Surface Roughness and Electrochemical Performance Properties of Biosynthesized α-MnO2/NiO-Based Polyaniline Ternary Composites as Efficient Catalysts in Microbial Fuel Cells

In this study, biosynthesized α-MnO2/NiO NPs and chemically oxidative polyaniline (PANI) were synthesized to form ternary composite anode material for MFC. The synthesized materials were characterized with different materials (UV-Vis, FTIR, XRD, TGA-DTA-DSC, SEM-EDX-Gwyddion, CV, and EIS) to deeply examine their optical, structural, morphological, thermal, roughness, and electrocatalytic properties. The degree of surface roughness for α-MnO2/NiO/PANI was 23:65 ± 5:652 nm. This value was higher than the pure α-MnO2, pure PANI, and even α-MnO2/PANI nanocomposite due to surface modification. The total charge storing performance for bare PGE, α-MnO2/PGE, PANI/PGE, α-MnO2/PANI/PGE, and α-MnO2/NiO/PANI/PGE were 5.291, 17.267, 20.659, 23.258, and 24.456mC. From this, the charge storing performance formed by α-MnO2/NiO/PANImodified PGE was highest, indicating that this electrode is best in cycle stability and increases its life cycle during energy conversion time in MFC. This is also supported by its effective surface area, having a value of 0.00984 cm. From this, it is evidenced that the ternary composite catalyst-modified anode facilitates the fast electrocatalytic activity as observed from its high peak current and lower peak-to-peak potential separation (ΔEp = 0:216V) than other electrodes. Such surface modification helps to store more electrical charge by increasing electrical conductivity during its charge/discharge processing time. In addition, the lower charge transfer resistance property with a value of 788.9 Ω and the fast heterogeneous electron transfer rate of ~2.92 s enable to facilitate glucose oxidation, and this enhances to produce high power output and increase wastewater treatment efficiency. As a result, the bioelectrical activity of α-MnO2/NiO/PANI composite-modified PGE was very effective in producing a maximum power density of 506.96mWm with COD of 81.92%. The above observations justified that αMnO2/NiO/PANI/PGE serves as an effective anode material in double-chambered MFC application.


Introduction
Focusing on alternative, renewable, and carbon-neutral energy sources produced by the bioelectrochemical system is necessary to keep the environment from pollution and economic sustainability across the globe [1]. Due to this, the microbial fuel cell (MFC) is chosen as the more affordable device that enables to produce renewable electrical energy followed by simultaneous wastewater treatment [1]. Therefore, the way to produce renewable energy from organic effluents and green treatments of liquid wastes has received much attention in MFC [2]. The device is able to produce renewable bioelectricity from stored chemicals found on organic pollutants in the presence of electroactive microorganisms (EAM) [3,4]. But the low power output, poor stability, and cost-ineffectiveness to upgrade the device are the main drawbacks that affect MFC [2]. This is due to the low electron transfer rate and low EAM attachment found on electrode components [5]. Electrodes from conventional carbon materials are the most common but are poor in energy conversion and low in wastewater treatment efficiency due to the short-term stability results for sluggish electron transfer rates between electrodes and EAM [6]. This limitation in general affects the whole performance of MFC.
To reduce these challenges, researchers have used transition metal oxide-(TMO-) based nanomaterial catalysts to modify such conventional carbon electrodes due to their low cost, environmentally friendly nature, abundance, high surface area to volume ratio, and fast electrokinetic activity in a widespread of electrochemical applications [7]. However, due to their poor electrical conductivity, poor dispersibility, and low stability in highly protonic media, they reduce their long-term electrocatalytic activity in bioenergy production (i.e., reduces the life cycle), bioremediation, and sensing activity [3,7]. Improving the electrochemical properties of TMO by forming a composite with conducting polymers enables to increase the life cycle of the modified electrode by improving its cycle stability in any energy conversion and storage applications. So, conducting polymers like PANI modify anodes by enhancing their electrical conductivity and surface areas when they form composites [8]. However, PANI lowers the electrochemical electrocatalytic activity and life cycle of the anode electrode in the MFC device under neutral conditions during its charge/discharge processing time. Not only this, the swelling and shrinkage behavior of PANI affects the physical strength of the bioanode while TMO NPs have a significant achievement to increase the cycle stability by increasing the specific capacitance of conventional carbon electrodes by forming composites under near-neutral and neutral solutions [9]. This is due to the finding of high theoretical capacitance on TMO and is considered a good option for anode modifier nanocatalysts when they form nanocomposites due to efficiency and stability improvement [10]. So, researchers usually combined different TMO with conducting polymers to modify conventional carbon material properties such as electrical conductivity, compatibility, and dispersibility [11][12][13]. As an advance, electrical conductivity, biocompatibility, high surface area, and surface roughness are the main requirement for bacterial attachment in MFC anodes [14]. So, when conventional carbon electrodes were modified with nanocomposite catalysts, their electrochemical catalytic property, durability, stability, and porosity requirements should successfully meet by improving the surface area. Such improvement facilitates fast extracellular electron transfer efficiency between EAM and anodes by forming a conductive immobilization matrix [15]. Immobilization of EAM helps to enhance the close contact between bacterial cells and electrode surfaces. So, the fabricated composite catalyst could act as a bridge to fasten electron movement across MFC. Simultaneously, the unique biocompatibility property of PANI could help to reduce extracellular electron transfer resistance in MFC [3], but this activity is restricted in the near-neutral and neutral media due to its swelling and shrinkage behavior [16].
To solve all limitations stated above and to be effective in MFC performance, some TMO NP-based hybrid composites which were synthesized by different methods were used as a good electrode modifier nanocatalyst. MnO 2 /polypyrrole [2,17], MnO 2 /PANI/MnO 2 [18], MnO 2 /polypyrrole/MnO 2 [19], and multiwalled carbon nanotubes/MnO 2 /polypyrrole [20] were studied. From those studies, their ease of synthesis was time-consuming; the use of expensive chemicals with environmentally intolerable solvents that might affect environmental safety, use of expensive synthesis instruments, lower efficiency in wastewater treatment and power output, and inefficient charge storing ability give the intention to extend this work on biosynthesized α-MnO 2 /NiO-integrated conductive PANI ternary composites for MFC applications. The synthesis of α-MnO 2 /NiO binary hybrids which were dispersed in the PANI matrix followed the green method. This was cost-effective and could enable to reduce expensive and toxic reducing chemical constituents because the plant extracts are an effective reducing and stabilizing agent to synthesize TMO-based nanomaterials. Therefore, finding a simple, cost-effective, and environmentally friendly green method is one of the core objectives of this study.
So, in this study, α-MnO 2 /NiO/PANI ternary nanocomposites were prepared by integrating the green method with cost-effective biosynthesized α-MnO 2 /NiO in a conductive PANI matrix. Hydrothermal, solvothermal, electrodeposition, electropolymerization, microwave-assisted, and pyrolysis methods were time-consuming and used expensive advanced instruments. Previously, we prepared Mn-Ni oxide bimetallic NPs by following the simple green method by using Vernonia amygdalina leaf extract as a reducing and stabilizing agent [21]. To be an effective nanocatalyst towards bioelectricity and its simultaneous waste remediation, the catalyst should be best in roughness degree and be efficient in electrocatalytic activities that enable to increase anode electrode performance for effective organic wastewater oxidation (i.e., facilitating substrate oxidation). Therefore, the combined α-MnO 2 /NiO/PANI nanocomposite has the best surface roughness with efficient electrochemical properties than other catalysts. This was clearly modified to a conventional pencil graphite electrode (PGE) evidenced from double-chambered MFC construction.

