<?xml version="1.0" encoding="UTF-8"?><!DOCTYPE article  PUBLIC "-//NLM//DTD Journal Publishing DTD v3.0 20080202//EN" "http://dtd.nlm.nih.gov/publishing/3.0/journalpublishing3.dtd"><article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" dtd-version="3.0" xml:lang="en" article-type="research article"><front><journal-meta><journal-id journal-id-type="publisher-id">JMMCE</journal-id><journal-title-group><journal-title>Journal of Minerals and Materials Characterization and Engineering</journal-title></journal-title-group><issn pub-type="epub">2327-4077</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/jmmce.2021.95030</article-id><article-id pub-id-type="publisher-id">JMMCE-111658</article-id><article-categories><subj-group subj-group-type="heading"><subject>Articles</subject></subj-group><subj-group subj-group-type="Discipline-v2"><subject>Chemistry&amp;Materials Science</subject><subject> Engineering</subject></subj-group></article-categories><title-group><article-title>
 
 
  Synthesis of Bi&lt;sub&gt;2&lt;/sub&gt;Fe&lt;sub&gt;4&lt;/sub&gt;O&lt;sub&gt;9 &lt;/sub&gt;Crystalline Ceramic as Extremely Capable Photocatalyst via Proficient Chemical Route
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Manish</surname><given-names>Kumar Verma</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Vinod</surname><given-names>Kumar</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Tapas</surname><given-names>Das</given-names></name><xref ref-type="aff" rid="aff2"><sup>2</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Ravi</surname><given-names>Kumar Sonwani</given-names></name><xref ref-type="aff" rid="aff2"><sup>2</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Vishnu</surname><given-names>Shankar Rai</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Dinesh</surname><given-names>Prajapati</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Kedar</surname><given-names>Sahoo</given-names></name><xref ref-type="aff" rid="aff2"><sup>2</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Vishal</surname><given-names>Kumar Kushwaha</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Asha</surname><given-names>Gupta</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Kamdeo</surname><given-names>Mandal</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib></contrib-group><aff id="aff2"><addr-line>Department of Chemical Engineering, Indian Institute of Technology (Banaras Hindu University), Varanasi, India</addr-line></aff><aff id="aff1"><addr-line>Department of Chemistry, Indian Institute of Technology (Banaras Hindu University), Varanasi, India</addr-line></aff><pub-date pub-type="epub"><day>26</day><month>08</month><year>2021</year></pub-date><volume>09</volume><issue>05</issue><fpage>444</fpage><lpage>461</lpage><history><date date-type="received"><day>27,</day>	<month>July</month>	<year>2021</year></date><date date-type="rev-recd"><day>29,</day>	<month>August</month>	<year>2021</year>	</date><date date-type="accepted"><day>1,</day>	<month>September</month>	<year>2021</year></date></history><permissions><copyright-statement>&#169; Copyright  2014 by authors and Scientific Research Publishing Inc. </copyright-statement><copyright-year>2014</copyright-year><license><license-p>This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/</license-p></license></permissions><abstract><p>
 
 
  Bi
  <sub>2</sub>Fe
  <sub>4</sub>O
  <sub>9</sub> crystalline ceramic was successfully synthesized through a soft chemical route at lower sintering temperature for analysis of photocatalytic behavior with respect to adsorption of Congo Red (CR) in the presence of UV-VIS irradiation. The single-phase formation of Bi
  <sub>2</sub>Fe
  <sub>4</sub>O
  <sub>9</sub> ceramic was confirmed by powder X-ray diffraction studies and particle size observed by TEM analysis was found to be 148 &#177; 5 nm which reveals the crystalline nature of the materials. Additionally, the photocatalytic activity of Bi
  <sub>2</sub>Fe
  <sub>4</sub>O
  <sub>9</sub> ceramic was evaluated by the degradation of Congo Red in presence of visible light. The optical band gap (Eg) of the synthesized materials was found to be 1.8 eV. It exhibited greater photocatalytic activity than other synthesized materials like BiFeO
  <sub>3</sub> as well as TiO
  <sub>2</sub> due to a smaller band gap (1.8 eV). Furthermore, process variables such as pH.
