Bergel, Electrochem. Commun., 2011, 13, 440–443 CrossRef CAS.
- A. N. Subba Rao and V. T. Venkatarangaiah, Environ. Sci. Pollut. Res. Int., 2014, 21, 3197–3217 CrossRef CAS PubMed.
- M. G. Tavares, L. V. A. da Silva, A. M. Sales Solano, J. Tonholo, C. A. Martínez-Huitle and C. L. P. S. Zanta, Chem. Eng. J., 2012, 204–206, 141–150 CrossRef CAS.
- C. I. Brinzila, M. J. Pacheco, L. Ciríaco, R. C. Ciobanu and A. Lopes, Chem. Eng. J., 2012, 209, 54–61 CrossRef CAS.
- W. Wu, Z.-H. Huang and T.-T. Lim, Appl. Catal., A, 2014, 480, 58–78 CrossRef CAS.
- L. Zhang, L. Xu, J. He and J. Zhang, Electrochim. Acta, 2014, 117, 192–201 CrossRef CAS.
- D. Devilliers and E. Mahé, Electrochim. Acta, 2010, 55, 8207–8214 CrossRef CAS.
- I. Sirés, C. T. J. Low, C. Ponce-de-León and F. C. Walsh, Electrochim. Acta, 2010, 55, 2163–2172 CrossRef.
- H. Xu, Q. Yuan, D. Shao, H. Yang, J. Liang, J. Feng and W. Yan, J. Hazard. Mater., 2015, 286, 509–516 CrossRef PubMed.
- A. Y. Bagastyo, J. Radjenovic, Y. Mu, R. A. Rozendal, D. J. Batstone and K. Rabaey, Water Res., 2011, 45, 4951–4959 CrossRef CAS PubMed.
- G. Zhao, Y. Zhang, Y. Lei, B. Lv, J. Gao, Y. Zhang and D. Li, Environ. Sci. Technol., 2014, 44, 1754–1759 CrossRef PubMed.
- H. An, H. Cui, W. Zhang, J. Zhai, Y. Qian, X. Xie and Q. Li, Chem. Eng. J., 2012, 209, 86–93 CrossRef CAS.
- J. Chen, Y. Xia and Q. Dai, Electrochim. Acta, 2015, 165, 277–287 CrossRef CAS.
- C. Borrás, T. Laredo, J. Mostany and B. R. Scharifker, Electrochim. Acta, 2004, 49, 641–648 CrossRef.
- L. S. Andrade, R. C. Rocha-Filho, N. Bocchi, S. R. Biaggio, J. Iniesta, V. Garcia-Garcia and V. Montiel, J. Hazard. Mater., 2008, 153, 252–260 CrossRef CAS PubMed.
- L. S. Andrade, L. A. Ruotolo, R. C. Rocha-Filho, N. Bocchi, S. R. Biaggio, J. Iniesta, V. Garcia-Garcia and V. Montiel, Chemosphere, 2007, 66, 2035–2043 CrossRef CAS PubMed.
- Q. Li, Q. Zhang, H. Cui, L. Ding, Z. Wei and J. Zhai, Chem. Eng. J., 2013, 228, 806–814 CrossRef CAS.
- H. Xu, D. Shao, Q. Zhang, H. Yang and W. Yan, RSC Adv., 2014, 4, 25011–25017 RSC.
- H. Kong, W. Li, H. Lin, Z. Shi, H. Lu, Y. Dan and W. Huang, Surf. Interface Anal., 2013, 45, 715–721 CrossRef CAS.
- J. Cao, H. Zhao, F. Cao and J. Zhang, Electrochim. Acta, 2007, 52, 7870–7876 CrossRef CAS.
- H. Xu, Q. Zhang, W. Yan, W. Chu and L. Zhang, Int. J. Electrochem. Sci., 2013, 8, 5382–5395 CAS.
- L. Aroui, L. Zerroual and M. Boutahala, Mater. Res. Bull., 2012, 47, 206–211 CrossRef CAS.
- X. Duan, F. Ma, Z. Yuan, L. Chang and X. Jin, Electrochim. Acta, 2012, 76, 333–343 CrossRef CAS.
- B. J. Hwang and K. L. Lee, J. Appl. Electrochem., 1996, 26, 153–159 CrossRef CAS.
- Q. Dai, H. Shen, Y. Xia, F. Chen, J. Wang and J. Chen, Sep. Purif. Technol., 2013, 104, 9–16 CrossRef CAS.
- H. Xu, W. Guo, J. Wu, J. Feng, H. Yang and W. Yan, RSC Adv., 2016, 6, 7610–7617 RSC.
- W. H. Yang, W. T. Yang and X. Y. Lin, Appl. Surf. Sci., 2012, 258, 5716–5722 CrossRef CAS.
- C. C. DeMerlis and D. R. Schoneker, Food Chem. Toxicol., 2003, 41, 319–326 CrossRef CAS PubMed.
- S. Ghasemi, M. F. Mousavi and M. Shamsipur, Electrochim. Acta, 2007, 53, 459–467 CrossRef CAS.
- X. Hu, R. Mamoto, Y. Shimomura, K. Kimbara and F. Kawai, Arch. Microbiol., 2007, 188, 235–241 CrossRef CAS PubMed.
- X. Li, D. Shao, H. Xu, W. Lv and W. Yan, Chem. Eng. J., 2016, 285, 1–10 CrossRef CAS.
- Y. Chen, L. Hong, H. Xue, W. Han, L. Wang, X. Sun and J. Li, J. Electroanal. Chem., 2010, 648, 119–127 CrossRef CAS.
- Y. Yao, L. Cui, L. Jiao, X. Chen, N. Yu and H. Dong, J. Solid State Electrochem., 2015, 20, 725–731 CrossRef.
- L. Xu, M. Li and W. Xu, Electrochim. Acta, 2015, 166, 64–72 CrossRef CAS.
- D. Shao, W. Yan, X. Li and H. Xu, ACS Sustainable Chem. Eng., 2015, 3, 1777–1785 CrossRef CAS.
- S.-P. Tong, C.-A. Ma and H. Feng, Electrochim. Acta, 2008, 53, 3002–3006 CrossRef CAS.
- Y. Duan, Q. Wen, Y. Chen, T. Duan and Y. Zhou, Appl. Surf. Sci., 2014, 320, 746–755 CrossRef CAS.
- S. Yang, Y. Feng, J. Wan, W. Zhu and Z. Jiang, Appl. Surf. Sci., 2005, 246, 222–228 CrossRef CAS.
- N. K. V. Leitner and M. Dope, Water Res., 1996, 31, 1383–1397 CrossRef.
- D. Shao, W. Yan, X. Li, H. Yang and H. Xu, Ind. Eng. Chem. Res., 2014, 53, 3898–3907 CrossRef CAS.
|
| This journal is © The Royal Society of Chemistry 2016 |
Click here to see how this site uses Cookies. View our privacy policy here.