Material
Synthesis. An optimized α-MnO 2 /NiO binary composite was prepared based on our previous method [21]. In detail, an aqueous nickel ion concentration of 51% (v/v) to KMnO 4 was added in a round-bottom flask which was placed on a controlled hot plate at a fixed temperature of 80°C and fixed pH~8 with continuous stirring. After 15 minutes,~75% (v/v) of V. amygdalina leaf extract was added dropwise in the given mixture. The reaction mixture was then waited for~25 minutes of stirring. Due to these, the speed of the stirrer was reduced due to thick dark brown precipitate formation. The obtained precipitate was centrifuged at 4000 rpm for 15 minutes. Recovered precipitates 2 Journal of Nanomaterials were washed several times with distilled water and absolute ethanol to remove organic contaminants. The 4-hour hot air oven-dried precipitate was calcined at 450°C for 2 hours to give α-MnO 2 /NiO bimetallic NPs. For the biosynthesized α-MnO 2 NP preparation, refer to our previous work [22]. PANI was polymerized chemically based on the literature [23] as follows. Firstly, 1 M aqueous HCl solution was mixed with 0.5 mL aniline in a round-bottom flask and stirred for 30 minutes. Secondly, 5.71 g of ammonium persulfate (APS) was dissolved in 50 mL distilled water and kept for 1 hour each. Finally, two solutions were mixed and stirred at room temperature until a dark green precipitate was formed and waited for 4 hours to polymerize. The final precipitate was washed with 0.2 M HCl solution until the filtrate becomes clear, then with ethanol to remove the monomer and oligomer and with distilled water to remove the remaining acid. The final powder was then dried in an oven at 60°C for 24 hours.
A typical in situ oxidative polymerization method was used to synthesize α-MnO 2 /PANI binary nanocomposites by using the literature with little modification [11]. In brief, 0.5 mL aniline was dissolved in 100 mL of 1 M HCl by using a glass round-bottom flask. The mixture was waited for 30 minutes, followed by stirring. Then, 0.5 g of optimized biosynthesized α-MnO 2 NPs [22] was dispersed in 25 mL distilled water, and the mixture was exposed for 5 minutes of ultrasonication to disperse the biosynthesized material. Finally, the dispersed α-MnO 2 NPs were added dropwise to aniline hydrochloride solution with 2.86 g of 50 mL APS (oxidant and codopant) at room temperature and stirred for 4 hours to complete the polymerization. The mixture changed in color, and the obtained precipitate was collected and washed with 0.2 M HCl solution until the filtrate becomes clear, then with ethanol to remove the monomer and oligomer as well as with distilled water to remove the remaining acid. Finally, the product was dried in an oven at 60°C for 24 hours to give α-MnO 2 /PANI nanocomposites.
A typical in situ chemical oxidative method was used to prepare α-MnO 2 /NiO/PANI ternary composites based on the literature with little modification [11]. Briefly, 0.5 g of homogenously suspended α-MnO 2 /NiO bimetallic NPs was dispersed in aniline hydrochloride aqueous solution (0:1 M aniline + 1 M HCl ðdopantÞ + 1:43 g of 50 mL APS ðcodopantÞ). The mixture was stirred continuously for 4 hours to complete the polymerization reaction. The final deep dark green precipitate was then collected by filtration and washed with 0.2 M HCl solution until the filtrate becomes clear, then with ethanol several times to remove the monomer and oligomer as well as with distilled water several times to remove the acid. Finally, the product was dried in an oven at 60°C for 24 hours to give α-MnO 2 /NiO/PANI nanocomposites.