 
</p></abstract><kwd-group><kwd>Chemical Route</kwd><kwd> Microstructural Studies</kwd><kwd> Dielectric Properties</kwd><kwd> Adsorption</kwd><kwd> Cyclic Voltammetry Analysis</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>Photocatalyst with higher activities for the environmental applications i.e. water disinfection, water purification and air purification have been major challenge in recent years. Among them, photocatalysis based on semiconductors such as titanium oxide has been attracted more attention for environmental applications due to strong oxidizing power, good chemical inertness, long-term stability and cost-effectiveness, etc. [<xref ref-type="bibr" rid="scirp.111658-ref1">1</xref>] [<xref ref-type="bibr" rid="scirp.111658-ref2">2</xref>] [<xref ref-type="bibr" rid="scirp.111658-ref3">3</xref>]. With dielectric constant, it has been used as a green technique for air and water treatment. Definitely, TiO<sub>2</sub> is certainly an excellent photocatalyst that carries out aerophilous decomposition. There are many organic compounds under UV radiation, whose band gap (3.2) is higher than TiO<sub>2</sub>, which limits any application [<xref ref-type="bibr" rid="scirp.111658-ref2">2</xref>] [<xref ref-type="bibr" rid="scirp.111658-ref4">4</xref>] [<xref ref-type="bibr" rid="scirp.111658-ref5">5</xref>]. Over many years, a number of photocatalytic semiconductors were worked out, such as CaBi<sub>12</sub>O<sub>4</sub>, BiFeO<sub>3</sub>, SrTiO<sub>3</sub>-Fe<sub>2</sub>O<sub>3</sub>, and the metallic element WO<sub>12</sub>, in addition to which a rumor has been reported [<xref ref-type="bibr" rid="scirp.111658-ref6">6</xref>] [<xref ref-type="bibr" rid="scirp.111658-ref7">7</xref>]. The band gap of those metal oxides which is applicable for the absorption of light, so that could it doubtless be economical photocatalysts beneath the light. Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> is a crucial material that may be used as a semiconductor gas sensing element and catalyst for ammonia oxidization. Besides, the above-named application, a recent study has been reported to Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> material that may be used as a semiconductor gas identifying element and catalyst for ammonia oxidation. Furthermore, Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> nanoplates will act as photocatalysts for acid-base indicator (Methyl Orange) degradation below visible light irradiation, whereas the Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> microplates solely exhibit this performed below ultraviolet light. Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> is a specific type of photocatalytic under UV-Visible light and it is used as semiconducting material, a possible gas sensitive material and catalyst for ammonia chemical reaction to Nitric Oxide [<xref ref-type="bibr" rid="scirp.111658-ref8">8</xref>] [<xref ref-type="bibr" rid="scirp.111658-ref9">9</xref>]. The microstructural property plays an important role in determining the physical properties of the crystal. The magnetic property, optical property, and semiconductor properties are closely related to their morphology [<xref ref-type="bibr" rid="scirp.111658-ref10">10</xref>] [<xref ref-type="bibr" rid="scirp.111658-ref11">11</xref>]. In addition to this, the relationship between the photocatalytic property and the electronic structure should also be studied to guide the further improvement of the photocatalytic activity. Moreover, investigations on photocatalytic performance only by photodegradation of dyes are not convincing, as it is hard to avoid the discoloring of dyes from adsorption and photosensitization. Photodegradation experiments on alternative organic contaminants are necessary to any judge the photocatalytic performance and create preparations for its practical applications within the future. Liquid ammonia together with the most important nitrogen-containing pollutants in waste may be a potential supply of oxygen depletion thanks to eutrophication [<xref ref-type="bibr" rid="scirp.111658-ref7">7</xref>]. Both ammonium ion NH 4 + and its conjugate base NH<sub>3</sub> are often present in water and effluent. Though the photocatalytic oxidation of NH 4 + /NH<sub>3</sub> by TiO<sub>2</sub> has been reportable in many studies, there are few reports on the photodegradation of NH 4 + /NH<sub>3</sub> in alternative systems. It’s revealing to begin the studies on the NH 4 + /NH<sub>3</sub> degradation by alternative photocatalysts, such as the ready Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> underneath actinic ray irradiation. Besides NH 4 + /NH<sub>3</sub>, the photocatalytic degradation of phenol on Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> is also according to the present paper. As is renowned, phenol is a widely used organic chemical present during a sort of wastewaters from numerous completely different industries, and it’s quite toxic and slowly degradable within the atmosphere. The phenol removal is additionally of high environmental concern to seek out a good photocatalyst for its oxidization [<xref ref-type="bibr" rid="scirp.111658-ref8">8</xref>]. Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub>, an antiferromagnetic semiconductor with a mullite structure has attracted in depth interest for its specific magnetic structures, potential photocatalytic application beneath ultraviolet (UV) and visual light, and plays a distinctive role as a gas sensor. The crystallographic structure of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> belongs to the orthorhombic space cluster Pbam, whose building block consisting of two formula units are often delineated as columns of edge-sharing FeO<sub>6</sub> octahedral connected by corner-sharing FeO<sub>4</sub> tetrahedral and bismuth atoms [<xref ref-type="bibr" rid="scirp.111658-ref10">10</xref>]. Although the antimagnetic force structure of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> has been investigated by many teams, the size-dependent magnetic properties of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> Nano Crytals (NC) haven’t been reported nevertheless, and also the investigation into the dimensions dependence of magnetic properties is of Brobdly importance for elementary researches and applications in spintronics. Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> NCs exhibit a wonderful photocatalytic reaction of stain (Methyline Blue) below actinic ray irradiation with the help of a little amount of H<sub>2</sub>O<sub>2</sub>. It’s conjointly found that a metamorphosis from anti-ferromagnetism to weak magnetic force happens once the average diameter of the nanoparticles is below 57 nm, and smaller Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> NCs exhibit higher photocatalytic activity under visible-light irradiation. Moreover, at the same time, our samples show a quicker degradation rate below actinic ray irradiance with the help of H<sub>2</sub>O<sub>2</sub> than do microplatets and nanosheets prepared by Ruan and Zhang [<xref ref-type="bibr" rid="scirp.111658-ref11">11</xref>]. Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> is also attention-grabbing because of its multiferroic nature, high gas sensitivity, and chemical action oxidization of ammonia to NO. The creation of nanostructures could be a basic strategy to realize excellent photocatalytic activity since the photocatalytic reaction occurs dominantly on the catalyst surface and nanostructures can without doubt offer an oversized expanse to volume magnitude relation. Up to now, the preparation of nanostructured Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> has been chiefly based on the hydrothermal method, sol-gel template technique, and melted salt technique. Within the side of morphology management, the hydrothermal route offers a plus over alternative preparation techniques; but, the merchandises obtained from the tactic tend to possess a reasonably massive particle size, and furthermore, a cumbersome abstersion method is usually needed to clean out impurities. The properties of useful materials powerfully rely on their morphology, microstructure, dimension and crystallinity. Manageable microstructure and morphology area unit are vital not just for basic analysis but additionally for technological applications. For the sake of morphology control, various methods such as hydrothermal process, sol-gel, solid-state reaction, and molten-salt synthesis for the preparation of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> have been employed [<xref ref-type="bibr" rid="scirp.111658-ref12">12</xref>] [<xref ref-type="bibr" rid="scirp.111658-ref13">13</xref>] [<xref ref-type="bibr" rid="scirp.111658-ref14">14</xref>].</p><p>In the present study, Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic was synthesized by the chemical method for improvement of photocatalytic activity of the materials as the chemical route is one of foremost promising routes than other routes due to its low cost, simple process, and low reaction temperature, potential price and advantage for large-scale production [<xref ref-type="bibr" rid="scirp.111658-ref6">6</xref>].</p></sec><sec id="s2"><title>2. Experimental Details</title><sec id="s2_1"><title>2.1. Material Synthesis</title><p>Analytical grade chemicals, Bi(NO<sub>3</sub>)<sub>2</sub>∙6H<sub>2</sub>O (99% Merck, India) and iron nitrate Fe(NO<sub>3</sub>)<sub>3</sub>∙9H<sub>2</sub>O were taken as starting materials for the synthesis of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic by the chemical route<sub>.</sub> The stoichiometric amount of bismuth nitrates was dissolved in de-ionized distilled water along with appropriate amount of glycine (C<sub>2</sub>H<sub>5</sub>(NO<sub>2</sub>), 99% Merck, India) as per equivalent to the metal ions. The resulting reaction mixtures were heated on a hot plate magnetic stirrer and maintaining the temperature 70˚C - 80˚C for evaporation of excesses of water. A fluffy mass obtained in the ignition process which burnt with a sooty flame. The obtained fluffy mass was crushed into fine powder with the help of mortar and pestle. The resultant dry powder was calcined at 600˚C for 6 h in the electrical muffle furnace and made pellets (13.0 mm diameters, 1.6 mm thicknesses) using 2 wt% polyvinyl alcohol (PVA) as a binder. These pellets were sintered at 800˚C for 6 h and further carried out different types of physiochemical characterizations such as XRD, SEM, TEM, EDX, Cyclic voltammetry, and Photocatalytic activity.