Enhanced performance and degradation of wastewater in microbial fuel cells using titanium dioxide nanowire photocathodes.

This paper explores the decolorization of dye wastewaters and electricity generation using dual-chamber microbial fuel cells (MFCs) with titanium dioxide nanowire (TiO2 NW) photocathodes. TiO2 NW cathodes under ultraviolet light are observed to enhance the reduction of azo dye Active Red 30 (AR 30) and electricity generation. The analysis of electrochemical impedance spectra (EIS) indicates acceleration of the electron transfer processes of photoelectrode reduction by the photocatalysis of TiO2 NWs, with polarization resistance of the photocathode being 10.45 Ω under light irradiation from 294 Ω in the dark. Ultraviolet-visible light spectroscopy shows that the maximum degradation of the MFCs is 78.1%; the azo bond of AR 30 may be cleaved by photoelectrons generated by light irradiation of the illuminated TiO2 NW photocathode. The electricity produced by microbial fuel cells (MFCs) is expected to enhance the reductive decolorization of the azo dye AR 30 solution. This journal is © The Royal Society of Chemistry.

Introduction

Synthetic azo dyes, as organic compounds with structural diversity, have been widely used in textile finishing mills. It is well known that the azo dyes have low degradability due to their high chemical, biological and photocatalytic stability.[1] The azo dye components remaining in the wastewater, even in low concentrations, will cause the light transmittance within the water body to decrease, which eventually leads to the destruction of the water ecosystem.[2,3] At present, many technologies have been used to treat azo dye wastewater, including sorbent removal,[4-7] coagulation/flocculation,[8-11] membrane separation[12-17] and advanced oxidation.[18,19] The unique advantages are respectively demonstrated in these treatment methods, however there are common problems with high energy input requirements and sludge generation. Therefore, it is imperative to develop effective treatment technology to solve the problem. As one kind of sustainable bio-electrochemical system, the area of interest in MFCs is to combine wastewater treatment and biological power generation.[20] Electrons are released by microorganisms to the anode in the MFC, and then transferred to the cathode by the circuit, where they combine with protons and electron acceptor (such as oxygen) to form water.[21-23] The microorganisms on the surface of the anode are used as biocatalysts to reduce the overpotential as well as enhance the speed of electron transfer to the cathode, and the azo compound can be reduced in the cathode chamber.

High cathode overpotential is one of the bottlenecks in the use of MFC to reduce azo dyes, and semiconductor materials as electrode catalysts for the photoelectric degradation of azo dye wastewater are widely considered as a novel technology in enhancing the performance of MFCs.[24,25] In the current research, the type of powder catalyst has been widely studied. Most of the catalysts are used as electrodes in the process of constructing microbial fuel cells, therefore, powdered catalytic materials and other conductive materials must be mixed and pressed to prepare electrodes and other conductive materials can easily block light and affect the absorption of light by the catalytic material in this process. Meanwhile, poor contact may occur during the mixing process of the powder catalytic material with other materials, which affects the conduction of photoelectrodes to photogenerated electrons and holes. Here, we propose the photocatalytic material prepared by the anodic oxidation method can take advantage of the natural connection between the photocatalytic material and the titanium electrode, reducing the mixing and pressing process of the photocatalytic material and the conductive matrix and making the photocatalytic material easier to carry out on the anode. The surface of the photoelectrode stimulates the absorption of light energy, and the photo-generated holes are quickly transferred to the circuit system, thereby accelerating the overall reaction speed of the microbial fuel cell. Li et al.[26] reported the effect of the presence or absence of light on the potential generated by the MFCs coated with rutile TiO2 cathode and found that the maximum potential presented in the illumination was 0.80 V while the maximum potential generated in the absence of light was 0.55 V. Long et al.[27] have systematically studied the titanium dioxide nanotube array significantly increased the power generation amount from 3.64 ± 0.112 mA to 6.246 ± 0.135 mA at the bioanode, which can effectively photo-catalytically degrade reactive brilliant active brilliant red X3 (ABRX3). Lu et al.[28] improved the maximum power density of the reactors under illumination was 1.6 fold, compared with dark conditions. This is the result of the enhanced cathode electron transfer by the use of semiconducting minerals, indicating that the potential of MFCs generated by light is increased. Substances of the cathodic surface, which have high redox potential, will be reduced by electrons transfer from the anode chamber. The bandwidth energy of the semiconductor materials is equal or exceeded by light energy, the electrons are excited from the valence band (VB) to the conduction band (CB) can generate the high oxidative photo-generated carriers (electron–hole pairs).[29] According to the mechanism, pollutants can increase the cathode redox potential, the performance of microbial fuel cells, while degrade the pollutants to achieve simultaneous degradation of the pollutants and the effect of power generation. Due to the outstanding advantages, the photoelectrodes has attracted attention of more and more researchers in the past years.[30-32] The Table 1 was conducted to summarize the typical research of the MFCs with photoelectrodes.