Electrode Fabrication.
Catalyst-modified electrodes were carried out by following the literature [24] as follows. Briefly, α-MnO 2 , PANI, α-MnO 2 /PANI, and α-MnO 2 /NiO/PANI were dispersed with polyvinyl alcohol (PVOH, MW = 44:05 g mol −1 ) polymer binder solution in the ratio of 1 : 5 (PVOH to NPs, wt/wt%). Before coating, the mixture was stirred for 1 hour at 70°C to disperse uniformly. Finally, a 100 μL of uniformly distributed suspension was coated on the PGE surface using the drop-cast method with the help of a microsyringe [25]. To improve its interface stability and bonding force, the modified electrode was oven-dried at 60°C for 12 hours [26]. Bare PGE (1 cm in length and 0.2 cm in diameter) was prepared by soaking in distilled water for 24 hours and rinsed with 0.2 M phosphate-buffered solution (PBS) [27].

Characterization
Techniques. UV-Vis (Azzota SM-1600 SPECTROPHOTOMETER, USA) was used to observe both the maximum wavelength and the absorption spectrum in the wavelength range of 200 nm-800 nm.
The existence of metal-nonmetal functional groups was monitored using Fourier transform infrared (FTIR) spectra with a PerkinElmer FT-IR BX spectrophotometer in the range of 4000-400 cm -1 with samples prepared using KBr pellets.
The structural elucidation was examined with powder Xray diffraction (XRD-7000, Shimadzu, Japan) with a voltage of 40 kV and a current of 30 mA using a Cu Kα X-ray radiation source (1.5406 Å) in the 2θ range of 10°-80°.
The surface morphology and elemental composition were investigated using scanning electron microscopyenergy-dispersive X-ray analysis (SEM-EDX, JEOL Ltd. instrument with a model of JCM-6000Plus).
Electrochemical measurements were carried out with a three-electrode electrochemical workstation (Biologic SP-300, Canada) containing bare/modified PGE, Ag/AgCl, and Pt wire as the working, reference, and counter electrodes, respectively. Electrochemical impedance spectroscopy (EIS) was measured in the frequency range of 200 kHz-10 MHz at AC perturbation of 10 mV. The cyclic voltammetry (CV) was also measured in the potential window between -0.8 V and +0.8 V at a scan rate of 50 mV s -1 . All the measurements were carried out in 100 mM phosphate-buffered electrolyte solution (pH = 7:4). EC-Lab v10.36 software was used for fitting both the cyclic voltammogram and the EIS spectrum.

MFC Setup and Operation.
To show the bioelectrocatalytic catalytic activities of ternary composites compared with bare PGE, a double-chamber MFC setup was constructed from two equal glass Büchner flasks connected with a glass tube (9 cm in length and 1.1 cm in diameter) which acts as a salt bridge filled with 12 g of KCl and 3 g agar shown in Figure 1. Unmodified PGE and modified PGE with the α-MnO 2 /NiO/PANI ternary composite catalyst were used as an anode while bare PGE was used as a cathode. The anode bioreactor was prepared from measurable artificial wastewater containing 160 mg L -1 of glucose substrate, 5840 mg L -1 of NaCl, 100 mg L -1 of KCl, 250 mg L -1 of NH 4 Cl, 12,000 mg L -1 of Na 2 HPO 4 ·12H 2 O, 2570 mg L -1 of NaH 2 PO 4 ·2H 2 O, 840 3 Journal of Nanomaterials mg L -1 of MgCl 2 ·6H 2 O, 500 mg L -1 of FeCl 3 , 2 mg L -1 of MnSO 4 ·H 2 O, 5 mg L -1 of CaCl 2 , and 340 mg L -1 of yeast extract to fulfill the micronutrient deficiency [28]. The anode was inoculated with E. coli cultured from wastewater effluents collected from the Adama Science and Technology University wastewater treatment plant, Adama, Ethiopia (latitude 8°33′43.56″ north and longitude 39°17′23.28″ east), using a sterile glass bottle tied up with a lightweight steel round stick. The anode chamber was kept airtight and filled completely with 160 mg L -1 of glucose substrate as a carbon source with inoculum added to achieve anaerobic conditions [29]. The cathode chamber was filled with 50 mM KMnO 4 which was dissolved in a neutral medium (100 mM, pH 7.40) PBS.