</p><p>A Congo Red (CR) dye was selected as the model pollutant in the adsorption study. Initially, a 500 mg/L of CR stock solution was prepared, and experimental samples of respective concentrations (5, 10, 20, 30, 40, and 50 mg/L) were prepared by serial dilution technique. A standard curve of CR was prepared at 497 nm by using a UV-Vis spectrophotometer (Universal Bio, India). The batch adsorption study was performed in 100 mL Erlenmeyer flask by adding absorbent into 50 mL CR solution and shaken at 120 rpm and 30˚C &#177; 1˚C. The effect of process time (0.5 - 10 min), CR concentration (5 - 50 mg/L), and adsorbent dosage (0.1 - 1.0 g/L) were studied against the removal of CR. The samples were taken at regular time intervals and then centrifuged at 5000 rpm for 5 to measure the final CR concentration. The removal efficiency (%) and adsorption capacity (q<sub>e</sub> (mg/g)) of CR dye was measured by the following equations.</p><p>Removal efficiency of CR dye = C i n − C o u t C i n &#215; 100 (1)</p><p>Adsorption capacity (q<sub>e</sub>) = C i n − C o u t M &#215; V (2)</p><p>where C<sub>in</sub> and C<sub>out</sub> represent the inlet and outlet concentration of CR dye (mg/L), respectively. V is the volume of CR solution (L) and M is the mass of adsorbent (mg/g).</p></sec><sec id="s2_2"><title>2.2. Material Characterization</title><p>The crystalline phase of sintered material was identified by an X-rays Diffractometer (Rigakuminiflex 600, Japan) at a scan rate of 3˚/min in 2θ range of 20˚ - 80˚ employing CuK<sub>α</sub> radiation of wavelength, λ = 1.54059 &#197;. The morphology of the fractured surface of sintered Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> was characterized by scanning electron microscope (ZEISS, model EVO–18 research; Germany).The Bright field TEM images were obtained with the help transmission electron microscopy (TEM, FEI Tecnai-20G<sup>2</sup>) with an accelerating voltage of 200 kV. For dielectric measurements, the pellets were polished and painted by silver paste; then dried at 300˚C for 3 h to form electrodes for the respective characterizations. Electrical measurement data were taken by LCR meter (PSM1735-NumtriQ, Newton 4<sup>th</sup> Ltd UK) by varying the temperature and frequency. Optical band gap energy of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> nanoparticle was evaluated from the observed diffuse reflectance spectra. Reflectance spectra recorded with the help of balanced deuterium-halogen source (DH 2000 BAL, Ocean Optics) with 210 - 2500 nm spectral range.</p></sec><sec id="s2_3"><title>2.3. Electrochemical Characterizations</title><p>Cyclic voltammetry and electrochemical impedance spectroscopy of all the samples have been performed by Versa STAT 3. Corresponding details have been studied in our earlier research work [<xref ref-type="bibr" rid="scirp.111658-ref15">15</xref>] [<xref ref-type="bibr" rid="scirp.111658-ref16">16</xref>].</p></sec><sec id="s2_4"><title>2.4. Electrode Preparation</title><p>The electrode preparation methods have been discussed in our earlier paper [<xref ref-type="bibr" rid="scirp.111658-ref17">17</xref>] [<xref ref-type="bibr" rid="scirp.111658-ref18">18</xref>].</p><p>Fabrication of the electrode was done by making a dispersion of 5 mg of prepared material, 2-propanol of 0.2 mL, Nafion of 12 &#181;L and drop casting 80 &#181;L on carbon paper of 1 cm<sup>2</sup> area. Silver glue was used to connect the current collector (copper wire) with the substrate (carbon paper).</p><disp-formula id="scirp.111658-formula1"><graphic  xlink:href="//html.scirp.org/file/3-2710897x9.png?20210831165108305"  xlink:type="simple"/></disp-formula></sec></sec><sec id="s3"><title>3. Results and Discussion</title><sec id="s3_1"><title>3.1. X-Ray Diffraction Analysis</title><p>X-ray diffraction pattern of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> polycrystalline ceramic sintered at 800˚C for 8 h is shown in <xref ref-type="fig" rid="fig1">Figure 1</xref> which confirms the single phase formation of the materials. All the diffraction peaks are correctly matched with JCPDS card no. 20-0836 which clearly reveals the absence of secondary phases in the synthesized materials. The orthorhombic structure of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic was fabricated by two formula units per unit cell. These formula units consist of evenly distributed FeO<sub>6</sub> octahedrons and FeO<sub>4</sub> tetrahedrons with a lower packing density than that of corresponding closed packed structures. The Bi<sup>3+</sup> ions are surrounded by eight oxygen ions with mutually orthogonal shorter BiO<sub>3</sub> and longer BiO<sub>5</sub> units The most intense peaks of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic corresponding to the planes (211), (220), (240), (133), (310), (420), (213), (530) are observed in the XRD pattern. All the characteristic peaks of XRD data were indexed on the basis of a cubic unit cell similar to Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub>. The lattice parameter and unit cell volume of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic were determined by using “Cel” software having lattice parameter a = 7.97 &#197;, b = 8.43 &#197;, c = 6.01 &#197;. The crystallite size (D) of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic was calculated with the help of Debye-Scherer’s formula as given by the following expression.