Kaiyuan Shi and
Igor Zhitomirsky*
Department of Materials Science and Engineering, McMaster University, 1280 Main Street West Hamilton, ON, Canada L8S 4L7. E-mail: zhitom@mcmaster.ca; Tel: +1-905-525-9140
First published on 24th November 2014
Multiwalled carbon nanotubes (MWCNT) are coated with nitrogen doped activated carbon (NC) for applications in electrochemical supercapacitor electrodes and devices. The capacitive behavior of the electrodes and devices is tested in solutions of organic dyes. The process involves energy accumulation in electrical double layers. The accumulated energy may be further utilized to remove dyes with a similar scheme via discharge of the supercapacitor, also fully regenerating the electrode materials for further use. Proof of concept investigations involve the testing of anionic and cationic dyes and analysis of the influence of dye concentration, charge as well as charge to mass ratio on the capacitance, impedance, specific power and energy of the devices. Cyclic voltammetry and chronopotentiometry data, obtained in different voltage windows, are used for the optimization of device performance. The discussion of quartz crystal microbalance data provides an insight into the factors which govern the charge–discharge behavior. The devices show good cyclic stability. This method offers the advantage of saving energy and applicability to a variety of different dyes.
A new wave of interest in the ES technology is related to the application of ES devices for capacitive deionization (CDI)22,23 which was found to be a robust, energy efficient, and cost effective technology for desalination of water with a low or moderate salt content. In the CDI technology, the charging process results in removal of ions from the solutions and their accumulation in electrodes for energy storage in electrical double layers. The energy, released during the discharge process, can be used for the charging of neighbouring cells. Therefore, the CDI technology offers the advantages of energy saving.22 Ongoing research is focused on the optimization of operation modes, investigation of the kinetics of ion removal and development of efficient electrode materials.23–26 Special attention is focused on the surface modification of electrode materials. It was shown that the fabrication of porous carbon electrodes with high surface area is of critical importance for further development of the CDI technology. Other important properties of electrode materials are: high chemical stability, high electronic conductivity, surface charge and good wetting behaviour.22
Recent advances in the CDI technology indicate that ES are promising devices for the capacitive removal of other charged species from aqueous solutions. Of special interest is the possibility of capacitive dye removal from the solutions. Organic dyes are widely used for many applications, such as solar cells,27 photocatalysis,28 transistors,29 biological and chemical sensors,30 lasers,31 medicine,32 textile industry33 and high tech applications.33 The increased utilization of organic dyes for various applications given their rich diversity and complexity mandates the development of robust methods for dye removal from the chemical waste. Physical adsorption, chemical and biochemical treatment are important methods for dye removal.34–36 Significant progress has also been made in the development of chemical oxidation and reduction, photocatalytic and ozonation methods.37 Electrochemistry is widely recognized as an essential tool for dye removal from wastewaters.38,39 Different electrochemical techniques have been developed, such as electrocoagulation, electrochemical reduction, electrochemical oxidation, photoassisted electrochemical methods and other techniques.39,40 The methods have some inherent problems,39 such as significant energy consumption, electrode degradation and limited range of applications. To date, no single method has demonstrated the combined facets of wide chemical compatibility, low energy usage, inexpensive processing, and high recyclability.39 The diversity and complexity of the dyes generates a need in new methods for dye removal.
In a previous investigation,41 we observed significant changes of the mass of quartz crystal microbalance resonators in response to an applied electric field in the dilute solutions of the anionic methyl blue dye. Such mass gain of the electrodes resulted from the accumulation of the dye molecules at the electrode surface. It was suggested that the accumulation of the charged dyes at the electrode can be used for energy storage and capacitive dye removal. However, previous investigations were limited to the quartz crystal microbalance studies of mass gain in the dilute solutions of the anionic methyl blue dye. No direct observation of capacitive behaviour and energy storage was reported.