Power Measurement.
The open-circuit voltage (OCV) and closed-circuit voltage (CCV) were monitored for 3 hours/day after 5 minutes of stabilization for every 5minute continuous interval using a digital multimeter (DT830D, Haoyue, China). The polarization determination was monitored from CCV against external resistors for a 15-minute time interval using the Decade Resistance Box (ANSHUMAN, Model: DRB-7T) by varying an external resistance from 10 kΩ to 200 Ω. The current flow across each resistor was determined by using Ohm's law: I = V/R and P = IV, where P is power, I is current, and V is measured voltage. Similarly, the current (J) and power (P) densities were calculated from the ratio of current and power to surface area (A) of the anode, respectively.

COD Removal and CE Measurement.
To measure the chemical oxygen demand (COD) and coulombic efficiency (CE), the following formulas would help to explain degradation efficiency [30]: where COD in (mg L -1 ) is the influent COD and COD out (mg L -1 ) is the effluent COD. The coulombic efficiency (CE) was measured as the ratio between the electrons transferred to the anode from the microorganism to the theoretical one that can be achieved if all organic substrates were digested by the microorganisms to generate electrons. Therefore, the CE can be calculated for batch reactor conditions as follows [30]: where M is the oxygen molecular weight (32), I is the current, and t is the time at the maximum power density. F is Faraday's constant, b = 4 indicates the number of electrons exchanged per mole of oxygen, V an is the anodic solution volume, and ΔCOD is the change in chemical oxygen demand after time t.

Results and Discussions
3.1. UV-Vis Analysis. The UV-Vis spectra of α-MnO 2 and PANI as well as α-MnO 2 /PANI and α-MnO 2 /NiO/PANI nanocomposites are given in Figure 2. In pure α-MnO 2 , the absorption peak observed at about 285 nm might be an electronic transition from the O 2p valence band to the Mn 3d conduction band or from the triply degenerate (t 2g ) valence band to the doubly degenerate conduction band (e g ) if the shape is purely tetrahedral, as shown in Figure 2(a) [22]. The absorption peak for PANI found at about 267 nm and near 405 nm indicated π → π * transitions of the benzenoid ring and polaron → π * transitions, respectively, as shown in  [31]. The shift to a higher wavelength in the α-MnO 2 /PANI nanocomposite than pure PANI is attributed to the chemical interactions between α-MnO 2 NPs and the quinoid ring of the PANI backbone (see Figure 2(c)) [13].
In the case of α-MnO 2 /NiO/PANI nanocomposites shown in Figure 2(d), a blueshift (below 300 nm) with a maximum absorption peak in the near-visible region (300 nm-400 nm) than pure PANI and α-MnO 2 /PANI may indicate the decreasing polaron path during PANI conjugation due to the loading of α-MnO 2 /NiO NPs in the conductive PANI matrix. According to Mohammad Shafiee et al. [23], a blueshift found on the UV region might be a strong interaction between metal oxide d orbitals and π orbitals found in the polymeric material. So, the significant redshift above 300 nm in the α-MnO 2 /NiO/PANI nanocomposite supports its improvements in electrical conductivity due to the polaron movement across the extended conjugation [32].