</p><p>D = k λ / β cos θ (3)</p><p>where, k is a dimensionless shape factor, with a value taken as 0.90, λ is the wavelength of X-ray,θ is the diffraction angle (Bragg angle), andβ is the peak width of the diffraction peak at half-maxima (FWHM) and their value is taken as in radian. The β is corrected value of diffraction peak due to instrumental broadening for crystallite size with reference to standard silicon wafer sample. The average crystallite size of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic calculated by Debye–Scherer’s formula and found to be 37.71 nm.</p></sec><sec id="s3_2"><title>3.2. TEM and SEM Analysis</title><p>Bright field TEM images of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic sintered at 800˚C for 8 h is depicts in <xref ref-type="fig" rid="fig2">Figure 2</xref>(a) which reveals the aggregation of the particles. The average particles size of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic was found to be 102.58 nm. Bright spot pattern observed in selected area diffraction (SAED) patterns for Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic shown in <xref ref-type="fig" rid="fig2">Figure 2</xref>(b), emerging through the corresponding planes (4 4 4), (3 1 0), (4 4 0) and (3 2 1), respectively confirmed crystalline nature of the material. <xref ref-type="fig" rid="fig2">Figure 2</xref>(c) exhibits high resolution TEM image displaying inter-planar (d) spacing for Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic. The d-spacing value observed for the Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic is d = 4.157 &#197; with the corresponding plane (2 1 1). The entire diffraction pattern obtained in the SAED pattern and HR-TEM image are good agreements with the JCPDS card number 46-0416 of the XRD results.</p><p>Microstructure feature of the grains of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub>ceramic was observed in the SEM analysis on the scale 200 nm which is shown in the <xref ref-type="fig" rid="fig3">Figure 3</xref>. It is revealed from the figure that homogenous grain was distributed of the materials. The average grain size of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic was found to be 100 &#177; 20 nm, measured with the help of Image-J software.</p></sec><sec id="s3_3"><title>3.3. Dielectric Properties</title><p>The variation of dielectric constant (ε) with frequency (Hz) and few selected temperatures of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic are shown in <xref ref-type="fig" rid="fig4">Figure 4</xref>. The value of ε decreases with increase of frequency as clear from the figure and remains constant at higher frequency range. This value at lower frequency region may be arises due</p><p>to space charge polarization in between semi-conducting grains and insulating grain boundaries and constant value of ε due to rapid periodic reversal of electric at higher frequency regions. That is why no charge accumulation occurs at interface in higher frequency and results lower value of ε. The value of dielectric constant of the material is found to be 645.45 at 20 Hz and 373 K.</p><p>Plots of dielectric loss (tanδ) with frequency at different temperatures of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic is shown in <xref ref-type="fig" rid="fig4">Figure 4</xref>. It is clearly revealed from the figure that the same trends in tanδ with frequency is observed as the dielectric constant up to 100 kHz and after which above 100 kHz, the value of dielectric loss exactly merged to each other over all measured temperatures. The value of tanδ for Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic was found to be less than 1.0 at 1 kHz at all measured temperatures. The higher value of dielectric loss of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic may be due to space charge polarization.</p><p><xref ref-type="fig" rid="fig5">Figure 5</xref> shows the variation of relative permittivity with temperature at some particular frequencies of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic. The below figure shows that dielectric constant first increases and attain maxima and then decreases with increase of temperature. The increment of ε with decreasing frequency may be due to reduction of bonding force in between the atoms which enhance the polarization of the materials.