A summary of photoelectrodes were used in MFCs

Reactor types	Photocathode design	Microbial composition	Source of inoculation	Performance	Reference
DCa/UVc	BTNAd	Proteobacteria	MFC effluent	6.246 ± 0.135 mA	27
DCa/Visb	Rutile coated graphite	MSf	Yeast extract	16.5 mA m−2	33
DCa/UVc	Cu2O nanowire	MSf	Freshwater sediment	46.44 mW m−2	34
DCa/Visb	Pd/SiNWe	MSf	Mixed anaerobic sludge	119 mW m−2	35
DCa/Visb	Pd/SiNWe	MSf	Mixed anaerobic sludge	180119 mW m−2	36
DCa/Visb	Bi/TiO2	MSf	Anaerobic sludge	224 mW m−2	37
DCa/UVc	TiO2	MSf	Anaerobic sludge	19.4 mA m−2	38
DCa/UVc	Algae	Rhodopseudomonas	Wetland sediment	202.9 ± 18.1 mW m−2	39

DC, dual chambers.

Vis, visible light.

UV, ultraviolet light.

BTNA, blue titania nanotube arrays.

SiNW, p-type silicon nanowire.

MS, mixed strains.

Due to its relatively stable chemical properties, biological stability, excellent electrical and optical properties, the titanium dioxide (TiO2) has been widely accepted for semiconductor catalyst material in terms of dye photocatalysis.[40] TiO2 has been proven to be a good ORR catalyst for enhancing the performance of MFCs, used for the photocatalytic reduction of dyes wastewater in the MFCs reactor, as well as the application of photocatalysis has significantly improved the power generation performance of microbial fuel cells.[41-43] However, most attention has been paid to the productivity efficiency of photocatalytic microbial anodes and little information has been reported concerning cathodic reduction to produce MFCs anodes and photocathodes for pollutant degradation and electricity generation.[27,34]

Nanostructured photocathodes can be produced with well properties on account of the synergy effect in MFCs, including great electrical conductivity, extra apparent area and high performance.[44,45] In this study, the TiO2 NWs photocathode of MFCs reactor were carried out the structure and photoelectrochemical properties. The systematic research was performed to analyze the output voltage, the photoelectrocatalytic activity, the degradation efficiency and mechanism of AR 30. In order to observe the electrode morphology and crystalline structure, the scanning electron microscope (SEM), the Fourier infrared spectroscopy (FT-IR) and the X-ray diffraction analysis (XRD) were applied for the characterization. In addition, the cyclic voltammetry (CV), the electrochemical impedance spectroscopy (EIS), Tafel test and the ultraviolet-visible spectrometer (UV-vis) were used to study the electricity generation and dye degradation ability of MFCs. The research further revealed the potential possibility of photocathode on improving the performance of reactor at the dye wastewater treatment combined power production of MFCs, and provide a new way for the degradation of pollutants in the reactor. We hope that the study will be useful to develop an efficient MFCs technique in azo dye-containing wastewater treatment and the development of MFC in the future.