FTIR Analysis.
The FTIR spectra of the pure NPs and their nanocomposites are shown in Figure 3. The spectra shown in Figure 3(a) demonstrated that characteristic peaks found at 3422, 3304, 596, and 495 cm -1 are attributed to -OH surface water stretching, H-O-H bending, O-Mn-O stretching collision, and Mn-O bond stretching vibrations, respectively [22]. The bands found at 3448, 2924, 1636, 1445, 1098, and 969 cm -1 showed N-H stretching, aromatic C-H stretching, quinoid ring stretching vibration, and benzenoid ring vibrations, respectively, as indicated in Figure 3(b) [33]. The reduction in peak intensity of PANI found in α-MnO 2 /PANI and the reduction in peak intensity at about 1098 cm -1 and 969 cm -1 as well as a new peak appearing at about 508 cm -1 with better peak intensity than pure PANI indicate the clear transformation of PANI in the nanocomposite (see Figure 3(c)). Moreover, an intense peak found at about 1094 cm -1 and 511 cm -1 illustrates the successful NiO interfaced in the MnO 2 /PANI binary nanocomposite system, as shown in Figure 3(d).
3.3. XRD Analysis. The XRD patterns of pure α-MnO 2 and PANI as well as α-MnO 2 /PANI and α-MnO 2 /NiO/PANI nanocomposites are shown in Figure 4. Figure 4(a) describes the spectrum of α-MnO 2 which has three intense characteristics at 2θ = 12:479°, 25.228°, and 37.218°, which are attributed to the diffraction planes found at (110), (220), and (211), respectively, which were indexed with the standard XRD pattern of α-MnO 2 (Crystallography Open Database (COD), Entry # 96-151-4117 (space group: I4/m (87))) with pure tetragonal phase and lattice parameters containing a = 9:78760 Å and c = 2:86500 Å [22]. The XRD pattern shown in Figure 4(b) showed two broad characteristic peaks found at 2θ = 20:494°and 25.413°, which are indexed to diffraction planes at (100) and (110), respectively, due to the characteristic chain of PANI [34]. For the α-MnO 2 /PANI nanocomposite, its diffraction peaks are almost similar to those of pure PANI in all planes except changes that occurred at 2θ = 21:151°indexed at (100) (Figure 4(c)). The better peak symmetry on α-MnO 2 /PANI than pure PANI showed that the presence of α-MnO 2 NPs results in its crystal structure distortion during the polymerization reaction. The spectrum of the α-MnO 2 /NiO/PANI nanocomposite is similar to that   Journal of Nanomaterials of the α-MnO 2 /PANI nanocomposite, as shown in Figure 4(d). The peak at 2θ = 21:151°and 25.413°may be attributed to the interaction of α-MnO 2 insertion in PANI while the intense broad peak at 14.208°and 25.684°indexed at (101) and (110) planes is due to the incorporation of NiO NPs in the conductive PANI matrix. The proof was identified and indexed from the standard XRD pattern of NiO (COD, Entry # 96-432-9324 from Match! 3 phase identification software) and in good agreement with the literature [35]. The overall crystallite size and d-spacing are summarized in Table 1. 3.4. Thermal Analysis. The thermal stability of pure α-MnO 2 and PANI nanomaterials as well as α-MnO 2 /PANI and α-MnO 2 /NiO/PANI nanocomposites was examined. Figure 5(a) (i) shows that at the temperature of 146.13°C, the weight loss amounted to be -5.024%, which can be reasonably attributed to existing water removal from the surface and lattice of the nanostructure, while the weight loss of -8.381% found at a temperature of 888.16°C might be the phase transformation of α-MnO 2 to Mn 2 O 3 [36]. In Figure 5(a) (ii-iv), PANI, α-MnO 2 /PANI, and α-MnO 2 /-NiO/PANI materials followed a similar weight loss pattern in the four major stages of weight loss. The first two stages of weight loss up to 150°C were attributed to the loss of vol-atile impurities and surface adsorbed water. The weight loss from 150°C to 500°C might be assigned to the removal of higher oligomers and other remaining residuals [37]. The presence of subsequent weight loss found on the PANI and nanocomposites is due to the thermooxidative decomposition of the PANI chain in the temperature range of 500°C-915°C [37].
The DTA curve shown in Figure 5(b) (i) revealed that α-MnO 2 has two endothermic peaks with more stability property, but the curve shown in Figure 5(b) (ii) attributed to the exothermic decomposition of PANI at a temperature of 210.46°C and 524.31°C is due to the different oxidation products [38]. Finally, the DTA curves shown in Figure 5(b) (iii and iv) that peak at 503.44°C and 467.70°C are for α-MnO 2 /-PANI and α-MnO 2 /NiO/PANI, respectively. This revealed that α-MnO 2 and α-MnO 2 /NiO have a clear interaction with PANI and increase stabilization. The lower temperature peak existence on both composites than pure PANI is due to the fast loss of different products from the polymer decomposition [39]. The summarized weight loss and peak analysis steps are given in Tables 2 and 3. 3.5. SEM-EDX Analysis. Figure 6(a) shows the SEM micrographs of the as-prepared α-MnO 2 nanoparticles with ballshaped flower-like architecture. Figure 6(b) shows the nonuniform, rough, and closely packed irregular granular micrographs for pure PANI. The clear distribution of α-MnO 2 nanoparticles over granular PANI is shown in Figure 6(c). The surface modification and binary composite formations clearly contribute to the better surface size distribution image of α-MnO 2 /NiO/PANI (Figure 6(d)). The incorporation of MnO 2 and NiO nanoparticles has changed the granular structure of PANI into a more ball-like spherical structure. The elemental composition of this ternary composite contains Mn, Ni, C, O, and codopant elements (S and Cl) with K traces (see Figure 6(e)). The excess of chlorine resulted from its adsorption on the surface of the salt or was trapped in this salt as anilinium chloride (emeraldine salt) during the reaction procedure [40]. The presence of sulfur which originated from APS on the synthesized material improves the electrocatalytic activity on the bare anode [41]. It is noted that the detection of elements using EDX is below 0.01 wt% [42]. So, in this investigation, the element nitrogen is not detected on the spectrum. At low energy resolution, peak overlap may occur between the nitrogen and the polyaniline carbon signal. To prevent this, some researchers have used a high-energy resolution instrument [43].  Journal of Nanomaterials 3.6. Surface Roughness. Nanomaterial surface roughness physical performance analyses have a significant impact on various electrochemical applications [44]. Hence, the surface topography loaded from SEM images of α-MnO 2 , PANI, and their nanocomposites was analyzed using Gwyddion software, as shown in Figure 7. The degree of surface roughness that arises from its parameters quantifies the direct pore occurrence from 2D (Figure 7(a1, b1, c1, and d1)) and 3D   Journal of Nanomaterials ( Figure 7(a2, b2, c2, and d2)) maps. These quantified parameters are mean roughness (R a ), mean square roughness (R q ), surface skewness (R sk ), and kurtosis coefficient (R ku ) [45]. So, from this study, all representative parameters were examined by the row statistical analysis approach shown in Table 4. The R a value of the α-MnO 2 /NiO/PANI nanocomposite was 23:65 ± 5:652 nm. This value was higher than α-MnO 2 and PANI, and even the α-MnO 2 /PANI nanocomposite has a lowerR a value. This shows that α-MnO 2 /NiO/PANI has a better rough surface than others which is a clear indication for its best surface area and reactive surface site [46]. The same principle is also proved from its R q (28:55 ± 5:617 nm ) values, indicating the degree of surface roughness variation is much higher than others. The R sk of α-MnO 2 /NiO/PANI nanocomposites shows a higher positive value than other prepared materials. The higher positive value indicated that there are more troughs (regions of positive curvature) than peaks on the surface. The R ku value of the α-MnO 2 /NiO/-PANI nanocomposite was −0:7148 ± 0:566. The results show that the pore size distribution of the α-MnO 2 /NiO/PANI nanocomposite is more scattered (i.e., the pore size distribution is not compact or more concentrated) than other nanomaterials. Therefore, from all parametric information, we conclude that α-MnO 2 and NiO nanomaterials are successfully incorporated in the conductive PANI matrix. Such dispersion enhances the mechanical properties [47] and thermal stability of the nanocomposites which was supported by the thermal analysis. Not only these, the addition of the above metal oxides on the polymer matrix led to increased surface roughness and increased multifunctionality by forming hierarchical shapes of the materials [48]. For comparison, all parameters are given in Table 4.