</p><p>The value of dielectric constant for Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> at 1 kHz, 10 kHz and 100 kHz were found to be 209, 138, and 88 respectively. The plot of Dielectric loss (tanδ) with temperature at 1 Hz, 10 Hz and 100 kHz is shown in <xref ref-type="fig" rid="fig5">Figure 5</xref>. The dielectric loss first increases and then decreases with increasing temperature. The increase in the tanδ with temperature may be regarded as oxygen vacancy present in the BiFeO<sub>3</sub> ceramic during sintering process. The value of tanδ for Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> was found to be 0.87, 0.33 and 0.14 at 1 kHz, 10 kHz and 100 kHz, respectively.</p></sec><sec id="s3_4"><title>3.4. Adsorption Studies</title><p>The contact time of dye solution with adsorbent is adversely affects the dye removal efficiency [<xref ref-type="bibr" rid="scirp.111658-ref19">19</xref>]. It is helpful to analyze the kinetics of dye removal. The effect of process time with respect to Congo Red (CR) removal (%) by Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> under the following conditions (pH: 7.0, CR concentration: 20 mg/L, adsorbent dose, 0.1 g/L, temperature: 30˚C &#177; 1.0˚C, and 120 rpm) is shown in <xref ref-type="fig" rid="fig6">Figure 6</xref>. The removal efficiency of CR dye was very fast up to 1.5 min and thereafter reached to the state of equilibrium after a very short contact time (5.0 min). Initially, 93.5% of CR removal efficiency was obtained in 1.5, which further increased with process time and reached 99.3% in 5 min. The obtained result reveals that the material offers very rapid adsorption of CR dye on Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub>. The effective adsorption of CR dye by Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> was endorsed to its higher surface area and more available surface active sites for adsorption of Cr dye.</p><p>Effect of process time on CR removal efficiency by Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> (pH: 7.0, CR concentration: 20 mg/L, adsorbent dose: 0.1 g/L: temperature: 30˚C &#177; 1.0˚C, and 120 rpm): The influence of adsorbent dose (0.1 - 1.0 g/L) against CR removal (%) by Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> under following conditions (pH: 7.0, CR concentration: 20 mg/L, process time: 5.0 min, temperature: 30˚C &#177; 1.0˚C, and 120 rpm) is shown in <xref ref-type="fig" rid="fig7">Figure 7</xref>. A gradually increasing trend of CR dye removal efficiency with increasing adsorbent dose was obtained. The low amount of adsorbent provides less adsorption site at constant CR dye concentration, resulting in low removal efficiency was found. Whereas, large adsorbent dosage leads to an increase in active surface area and adsorption site at constant CR dye concentration, and thus increased CR dye removal efficiency. The CR removal efficiency of 25.4% was found with an adsorbent dose of 0.1 g/L, which was further increased to 97% with 0.8 g/L of adsorbent dose. After that, the CR removal efficiency was not much improved with the adsorbent dose and found to be 99% with 1.0 g/L of adsorbent dose. It was probably due to about all adsorbate (i.e., CR dye) was adsorbed onto the active sites of the adsorbent (Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub>). The effect of adsorbent dose (i.e., polydopamine-kaolin and polydopamine-reduced graphene oxide-kaolin) on the</p><p>removal of Methylene Blue (MB) was studied and high removal efficiency of MB was obtained at high adsorbent dose due to availability of high active surface area and adsorption site [<xref ref-type="bibr" rid="scirp.111658-ref19">19</xref>].</p><p><xref ref-type="fig" rid="fig8">Figure 8</xref> depicts Effect of adsorbent dose on CR removal efficiency by Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> (pH: 7.0, CR concentration: 20 mg/L, process time: 5.0 min, temperature: 30˚C &#177; 1.0˚C, and 120 rpm). The effect of initial CR concentration (5 - 50 mg/L) in removal efficiency (%) of CR dye by Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> under following conditions (pH: 7.0, adsorbent dose: 0.1 g/L, process time: 5.0 min, temperature: 30˚C &#177; 1.0˚C, and 120 rpm) is shown in <xref ref-type="fig" rid="fig8">Figure 8</xref>. It can be perceived from the figure that the adsorption of CR dye on Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> was decreased with increasing initial concentration of CR. Initially, CR removal efficiency was gradually decreased with increasing CR up to 20 mg/L, and thereafter the CR removal efficiency was decreased very sharply with increasing CR concentration. The highest CR removal efficiency of 97.8% was obtained at the lowest CR concentration of 20 mg/L, whereas the lowest CR removal efficiency of 42.5% was obtained at the highest CR concentration of 50 mg/L. The high concentration of CR dye could lead to the quick saturation of active site; hence the removal efficiency decreased at high CR concentration. The adsorption of methylene blue (MB) by graphene oxide modified kaolin was studied at various MB concentrations (5 - 40 mg/L), and the lowest removal efficiency of MB was obtained at the highest concentration due to saturation of active sites [<xref ref-type="bibr" rid="scirp.111658-ref20">20</xref>].