Materials and methods

MFCs construction and operation

A typical dual-chamber MFC reactor was employed in this research. Each chamber was separated by cation exchange membranes (Qianqiu, Zhejiang, China) with an area of 85 cm2 and constructed of two equal volumes of 100 mL rectangular plexiglass chambers (Wenoote, Shanghai, China). Anode chamber was sealed with rubber stopper and cathode chamber was left with a 10 cm vent for continuous air filling continuously. Furthermore, the straight distance between anode and photocathode electrode was approximately 10 cm in microbial fuel cells and the external resistance was 22 Ω. Three different types of cathode electrodes (TiO2, TiO2 NWs, plain Ti, respectively) are connected by titanium wire. The Ag/AgCl worked as a reference electrode, then a 360 nm ultraviolet light source was installed 10 cm away from the cathode (Antoine; Change Lighting Technology Co., Ltd., Dongguan, China). The anode chambers were inoculated with reacclimated microbial solution initially from the wetland sediment, in addition, the microbial community had been function stably for three years within the effluent from previous MFCs.[34,39] The anolyte was mineral salt (1.98 g L−1), K2HPO4 (6.59 g L−1), KH2PO4 (2.88 g L−1), C6H12O6 (1.00 g L−1) and CH3COONa (1.42 g L−1) and this catholyte comprised: NaNO3 (1.40 g L−1), NaHCO3 (0.98 g L−1), KCl (0.11 g L−1) and Active red 30 (AR 30, 10 mg L−1). The cathode compartment in MFCs was ventilated with oxygen pumps at a gas flow rate of 70 L h−1 to provide sufficient oxygen for the electrochemical reaction, and distilled water was used to supplement the evaporated water every 24 hours. All MFCs reactors are operated in a 25 ± 2 °C incubator (GHP-9080, Bluepard, Shanghai, China).

Preparation of titanium dioxide nanowire electrode

TiO2 nanowires were prepared by thermal annealing of anodized titanium plates in air. Titanium plates (3.0 × 2.0 × 0.1 cm, purity 99%) were successively immersed into an aqueous solution of 15 wt% sodium hydroxide at 60 °C, 30 vt% hydrochloric acid solution for pretreatment at 100 °C, and then stored in deionized water or isopropyl alcohol after the ultrasonic cleaning. The pretreated titanium samples were immersed in a 5 wt% NH4F and ethylene glycol solution and further anodized at the constant battery voltage at 30 V for 6 hours. A graphite plate was performed to use as the counter electrode and the magnetic stirrers were used in this process. After the solution turned blue, the titanium plate was washed by the deionized water, and then dried at about 40 °C in the drying oven. The 100 mA cathode current was applied by an electrochemical workstation for 30 s to oxidize the electrode, which in the electrolytic solution was 0.1 M KH2PO4. Finally, the titanium plates were calcined at 450 °C for 2 hours using the electric box resistance furnace (SX2-0.5-10A, Shaoxing, China).

Electrode characterizations

The apparent topography of the prepared materials was determined by employing the scanning electron microscope (SEM, JSM-5600 LV, Tokyo, Japan) at the start and the constituent elements were observed by a co-configured energy dispersive spectrometer (EDS, 20.0 kV). The crystal phases of prepared electrodes were used for the identification by the X-ray diffraction technology (XRD, Rigaku D/MAX-2550VB/PC, Tokyo, Japan). The functional groups and metal bonds contained in the sample were determined for the identification using the Fourier transform infrared spectroscopy (FT-IR, Nicolet Nexus 470, Massachusetts, America).