There is a need in the proof-of-concept studies, involving demonstration of capacitive properties and energy storage in individual electrodes and two electrode devices in dye solutions, including solutions of different cationic and anionic dyes at different concentrations. The important task is the measurements of capacitance of individual electrodes and devices using cycling voltammetry and constant current charge–discharge techniques. Another important task is the measurements and analysis of impedance and AC capacitance, derived from the impedance data. Such studies must be performed in more concentrated solutions in order to achieve sufficient energy accumulation in the electrical double layers. Critical to the development and testing of robust ES cells is the utilization of efficient electrodes with high active mass loadings. In contrast to previous investigations, the microbalance data must be obtained at different voltages. One of the important parameters of the supercapacitor devices is the voltage window, which must be optimized using electrochemical testing and quartz crystal microbalance data. The comparison of the data for different dyes with different structures and charges can provide valuable information, related to the feasibility of energy storage in devices, containing organic dyes as electrolytes. It is important to analyze the Coulombic efficiency and power-energy characteristics of the devices. Such proof-of concepts studies were the goal of our work, focused on the analysis of capacitive behavior of electrodes and devices in solutions of different dyes.
In addition to addressing the proof-of-concept questions, we analyzed the data for different dyes, which provide an insight into the influence of dye structure and charge on capacitive behavior of the devices. Moreover, the results presented below indicated that the method of capacitive dye removal can be used for energy storage. Electrode regeneration resulted in energy release that may be further utilized for continued purification via charging of neighboring cells or other applications. This method offers the advantage of vastly improved energy utilization. The dyes can be reused after the electrode regeneration. Our results demonstrate the wide applicability of capacitive dye removal that can be used for both cationic and anionic dyes.
The QCM studies of capacitive adsorption and desorption were performed in the pulse mode, using positive and negative pulses with a constant voltage of 1 V or by applying a series of positive or negative pulses of increasing amplitude in the range of 0.6–1.4 V. The electrode separation distance was 1 cm. The ON and OFF times were 1 min. A Keithley (model 2400) power supply was used for the QCM studies.
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Fig. 2 (A) Aqueous solutions of (a) SF, (b) CL, (c) AM and chemical structures of (B) SF, (C) CL and (D) AM. |
The use of NC–MWCNT as an electrode material for capacitive dye removal offered the advantages of high surface area of NC and high conductivity of MWCNT. Fig. 3A and B presents typical TEM images of NC–MWCNT at different magnifications. The TEM image at lower magnification (Fig. 3A) showed uniform diameter of NC–MWCNT. The higher magnification image (Fig. 3B) indicated the formation of relatively uniform NC coatings. The NC–MWCNT material has a surface area of 1889 m2 g−1 (Fig. S1† and related data analysis in the ESI†).
Fig. 4(A and B) shows CVs for NC–MWCNT electrodes in SF and CL solutions. The area of the CVs increased with increasing dye concentration, indicating the increase in number of adsorbed dye molecules, contributing to the formation of the electrical double layer and charge–discharge currents. The capacitances, calculated from the CV data are presented in Fig. 4C. The electrodes showed comparable capacitances of 39 and 41 F g−1 in the solutions of SF and CL dyes, respectively, at dye concentration of 100 mg L−1. However, the capacitance achieved in SF solutions at concentrations of 200 and 400 mg L−1 was higher than the capacitance in CL solutions of similar concentrations. The capacitances in 400 mg L−1 solutions of SF and CL dyes were found to be 145 and 103 F g−1, respectively.
Fundamental studies performed by other groups showed that capacitance of porous carbon materials depends on the size of the electrolyte molecules and pore size of carbon.52–56 They found53 that using ionic liquid electrolytes and activated carbons with controlled pore size, the specific capacitance of 160 F g−1 can be achieved, which is much higher than the specific capacitance reported (50–100 F g−1) for commercial activated carbons. The size of SF and CL dyes (Table S1†) is comparable with the size of the ionic liquid molecules.53 The specific capacitance of NC–MWCNT electrodes, achieved in the SF solutions was comparable with specific capacitance of the carbon materials in ionic liquid electrolytes. It is important to note that the solutions of SF and CL dyes contained large cation or anion, respectively, and smaller counter ions. In this case, the capacitive performance is strongly influenced by large ions. The lower capacitance, achieved in the CL solutions, can be partially attributed to larger mass and size of the CL molecules (Table S1†), which can result in lower ion mobility. It is known54 that charge storage in double layers is influenced by ion transport. The difference in performance of NC–MWCNT electrodes in the solutions of SF and CL dyes can also be attributed to electrostatic interactions of NC–MWCNT and SF+ cations or CL− anions. Recent studies have shown that cationic and anionic transports in pores depend57–60 on point of zero charge of the electrode material. It was demonstrated that negatively charged carbon nanotubes promoted cationic transport.58 The potential of zero charge was found to be different from the potential of zero mass change,61 that separates the mass change of the electrode due to adsorption of cations and anions. Other investigations emphasized the influence of hydrophobic interactions with pore walls.62
The investigations of the electrochemical impedance Z* = Z′ − iZ′′ of the NC–MWCNT electrodes in SF and CL solutions, presented in the Nyquist plot (Fig. 4D), showed that the increase in dye concentration resulted in decreasing resistance R = Z′. The decrease in Z′′ with increasing dye concentration indicated increasing capacitance C′ = Z′′/ω|Z|2.