</p></sec><sec id="s3_5"><title>3.5. Electrical Conductivity</title><p>The conductivity behavior of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> material shows photoconductivity and optical activity for the improvement of their properties. <xref ref-type="fig" rid="fig9">Figure 9</xref> shows the frequency-dependent conductivity behavior at completely different temperatures. The electrical transport properties of the materials derived from AC conductivity and therefore the total conductivity of the materials measured through Almond-West power law that was calculated by the following Equation (3). Frequency</p><p>dependent of AC conductivity for Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic was determine by Jonscher’s power law as given by using Equation (4).</p><p>σ A C = σ D C + A ω s (3)</p><p>σ A C = A ω s (4)</p><p>where, σ<sub>DC</sub> is the frequency-independent conductivity dominant at the lower frequency region. A is the temperature-dependent pre-exponential factor and sis the frequency exponent parameters (0 &gt; s &gt; 1), dependent on both of materials and temperature and frequency independent, ω is angular frequency (ω = 2πf). The value of frequency exponent parameters(s) obtained from the slope of the curve by linear square fitting and found to be −0.23, −0.12, 0.25 and 0.42 at 313, 333, 353 and 373 K temperatures. It is observed that the value of s for Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic almost equal to 1 and increases with increase of temperatures. The increase in s value with temperatures indicates the presence of hopping charge conduction mechanism in the Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic.</p><p>The activation energy for the AC conductivity, E<sub>ac</sub> of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic sintered at 800˚C for 8 h, can be calculated from the slope of logσ<sub>AC</sub> vs. inverse of temperature curve is depicts in the figure. It is observed from the figure that the value of conductivity linearly increases with increases of temperature. The AC conductivity was strongly correlated with the conduction mechanism in the materials over DC conductivity which occurred at higher temperature side due to thermally activated process.</p><p>The temperature-dependent of AC conductivity can be measured by Arrhenius equation and it calculated with the help of following expressions:</p><p>σ = σ 0 exp ( − E a k T ) (5)</p><p>where, σ is the conductivity of the materials, σ<sub>0</sub> is the pre-exponential factor, E<sub>a</sub> is the activation energy for the thermally activated process, T is the absolute temperature and k is the Boltzmann constant.</p><p>The activation energy of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> sample measured by using linear fitting of <xref ref-type="fig" rid="fig1">Figure 1</xref>0 and observed to be 0.042, 0.039 and 0.037 eV at 1 kHz, 10 kHz, and 100 kHz, respectively. From above observed data, it is found that the activation energy values (E<sub>a</sub>) slightly increases with decreasing the frequency which may be lead to be thermally activated process. The lesser value of E<sub>a</sub> with regarding to higher frequency may be cause of hopping charge mechanism which increases the conduction mechanism of the materials [<xref ref-type="bibr" rid="scirp.111658-ref5">5</xref>].</p></sec><sec id="s3_6"><title>3.6. Diffuse Reflectance Spectral Studies</title><p>Diffuse reflectance spectra of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> nanoparticle <xref ref-type="fig" rid="fig1">Figure 1</xref>1 showing strong light absorption in the UV-Visible region. However, it has also strong optical absorption extending upto NIR region. Similarly, reported optical band gap value (E<sub>g</sub>) of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> nanoparticle is 1.29 eV [<xref ref-type="bibr" rid="scirp.111658-ref21">21</xref>] [<xref ref-type="bibr" rid="scirp.111658-ref22">22</xref>], that may vary depending upon</p><p>the size of nanoparticle prepared and corresponding synthesis process. Similarly variation in techniques adopted for measurement of optical band gap, also have significant effect on the measured band gap value. In the present experiment we have adopted Kubelka-Munk theory for evaluation of optical band gap value of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> nanoparticle, from recorded diffuse reflectance spectra.</p><p>F ( R ) = α S = ( 1 − R ) 2 2 R (7)</p><p>F(R): Kubelka-Munk function;</p><p>α: absorption coefficient;</p><p>R: reflectance;</p><p>S: scattering factor.</p><p>Equation (7) describes that Kubelka-Munk function is proportional to absorption coefficient.</p><p>Optical band gap can be calculated from the plot of diffuse reflectance versus wavelength, where onset of linear increase in curve determines the corresponding band gap energy. But this method of calculating band gap energy produces slightly inaccurate value, hence it is mandatory to report the type of transition (direct/indirect) during evaluation.