Electrochemical experiments

The test data acquisition system (BT-2016C, LANBTS, Wuhan, China) was used to record the cell output voltage level of the reactor each 30 seconds in this study. The electrochemical characteristics of the MFCs reactor with cathodic photoelectrodes were observed within third consecutive cycles in detail.[46] The electrochemical measurements were accurately evaluated in order to the performance of MFCs reactor under different conditions by the electrochemical workstation methods (CHI760E, Chenhua, Shanghai, China), including the cyclic voltammetry (CV), the electrochemical impedance (EIS) and the Tafel curve. The CV in the experiment was performed to implement in a potential range of 0 to 2.0 V (vs. Ag/AgCl) with the sweeping rate of 10–80 mV s−1 under different test systems. The titanium dioxide nanowires, graphite and Ag/AgCl (sat. KCl) were separately used as the work electrode, counter electrode and reference electrode in standard three-electrode and the titanium dioxide nanowires, graphite were used as the work electrode, counter electrode in two-electrode system. The EIS was performed (10 Hz to 500 kHz) to calculate the resistance of electrodes and then the fitting calculation data were received with Z-SimpWin software by using a suitable model. The Tafel plots was investigated within the overpotential range of 0.5 to −0.5 mV with a sweeping rate at 1 mV s−1 to evaluate the corrosion resistance of cathodic materials. In addition, we used the electrochemical measurements for the anode compartment in the microbial fuel cells under anaerobic/anoxic conditions, which based on the open circuit was carried out to maintain a continuous output voltage before the electrochemical test.

Photoelectrocatalytic degradation experiments

After the MFCs reactor were constructed, the carbon felt cathode was replaced with a titanium dioxide nanowires or titanium electrodes. The azo dye AR 30 was used as a model organic pollutant in order to determine the photoelectrochemical degradation of the MFCs. The 100 mL of 10 mg L−1 AR 30 solutions were carried out to enter the cathodic chamber, then irradiated with an ultraviolet light source at a distance of 10 cm. The 22 Ω external resistor was used to the connection of the anode and cathode electrode, and then a data acquisition system was used to monitor the voltage of MFCs. During the experiments, the samples of the cathode chamber were extracted every 1 hour and analyzed the concentration of azo dye AR 30 by the ultraviolet-visible light spectrophotometer (UV-vis, TU-3900). The absorption wavelength of the dye solution was determined to be 540 nm.

Results and discussion

Characterization of photocathode

The scanning electron microscope (SEM) analysis can be performed to characterize the microscopic surface and structure of the sample. The microtopography of TiO2 nanowires electrodes was investigated using SEM-EDS and the images are shown in Fig. 1(a and b). The hollow TiO2 NWs grows on the substrate thickly, and it is well known that the nanowires can be used for the transfer process of electrons as the effective structure which has been shown to be an efficient structure for electron transfer processes.[25]Fig. 1(a and b) is the image of a TiO2 NWs photoelectrode, it is easy to find that the nanowire structure is relatively complete, and the shape is regular, and the size is relatively uniform. The average diameter is 0.56 μm, and they overlap each other to form a thin film. The titanium dioxide nanowires may progressively grow on the appearance of titanium plate by electrochemical etching reaction. The chemical composition and stoichiometry of photoelectrodes were examined by EDS, the elemental composition of titanium dioxide nanowire photoelectrode, which is in accordance with the operating conditions.

Fig. 1

(a and b) SEM image of the TiO2 NWs electrode. (c) FTIR spectra of commercial titanium dioxide and TiO2 NWs electrode. (d) XRD pattern after pretreatment.

FT-IR spectroscopy was employed to prove the properties of the prepared materials. Prepared photoelectrodes show practically the similar spectrum as commercial titanium dioxide, which shows that titanium dioxide materials have high purity in Fig. 1(c). Specifically, the significant peaks at 3444.99 cm−1 and 1603.44 cm−1 were accorded with the –OH stretching vibration and the –OH bending vibration absorption. Thus, the significant peak at 697.19 cm−1 was accorded with the vibration absorption of Ti–O. Due to the position of the characteristic peak of the prepared titanium dioxide nanowire shifted to high frequency, the absorption peak of TiO2 became wider and the weak peak of the electrode was clearly presented, which certified that the electrode conductivity can be increased by preparing nanowires.