Electrochemical Property.
In order to evaluate the electrochemical performances of unmodified and modified electrodes, CVs were performed under phosphate-buffered electrolyte solution, as shown in Figure 8. A pair of quasireversible redox peaks was dominated on the nanocomposite-modified electrode from the best fit line of I p versus v 1/2 . The reversibility of these peaks suggests that the fabricated nanocomposite does not decompose during the charge transfer mechanism, and this helps for fast electron transfer ability. A pair of weak redox peaks was observed at bare PGE with anodic (I pa ) and cathodic peak current (I pc ) values of 0.735 mA and 4.379 mA, respectively, which was lower than other electrodes, as shown in Figure 8(a). After modification, the peak current observed by PGE was 2.685 mA and 6.079 mA for I pa and I pc , respectively. The bare electrode modified by the α-MnO 2 /NiO/PANI nanocomposite was increased by 3-fold anodic peak current than unmodified PGE. The rest of the peak currents determined by α-MnO 2 , PANI, and α-MnO 2 /PANI-modified PGE are given in Table 5. The increase in peak current in all modified electrodes indicated the better electrocatalytic activity of α-MnO 2 NP interaction in the PANI matrix and good attribution of the nanocomposite on the PGE surface. So, the anodic peak current was found to be higher in α-MnO 2 /NiO/PA-NI/PGE (2.685 mA at a potential of -0.573 V) than the other modified electrodes including bare PGE. This suggests that dispersion of α-MnO 2 /NiO bimetallics in the PANI matrix modified the surface activity of PGE and changes its anodic peak potential. This activity extends to increase the total charge storing performance in the order of α-MnO 2 /NiO/-PANI/PGE>α-MnO 2 /PANI/PGE>PANI/PGE>α-MnO 2 /P-GE>PGE anode electrode, as shown in Figure 8(b). This order facilitates a conductive anode formation. It indicated that α-MnO 2 /NiO/PANI/PGE exhibited a fast electron transfer rate that enables to increase electrical conductivity due to having lower peak-to-peak potential separation (ΔE p = 0:216 V) than other electrodes. The effective surface area (effective electroactive area) of the electrode is the main factor which affects the electrocatalytic performance activities. So, to determine this area, the equation proposed by Randles-Sevčik was followed [7]:    Journal of Nanomaterials where M stands for catalysts such as PGE, α-MnO 2 , PANI, α-MnO 2 /PANI, and α-MnO 2 /NiO/PANI. As observed from the CV result, α-MnO 2 /NiO/PANI nanocomposite-modified PGE was the best electrode among the rest. Therefore, the effect of the scan rate on the cyclic voltammetric performance of α-MnO 2 /NiO/PANI/PGE is shown in Figure 9(a) at the scan rates (5-200 m Vs -1 ). The responses of both I pa and I pc currents gradually increase with increasing scan rates along with oxidation and reduction peak potentials that shift to the right and left, respectively. Figure 9(b) justifies the linear dependence of both I pa and I pc versus the square root of the scan rate with linear regression equations of I pa = 0:30405v 1/2 + 0:29912 (R 2 = 0:97) and I pc = −0:63452v 1/2 − 1:1702 (R 2 = 0:98). The dependence of peak potentials (E pa and E pc ) against the scan rate is also shown in Figure 9(c). Hence, we imply that the nature of the redox process occurring on the electrode surface is nearly    [20] and is clearly a diffusioncontrolled process [51]. The anodic peak potential (E pa ) was highly correlated with the natural logarithm of the scan rate (ln v) for α-MnO 2 /NiO/PANI/PGE in PBS (pH = 7:4) (Figure 9(d)). To evaluate the electrochemical parameters from such linearity, the Laviron equation was applied as follows [52]: where E o is the formal potential (E pa + E pc /2), α is the charge transfer coefficient of the system, v is the scan rate, n is the number of electron transfer, R is the universal gas constant (8.314 J mol -1 K -1 ), T = 298 K, F = 96,493 C mol −1 , and k s is the heterogeneous electron transfer rate constant. From the slope of E pa vs. ln v, α = 0:51. So, if α is closer to 0.5, the electrode reaction is quasi-reversible and governed by the diffusion-controlled process [53]. The Laviron equation [54] was applied to calculate k s for each electrode as well as electron transfer at each scan rate: The calculated k s value of α-MnO 2 /NiO/PANI/PGE at constant scan rates of 50 mV s -1 was higher than the rest of