</p><p>Absorption edge analysis was applied to find the type of transition and to determine the optical band gap represented in Equation (8).</p><p>α h ν = k ∗ ( h ν − E g ) 1 / n (8)</p><p>k: energy independent constant;</p><p>E<sub>g</sub>: Optical band gap.</p><p>The exponent indicates the type of transition where, value of n = 2 and 1/2 for direct and indirect allowed transitions respectively. Since F(R) is proportional to α, modified form of Equation (2) can be represented as:</p><p>F ( R ) ∗ h ν = k ∗ ( h ν − E g ) 1 / n (9)</p><p>The exponent n in Equation (3) can be determined from the plot of (F(R)∙hν)<sup>n</sup> vs. hν. The best fit to the straight line near the onset of absorption, observed for n = 1/2 recommending indirect allowed transition for Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> nanoparticle.</p><p>From the plot of (F(R) * hν)<sup>1</sup><sup>/2</sup> vs. hν, the band gap value of prepared Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> nanoparticle is calculated to be 1.83 eV, from the extrapolation of linear region of curve.</p></sec><sec id="s3_7"><title>3.7. Cyclic Voltammetry</title><p>It can be seen from <xref ref-type="fig" rid="fig1">Figure 1</xref>2 that Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> has redox peaks at 0.11 V/0.08 V. This shows that the material is pseudo capacitive in nature. The maximum currents generated during the CV are 4.9 A/g and 5.1 A/g for oxidation and reduction, respectively. The calculated specific capacitance for the electrode is 215 F/g. This signifies that the material can also be used as an electrode in electrochemical supercapacitors.</p><p>From <xref ref-type="fig" rid="fig1">Figure 1</xref>3, the equivalent series resistance is found to be 17.1 Ω and charge transfer resistance is 11.5 Ω. Due to minimum charge transfer resistance it can be used in supercapacitors as electrodes (as conducting in nature).</p></sec></sec><sec id="s4"><title>4. Conclusion</title><p>Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic was synthesized by semi-wet method and studied as active photocatalysts. The sample was characterized by using different characterization methods such as X-Ray Diffraction (XRD), Scanning Electron Microscopy (SEM), Transmission Electron Microscopy (TEM). Additionally, the photocatalytic activities of synthesized Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> were evaluated by photo degradation of Congo Red (CR). The Effect of process time, adsorbent dose and initial Congo Red concentration were optimized at batch mode and the outcomes demonstrate that Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> shows the pre-eminent potential for the photo degradation of Congo Red. The UV-visible study of BFO revealed a direct transition at 1.8 eV for visible light absorption. The frequency and temperature-dependent AC conductivity observed by the Arrhenius equation explain the hopping charge mechanism in the Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> ceramic. The expected specific capacitance of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> based three-electrode system is found to be 215 F/g, and it exhibits pseudo capacitive nature. The electrode has a comparatively less charge transfer resistance of 11.5 Ω. The dielectric constant of the Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> was calculated with variation temperature and frequency and found to be 645.45 at 20 Hz and 373 K.</p></sec><sec id="s5"><title>Acknowledgements</title><p>Manish Kumar Verma thanks Head, Department of Chemistry, Indian Institute of Technology (BHU) Varanasi, India, for the continuation of financial assistance as a CSIR fellowship. The authors are thankful to the Incharge, CIFC, IIT (BHU) Varanasi for providing TEM, SEM, and XRD facilities.</p></sec><sec id="s6"><title>Conflicts of Interest</title><p>The authors declare that there is no conflict among them regarding the publication of this article.</p></sec><sec id="s7"><title>Cite this paper</title><p>Verma, M.K., Kumar, V., Das, T., Sonwani, R.K., Rai, V.S., Prajapati, D., Sahoo, K., Kushwaha, V.K., Gupta, A. and Mandal, K. (2021) Synthesis of Bi<sub>2</sub>Fe<sub>4</sub>O<sub>9</sub> Crystalline Ceramic as Extremely Capable Photocatalyst via Proficient Chemical Route. Journal of Minerals and Materials Characterization and Engineering, 9, 444-461. https://doi.org/10.4236/jmmce.2021.95030</p></sec></body><back><ref-list><title>References</title><ref id="scirp.111658-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">Li, X., Liu, S., Lv, K., Deng, K., Liu, S., Li, X., et al. (2008) (Bi, C and N) Codoped TiO2 Nanoparticles. Journal of Hazardous Materials, 161, 396-401. https://doi.org/10.1016/j.jhazmat.2008.03.111</mixed-citation></ref><ref id="scirp.111658-ref2"><label>2</label><mixed-citation publication-type="other" xlink:type="simple">Sun, A., Chen, H., Song, C., Jiang, F., Wang, X. and Fu, Y. (2013) Magnetic Bi25FeO40-Graphene Catalyst and its High Visible-Light Photocatalytic Performance. 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