As shown in Fig. 1(d), XRD further confirmed the crystal phase of the obtained sample. The crystalline structure of titanium dioxide nanowire was analyzed, comparing with commercial titanium dioxide. Three distinct reflections attributed to Ti observed at 35.113°, 38.254°, and 40.005°, which can be described to the Ti tetragonal (JCPDS no. 44-1294). The peak at 41.098 corresponded to (002) is titanium hydride (JCPDS no. 25-0983). Titanium hydride was formed on the surface of the pretreated titanium plate, which can increase the real area of the substrate and the working life of the electrode compared with a smooth electrode. Additionally, the diffraction peak of photoelectrode at 25.332°, 38.080°, 38.474°, 47.970°, 54.060°, 55.027°, 62.619° can be indexed with the TiO2 tetragonal (JCPDS no. 21-1272). The pattern revealed the structure of electrodes with peaks at 2θ = 25.332°, 38.474°, and 47.970° corresponded to (101), (112) and (200) indexed with anatase-phase titanium dioxide. The remaining peaks at 38.080, 54.060, 55.027, and 62.619° corresponded to (004), (105), (211), and (213) are rutile titanium dioxide. The crystallite size of the TiO2 NWs electrode was calculated exactly by means of the Debye–Scherrer's eqn (1),In this formula, D, λ, β and θ are the crystalline size in the direction perpendicular to the lattice planes, the wavelength of the CuKα line, the full-width at half maxima intensity of the peak and the Bragg angle, separately. In addition, the default value of λ was given as 0.154 nm in the case of CuKα. The calculation results were shown that the crystallite size of anatase and rutile TiO2 were respectively estimated to be 570.89 nm and 505.05 nm according to this equation and then the reduction of crystallite size and the increase of specific surface area may effectively promote the progress of the PEC reaction as well as the photocatalysis of the rutile titanium dioxide enhanced cathodic electron transfer.[28]

Electrochemical characterization of photoelectrode

It is be seen clearly from Fig. 2 that the titanium dioxide nanowires have capacitive performance in a three-electrode configuration and may be easily applied to the symmetric capacitor. According to the cyclic voltammetry curves in two-electrode model, it can be inferred that the nearly quasi-rectangular curves have the wide working potential window in MFCs.[47]Fig. 2(a–c) shows that the area of the voltammogram follows the order of open circuit > cathode > anode, which indicates that the titanium dioxide nanowire electrode cathode has great potential in catalyzing ORR.

Fig. 2

Electrochemical tests in electrolyte. (a) CV curves of TiO2 NWs electrode electrolyte in three-electrode mode. (b) CV curves of TiO2 NWs anode in two-electrode mode. (c) CV curves of TiO2 NWs cathode in two-electrode mode. (d) Nyquist plots of different electrodes and equivalent circuits used to fit the EIS data. (e) Tafel polarization curves of different electrode. (f) The cells voltage over time under external resistance.