The capacitive dye removal has also been investigated using a QCM method, which is an efficient tool for monitoring the incorporation of ions into the ES electrodes during charge and discharge cycles.61,63,64 Testing results showed that the application of negative or positive pulses to the NC–MWCNT electrodes in SF or CL solutions, respectively, resulted in mass gain, attributed to incorporation of cationic SF or anionic CL species into the electrode (Fig. 5A and B). The mass gain versus time curves for the electrodes are typically characterized by several domains, representing complex interactions of ions and porous electrodes.61 The electrode mass decreased during the OFF time. The experiments showed periodic variations in the electrode mass. Such periodic variations, related to dye removal, indicate a possibility of regeneration of the electrode material. The increase in pulse amplitude resulted in increasing mass gain (Fig. 5B and D and Table S2†), indicating the increase in amount of ions incorporated into the electrodes.
The results of CV and QCM testing paved the way for the fabrication of ES devices that enabled the removal of dyes from aqueous solutions and energy storage in electrical double layers of NC–MWCNT electrodes (Fig. S2†). The charge–discharge behavior of the two-electrode devices was analyzed in different voltage windows (Fig. 6A–F). Fig. 6(A and D) shows CVs in different voltage windows for the ES devices, containing SF or CL electrolytes at a scan rate of 2 mV s−1. The increase in the voltage window above 0.9 V resulted in significant increase in current, attributed to redox reactions. The galvanostatic charge–discharge curves obtained at a current density of 3 mA cm−2 showed significant voltage drop at the beginning of the discharge for voltage windows above 0.9 V (Fig. 6(B and E)). Such voltage drop V = IR (I – current) can be attributed to increased electrical resistance R of the cells. The cell capacitances and Coulombic efficiencies decreased in the potential windows above 0.9–1 V (Fig. 6C and F). Therefore, further investigations were performed in the potential window of 0.9 V. Fig. 7(A and B) shows CVs at different scan rates in the voltage window of 0.9 V. The larger area of the CVs obtained for the cells, containing SF electrolyte (Fig. 7A), compared to the cells, containing CL electrolyte (Fig. 7B), indicated higher capacitance of the SF cells. The capacitance, calculated from the CV data is plotted versus scan rate in the Fig. 7C. The cells, containing SF electrolyte, showed higher capacitance, compared to the cells containing CL electrolyte. The difference was especially evident at scan rates above 2 mV s−1. The lower capacitance of the cells, containing CL electrolyte, can result from higher resistance of such cells (Fig. S3†). Moreover the analysis of the impedance data showed that the real component C′ = Z′′/ω|Z|2 of complex capacitance for CL containing cells was lower, compared to that of SF containing cells (Fig. S3†). This result correlated with capacitance data, calculated from CVs for the same cells.
Fig. 8(A and B) shows charge–discharge behavior of ES devices, containing two NC–MWCNT electrodes and SF or CL electrolytes in a voltage window of 0.9 V. The charge–discharge curves showed nearly symmetrical triangular shape, however voltage drop was observed at the beginning of the discharge curve. This voltage drop U = IR (I – current, R – resistance) was especially evident for the cells, containing CL electrolyte, due to higher resistance. The devices, based on SF electrolyte showed higher capacitance and better capacitance retention (Fig. 8C) in the current density range of 1–8 mA cm−2. The energy densities and power densities for the devices were presented in Fig. 8D. The devices (Fig. 8D, insets), based on SF and CL showed maximum energy density of 5.3 and 4.1 mW h g−1 and power density of 525 and 137 mW g−1, respectively.