12
Journal of Nanomaterials the electrode, and this indicated that the α-MnO 2 /NiO/PANI nanocomposite is a good facilitator for direct electron transfer between electroactive species and bare PGE (see Table 6).
The direct dependence of k s over peak potential is also given in Table 7.
EIS is an efficient technique to estimate electron transfer properties between electrode surfaces and electrolyte interfaces during redox reactions [52]. The Nyquist plot shown in Figure 10(a) describes that both the α-MnO 2 /PANI and α-MnO 2 /NiO/PANI composite-modified electrodes have lower solution and charge transfer resistances (R s and R ct ) in the high-frequency regions due to their electrical conductivity improvement. The R s was determined from a higher frequency intercept on the real axis. The value was in the range of 8.86-9.26 Ω for α-MnO 2 /PANI and α-MnO 2 /NiO/-PANI composite-modified electrodes. The R ct values of the α-MnO 2 /NiO/PANI-modified PGE (788.9 Ω) and α-MnO 2 /-PANI/PGE (958 Ω) were lower than that of unmodified PGE (1519 Ω), indicating that the modified anode surface had improved its electrocatalytic activity and surface roughness modification which is responsible for conductive biofilm attachment and EAM growth. The same behavior is also observed from bode plots of frequency-dependent impedance magnitude (log | Z | ) (Figure 10(b)). Their diffusion resistance (Z w ) found in the lower frequency region is also lower than pure α-MnO 2 and PANI-modified PGE (see Table 8). The lower diffusion resistance found on the composite-modified PGE showed that the electrode could have a capacitive characteristic due to the finding of phase angles found in the range between -45°and -90°with frequency lower than 100 Hz, as shown in Table 8 and Figure 10(c). Since the capacitive behavior is governed for all electrodes in this phase angle range, and this also suggests their good redox behavior. In the frequency range of 100 Hz-104 Hz, the phase angles decrease rapidly and are close to zero, indicating less electrolyte ion adsorption on electrode surfaces, and resistive behavior is dominated [55]. From this, it is evidenced that the current generation signal in the given time is much better than bare PGE (Figure 10(d)). In Figure 10(e), as the number of cycles increases, the stable current production by α-MnO 2 /NiO/PANI ternary compositemodified PGE becomes higher in efficiency than that by α-MnO 2 /PANI binary composite-modified PGE due to the long life cycle, high metallic conductivity, and fast charge/discharge mechanism nature of NiO NMs [56].