The electrochemical impedance spectroscopy was carried out the effect of illumination on the charge transfer performance of different electrodes, the analysis of electrodes was performed under dark and ultraviolet light irradiation. The Nyquist plots of electrodes was fitted by different equivalent circuits under dark/light conditions. The impedance of the sample was represented by the radius of curvature of the curve, the larger the radius of the curve, the greater the impedance of the sample, and the smaller the number of electrons moving in the electrochemical circuit. As shown in Fig. 2, it can be inferred that the MFCs using the titanium dioxide nanowires have higher rate of promoting electron transfer compared to titanium plate electrodes. The calculated results of electrodes from Nyquist plots were shown in Table 2 by fitting the equivalent circuit model in Fig. 3. The EIS results of open/closed MFCs under a dark condition were analyzed using the R1(CPE1R2)W model, in which CPE1 representing the electrode capacitance and R2 representing the polarization resistance were composed the parallel combination, and R1 corresponding to the ohmic resistance was connected in series with them. In the open circuit condition of MFCs, the R2 value of titanium electrode was 2 fold larger than the TiO2 NWs cathode. The fitting model R1 (CPE1R2)(CPE2R3)W was performed to analyze the results under lighting conditions, in which R3 and CPE2 represent oxide layer resistance and oxide layer capacitor, respectively. Compared with the titanium electrodes of MFCs under dark conditions, the R2 value of the TiO2 NWs cathodic electrode was estimated to be 292.4 Ω. It can be inferred that the polarization resistance of the TiO2 NWs cathodic electrode under above two fitting modes was significantly lower than the titanium cathode in the same bio-electrochemical system. The R3 value of MFCs with TiO2 NWs cathodic electrode under illumination was significantly reduced to 10.45 Ω, which prove that the conductivity of the TiO2 NWs cathodic electrode increases sharply and the PEC activity of the titanium dioxide was considered to be the possible reason. The data fitting results of the Z-SimpWin software were performed to indicate the polarization resistance of TiO2 NWs electrode in closed circuit was significantly reduced and the conductivity cathodic electrode increases sharply, which proved that the largest electrochemical active points was considered to be the possible reason.[48] It can be inferred that the main reason for the exaltation of the power production with TiO2 NWs may be the high electron transference in the light irradiation.[49]

The fitting results of different cathodes electrodes from Nyquist plots

Cathodes	R 2/Ω cm−2	CPE/Ω cm−2 Sn	(A) Dark conditions		(B) Under illumination
			R 2/Ω cm−2	CPE/Ω cm−2 Sn	R 3/Ω cm−2	CPE/Ω cm−2 Sn
Pretreated Ti	9901	9.132 × 10−5	3650	9.84 × 10−4	18.56	3.90 × 10−3
TiO2 NWs	4849	6.132 × 10−5	292.4	3.26 × 10−2	10.45	1.56 × 10−1

Fig. 3

Equivalent circuit models were used in the analysis of electrodes in MFCs (a) under the dark conditions (b) under illumination.

Tafel polarization curves were used to analyze the influence of current density for the corrosion resistance of MFCs cathode materials. It is clear from Table 3, the electrochemical corrosion parameters were calculated by fitting the polarization curve Tafel region, including the corrosion potential (Ecorr), the self-corrosion current density (Icorr) and the polarization resistance (Rp). The Ecorr of metals was inversely proportional to the corrosion tendency, and the magnitude of the corrosion rate was related to the metal polarization phenomenon while the Icorr of the electrode was proportional to the corrosion rate of the system and inversely proportional to the corrosion resistance. Observation of the Tafel curve in Fig. 2(e) shows that titanium dioxide nanowire has the lowest corrosion current density, indicating good corrosion resistance and provides a good basis for further photodegradation experiments.

Corrosion parameters of different electrodes

	E corr (vs. SCE)/V	I corr/(μA cm−2)	R p/(kΩ cm2)
Graphite	0.426	17.6	1481.5
Pretreated Ti	0.061	8.4	2333.7
TiO2 NWs	−0.231	2.4	193.1