The SF and CL dyes contain only one charged group per molecule. We suggest that capacitive removal is especially attractive for the dyes with several charged groups per molecule and higher charge to mass ratio. As pointed out above, the structure of AM dye is similar to that of CL dye, however, the AM molecule has three charged groups. The higher charge to mass ratio of AM molecules can be beneficial for their electromigration during charge and discharge. The ES cells, containing AM electrolyte, showed improved capacitive behavior, compared to the cells, containing CL electrolyte of the same concentration. The improved capacitive behavior is indicated by the larger area of CVs and nearly triangular shape of charge–discharge curves with reduced V = IR drop at the beginning of discharge in the voltage window of 0.9 V (Fig. 9A and B). The CVs obtained in larger voltage windows showed significant deviation from the box shape and increasing current related to electrochemical decomposition of water (Fig. S4A†). The charge–discharge curves showed the increase in voltage drop with increasing voltage window (Fig. S4B†). Therefore, similar to SF and CL cells, the voltage window of the AM cells was optimized at 0.9 V. Fig. 9C and D shows capacitances, calculated from CVs (Fig. 9A) and galvanostatic discharge (Fig. 9B) data. The AM cells showed higher capacitance and improved capacitance retention at high charge discharge rates, compared to CL cells. The capacitance of the AM cell at a scan rate of 20 V s−1 was 9.0 F g−1 (0.27 F cm−2), whereas the capacitance of the CL cell at the same scan rate was only 2.7 F g−1 (0.08 F cm−2). The capacitance of the AM cell at a discharge current of 8 mA cm−2 was 19.5 F g−1 (0.60 F cm−2), however the capacitance of CL cell at the same discharge current was only 9.60 F g−1 (0.29 F cm−2). The difference can result from higher mobility of the AM dye, which has higher charge and higher charge to mass ratio, compared to CL. The analysis of the impedance data for the cells, containing AM electrolyte showed lower resistance R = Z′ of the AM cells (Fig. S5A†), compared to the resistance of the CL cells. The lower resistance can provide improved power density. Moreover the AM cells showed higher AC capacitance C′ (Fig. S5B†), compared to the capacitance of CL cells. The capacitance of the AM cell, calculated from the discharge data increased with increasing voltage window and showed a maximum at a voltage of 1.1 V (Fig. 9E). The Coulombic efficiency (Fig. 9E) decreased with increasing voltage window, especially at voltages above 0.9 V. Fig. 9F presents a Ragone plot for the cell, containing AM electrolyte. The cell showed maximum energy density of 7.0 mW h g−1 and maximum power density of 337 mW g−1. The higher power density of the cell, containing AM electrolyte, compared to the cell containing CL electrolyte are attributed to higher capacitance and lower resistance of the AM cell.
The use of capacitive dye removal offers the advantage of efficient energy utilization, because the dyes, removed from solutions are used for energy storage in the electrical double layers. On the discharge cycle, this energy may be utilized to charge an analogous ES for dye removal or other applications. Turning again to the QCM data it should be mentioned that the method allows electrode regeneration. The dyes released during the discharge cycle can be used for other applications. This suggestion was supported by the analysis of cyclic stability of the cells. The AM cells showed 85.3 and 80.4% capacitance retention after 1000 and 3000 cycles, respectively (Fig. S6†). Quartz crystal microbalance studies of efficiency of dye removal (Fig. S7†) showed that one charging cycle resulted in the removal of 14.65% of AM dye from 50 mg L−1 AM dye solution at a deposition voltage of 1 V. The mass ratio of removed dye material to the mass of electrode material was 80 mg g−1. It is expected that further advances in the capacitive dye removal method can be achieved by the development of efficient electrodes with high porosity and this method will be used for other cationic and anionic dyes.
Footnote |
† Electronic supplementary information (ESI) available: BET results, cyclic voltammetry, chronopotentiometry, impedance spectroscopy data and cyclic behaviour, basic properties of dyes. See DOI: 10.1039/c4ra12635a |
This journal is © The Royal Society of Chemistry 2015 |