MFC Application.
At steady-state conditions, the catalytic activity investigations of composite-modified electrodes under steady-state conditions are shown in Figure 11. The highest open-circuit voltage (OCV) elucidated by α-MnO 2 /-NiO/PANI/PGE was 616:72 ± 56:65 mV which was higher than bare PGE with values of 222:36 ± 8:16 mV. A total of 180-minute measurements per day were operated for each electrode (Figure 11(a)). On the second day, the 3-hour measurement was the better time to perform MFC using α-MnO 2 /NiO/PANI/PGE than unmodified PGE. From these continuous operations, the higher OCV determination throughout the day using α-MnO 2 /NiO/PANI ternary composite-modified PGE was due to the effective adhesion between the E. coli colony and the α-MnO 2 /NiO/PANI catalyst ( Figure 11(b)); these may also be attributed to high charge density capacity after forming the bioanode. These interactions cause increasing conductive biofilm formation by increasing its active surface area on the electrode surfaces which leads to improved fast electron transfer rates on the anode surface in the MFC operation. Each day, OCV values produced by two electrodes are given in Table 9. So, the prepared ternary composite is considered an effective catalyst to increase MFC performances under steady-state conditions.
At non-steady-state conditions, the electrocatalytic activity of α-MnO 2 /NiO/PANI composite-modified PGE and unmodified PGE MFC performance tests is given in Figure 12(a). The mean maximum power density of 506.96 mW m -2 was delivered with α-MnO 2 /NiO/PANI composite-modified PGE while 65.74 mW m -2 was obtained using bare PGE. The current density formed at this maximum power density was 2710.51 and 436.52 mA m -2 for α-MnO 2 /NiO/PANI/PGE and PGE, respectively. The capacity of composite-modified electrodes was 7.71 and 6.21 times higher in power and current densities than that of unmodified PGE. The calculated internal resistance obtained from slopes of measured voltage versus current density [57] was 1183.29 Ω and 3745.74 Ω for α-MnO 2 /NiO/PANI/PGE (R 2 = 0:97916) and PGE (R 2 = 0:98858), respectively. An increase in surface areas lowers the internal resistance found on the modified electrodes, indicating fast extracellular electron transfer between the E. coli and the bioanode. The good electron transfer between π orbitals of PANI and d orbitals of Mn 4+ -Ni 2+ enables the α-MnO 2 /NiO/PANI composite to be effective in power density during glucose oxidation in the given time of operations (Figure 12(b)). Thus, the charge   14 Journal of Nanomaterials storage capacity from current discharge as a function of time in the given areas of electrodes was much higher in modified electrodes than bare PGE (see Figure 12(c)). The flow of free charge hindered using bare PGE might arise due to its highest internal resistance found from the polarization curve. This proved that the higher electrical conductivity elucidated from electrochemical performance analysis showed that α-MnO 2 /-NiO/PANI/PGE produces a higher power output at a lower external load (Figure 12(d)). Hence, the area under time-dependent current at higher external resistance becomes too low due to the continuous charge loss from glucose decomposition. Therefore, the good integration between bimetallic oxides with conductive PANI enhances MFC performance.
3.9. Bioanode Morphology Analysis. The surface morphology of the anode surface is shown in Figure 13. Before MFC operation, an irregular (with flakes in shape) rough surface Electrode    Figure 13(a). The roughness of this surface is attributed to the granularity of the conductive materials [58]. After PGE is immersed in the anode bioreactor, the surface morphology of PGE is clearly covered by small colonies of E. coli which forms a biofilm due to the little hydrophilicity nature of bare PGE, as shown in Figure 13(b). However, such adherence of E. coli on the PGE surface was ineffective for power generation during MFC operations. This is due to the poor capacitive and little substrate degradation activity of carbon electrode materials in MFC performance [10]. So, to solve these limitations, bare PGE was successfully modified with α-MnO 2 /NiO/PANI ternary composites. As shown in Figure 13(c), the integration between α-MnO 2 /NiO binary composites in the conductive PANI matrix exhibited a higher bacterial colony. It is observed that the distribution of bimetallic oxide with positively charged PANI enhances the glucose electrochemical reactions. Such reaction was enabled to facilitate better power production than bare PGE, as described from the MFC test analysis. This is due to the formation of thick conductive biofilm as evidenced from the high-magnification surface topography view, as shown in Figures 13(d) and 13(e). From this magnified image, E. coli cells are tightly attached to the modified anode surface to form the bioanode electrode. Xu et al. [59] have reported that when a bare carbon electrode is modified by conductive composites from PANI, its surface roughness and biocompatibility are increased, which makes it more comfortable for more biofilms to attach, helping it  16 Journal of Nanomaterials become more conductive [59]. Finally, this enabled the creation of a direct electron transfer improvement between E. coli outer membrane c-type cytochromes and α-MnO 2 /NiO/-PANI/PGE for better MFC performance operation.
3.10. COD Removal and CE Performance. In addition to generating electricity, treating glucose-based artificial wastewater using bare PGE and α-MnO 2 /NiO/PANI-modified PGE is shown in Figures 14(a) and 14(b). It is observed that the higher glucose degradation performance was performed with a lower concentration and higher removal efficiency of 30.37 mg L -1 and 81.92%, respectively, using α-MnO 2 /NiO/PA-NI/PGE. Degradation efficiency using bare PGE was too low due to the slower glucose biodegradation rate, indicating less COD removal efficiency over a given time period. Thus, electron transfer from decomposed glucose to the bare anode is too slow while faster in α-MnO 2 /NiO/PANI ternary composite-modified PGE due to their surface modification.
To support this, the degree (fraction) of electrons produced from glucose to modified PGE was higher in terms of CE with 17 Journal of Nanomaterials a value of 10.30% while PGE alone has a small CE value of 2.29%, as shown in Figure 14(b) and Table 10. The faster electron transfer using ternary composite-modified PGE was also effective in bioelectricity generation conversion during the time of treatment at the same conditions. Literature survey described that the lower CE values have indicated that a portion of electrons extracted from substrates are used for the biosynthesis of cellular compounds, not for complete bioelectricity production, whereas higher CE would indicate the dominance of bioelectricity conversion rather than for biosynthesis [60].

Conclusion
α-MnO 2 /NiO/PANI ternary composites are prepared by dispersing the optimized biosynthesized α-MnO 2 /NiO bimetallic NPs in the conductive PANI matrix using the in situ chemical polymerization method. The prepared ternary composites showed to be best in the degree of roughness and charge storing performances with a value of 23:65 ± 5:652 nm and 24.456 mC. This property clearly increases the biocompatibility, electrical conductivity, and life cycle of the anode in MFC by improving its performance towards a maximum power density of 506.96 mW m -2 with a COD removal of 81.92%. The power density produced by the α-MnO 2 /NiO/PANI ternary composite-modified anode is better in efficiency than power output which was done by biosynthesized α-MnO 2 /NiO bimetallic NPs with a mean value of 412.24 mW m -2 [21]. The CE produced by the α-MnO 2 /-NiO/PANI/PGE ternary composite was 10.30% which was almost 5-fold better than bare PGE with a value of 2.29%. Therefore, this study contributes to advances in the use of biosynthesized α-MnO 2 /NiO-based PANI ternary composites as an emerging cost-effective catalyst for anode modifier catalysts in energy conversion and simultaneous wastewater treatment application in MFC.

Data Availability
Data are available in the manuscript.

Conflicts of Interest
The authors declare no conflict of interest in this paper.

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Journal of Nanomaterials