The continuing steady process of electrodes was correspondingly vital symbol to estimate the activity of MFCs in the research. Hence, the voltage output of MFCs in closed circuit under the intermittent method was accurately monitored by a data acquisition system in order to observe the stable and durable performance of the electrodes. Fig. 2(f) shows that the voltage can be maintained at the highest pressure of 8–12 days for each cycle, and the electrodes can be maintained of continuous operation at such current densities.[50] Furthermore, the microbial fuel cells with TiO2 NWs cathode exposed the maximum voltage output level of 221 ± 0.02 mV, which was 23.76 and 1.43 times of that of Ti (9.3 ± 0.02 mV) and commercial TiO2 (154.37 ± 0.02 mV), separately. The better coulombic efficiency was generally expressed as a higher voltage output levels and the MFCs with TiO2 NWs photoelectrode was proven to get a large amount of energy using data acquisition system. The MFCs reactors in this study were determined for long-term operation (about 50 d) in a constant temperature incubator, which the voltage output level was controlled stability within each operating cycle. Furthermore, the test results indicated that TiO2 NWs photoelectrode was relatively proven the greatest stability and durability of photoelectrodes in microbial fuel cells.

The optical absorption characteristics of electrodes

As is shown in Fig. 4, the diffuse reflectance spectra of pretreated titanium plates and TiO2 NWs. The optical absorption characteristics of the pretreated titanium plates and TiO2 NWs photoelectrodes were investigated by using UV-vis DRS as well as the test result was presented in Fig. 4(a). TiO2 NWs can absorb light more strongly after anodizing. The absorption of ultraviolet light (<350 nm) and ultraviolet light (>400 nm) in TiO2 NWs is obviously enhanced compared with pretreated titanium plates.

Fig. 4

(a) UV-visible light absorption DRS patterns, (b) calculated energy bandgap of pretreated titanium plates, (c) calculated energy bandgap of TiO2 NWs.

The applicable conditions were affected by the size of the material band gap. Therefore, the UV-vis DRS data was used to calculate the band gap energy value of electrode materials based on formula (2) and the calculated results were shown in Fig. 4(b and c):where α is the absorption coefficient, β is a proportional constant related to the band tailing parameter, hv is the incident photon energy related to Planck constant and Eg is the indirect optical energy gap. The m is related to the semiconductor materials as well the type of transition, m = 1 and m = 4 corresponded to the direct band gap semiconductor materials and the indirect band gap materials, respectively. Titanium dioxide is generally regarded as an indirect bandgap semiconductor and the energy (hv) and (αhv)2 can be used as coordinate axes to draw the forbidden bands diagram of titanium dioxide and titanium. Along the calculated curve was made a reverse tangent to the intersection of y = 0 as well the value obtained at the intersection points is the band gap value of titanium dioxide and titanium. As can be seen from Fig. 4(b and c), the band gap values of the pretreated titanium plates and the prepared titanium dioxide nanotubes are approximately 2.84 eV and 3.22 eV, respectively, which are correspond to the results of previous journal studies.[51]

The degradation performance of photoelectrodes

The degradation performance of TiO2 NWs photoelectrode in MFCs for azo dyes was evaluated by UV-vis spectrophotometer. The results of the spectral scanning results over time were shown in Fig. 5(a) by using photoelectrode to degrade the dye AR 30 solution under illumination. It is can be obviously inferred that the strength of the feature peak corresponding to the azo structure of the dye AR 30 gradually declines over time increases. The feature peak of the azo structure was performed to virtually disappear after 6 hours of degradation, which proves that the photoelectrode possess the well photocatalytic degradation performance of the azo dye AR 30 solution in microbial fuel cells.[52]

Fig. 5

(a) Photo images of AR 30 in the photodegradation; (b) degradation efficiency curve during open/closed circuit/light–dark conversion.

Fig. 5(b) illustrates the degradation degree of azo dye AR 30 by TiO2 NWs photocathode under different conditions of MFCs. From the curve, we can see that the photocatalytic degradation effect is different under various operating conditions. It can be shown from the degradation curve that the maximum degradation rate of MFCs were 52.95% and 78.1% under open circuit and turnover conditions, respectively. Meanwhile, the maximum degradation of the MFCs under light irradiation was 1.47 times stronger than in the darkness. The results show that the photocathode in MFCs has the highest degradation rate of dyes after 6 hours of ultraviolet irradiation, and the best decolorization performance was obtained. The main reason may be the enhancement of the decolorization of the dye by the light-induced electrons. It can be inferred that the TiO2 NWs photoelectrode under the excitation of ultraviolet light generated the electron–hole pairs, and then the free charge carriers were separated. In addition, the results of monitoring the degradation of azo dyes in the cathode compartment showed the TiO2 NWs electrodes under ultraviolet photoexcitation had a catalytic process to degrade the azo dye. Therefore, a relatively high degradation rate of MFCs can be achieved by this photocatalytic process, and the photogenerated holes (h+VB) of the electrode in the cathode chamber enhanced the reaction rate by the electrons (e−CB), the output voltage of MFCs were increased, as well as the internal resistance was decreased.

To more comprehensively examine the performance of TiO2 NWs, the comparison of polarization and power density (PD) curves in MFCs with photoelectrodes under light and dark was shown in Fig. 6(a). The results show that the maximum PD curves of the MFCs were 23.41 and 45.63 mW m−2, under light and dark condition, respectively. The maximum power density under light conditions was approximately twice that under dark conditions. It can be inferred that the catalytic efficiency of photoelectrodes substantially enhance in the light compared to the dark, and the further shows that light can be beneficial to increase the power production of the reactor. The instantaneous photocurrent response curve of the prepared photoelectrodes under ultraviolet irradiation was shown in Fig. 6(b). The curve showed that the photocurrent response with the TiO2 NWs sample was particularly obvious, and the test time interval between the light–dark transitions was 20 s. Usually, the separation capability of electrons and holes pairs is proportional to the photocurrent density, which has a significant effect on the improvement of photocatalytic activity. The stronger photocurrent response intensity of photoelectrodes was presented from the curve and the large local micro-regions may be the main reason, which has a positive effect on the separation/transmission of electrons and holes as well as further increases the production capacity of microbial fuel cells.

Fig. 6

(a) The power curve of MFCs with TiO2 photocathode under light and dark. (b) Transient photocurrent responses of MFCs with TiO2 NWs photocathode.

Due to the cleavage of the azo bond, the degradation product of AR 30 in MFCs was a reductive product, indicating that the photo-generated holes generated by the photoelectrode are directly consumed by the electrons from the anode. The generated photo-generated electrons and the excess electrons transferred from the anode participated in the process of organic reduction, realizing the bond breaking and decolorization of AR 30. Under aerobic conditions, O2 and AR 30 competed to become the electron acceptor. However, O2 had a higher redox potential and preferentially reacted with the electrons transferred from the anode, resulting in a higher cathode reduction potential and electricity generation performance. The strong oxidizing free radicals generated in the process affected the oxidative degradation of organic matter. The remaining electrons reacted with AR 30 to achieve reduction and decolorization.

Conclusion

In this research, the dye degradation and electricity generation were studied in MFCs by employing the prepared TiO2 nanowires photocathode. The charge transfer performance of prepared materials was evaluated through electrochemical measurement. The results showed that the photoelectrode exhibited high output voltage and low internal resistance in the reactor of MFCs under illumination. The anticorrosion of TiO2 NWs photoelectrode as the cathode contributed to the long-time operation (about 50 d) of MFCs in constant temperature incubator (25 ± 2 °C). The photocathode significantly promoted the separation of azo bonds and degradation of AR 30. The possible mechanism of the whole photocathodic MFCs could be explained as follows: under light irradiation, the photogenerated electrons of the cathode were released and reacted with the terminal electron acceptor, thus leaving the photogenerated holes as electron acceptors. These holes, combined with the electrons transferred from the anode, led to the accelerated reaction of cathode, the increased output voltage and the decreased internal resistance. Therefore, the photoelectrode in this study can be used as a safer and cleaner microbial fuel cell (MFCs) to treat dye wastewater and generate electricity at the same time in the future.

Conflicts of interest

There are no conflicts to declare.