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    <identifier>10.57760/sciencedb.11935</identifier>
    <datestamp>2023-11-11T18:30:32Z</datestamp>
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  <dc:date>2023-11-11</dc:date>
  <dc:title>Characterization and Electrocatalytic activity analysis</dc:title>
  <dc:identifier>doi:10.57760/sciencedb.11935</dc:identifier>
  <dc:language>en</dc:language>
  <dc:description>1.&amp;nbsp;The morphology of TNTs array and SnO2-Sb electrodes were analyzed by SEM(S4700, Hitachi Ltd), including Figure 1 and Figure 3.2.&amp;nbsp;The wettability of TNTs substrates&amp;nbsp;were&amp;nbsp;examined by a contact angle test&amp;nbsp;with absolute ethyl alcohol, as shown in Figure 2.3.&amp;nbsp;The&amp;nbsp;crystalline patterns of&amp;nbsp;TNTs array and SnO2-Sb&amp;nbsp;electrodes&amp;nbsp;were analyzed by XRD (D/max-rB, Rigaku) with Cu&amp;nbsp;K&amp;alpha;&amp;nbsp;radiation, as shown in Figure 4.&amp;nbsp;Effect of preparation conditions for TNTs arrays on the average crystal size of SnO2-Sb calculated by Scherrer Formula, as shown in Table 1.&amp;nbsp;Scherrer Formula: D=K&amp;lambda;/(&amp;beta;cos&amp;theta;), where D is the crystallite size, K is the Scherrer constant (0.89), &amp;lambda; is the wavelength of incident ray, &amp;beta; is the full width at half maximum of the peak, and &amp;theta; is the position of plane peak.4.&amp;nbsp;Electrochemical analysis&amp;nbsp;was carried out in a&amp;nbsp;system consisted of a SnO2-Sb working electrode, a platinum sheet counter electrode, and a saturated Ag/AgCl reference electrode. Oxygen evolution potential was tested by LSV measurement in H2SO4&amp;nbsp;solution (0.5 mol/L), as shown in Figure 5. The double electrode layer structure&amp;nbsp;was analyzed&amp;nbsp;by EIS&amp;nbsp;measurement&amp;nbsp;inNa2SO4&amp;nbsp;solution ( 0.25 mol/L) with frequency range from 105 to10-1&amp;nbsp;Hz under an impedance amplitude signal of 5 mV. The aforementioned experiment was conducted in a three-electrode system using an electrochemical workstation (Auto Lab PGSTAT128N, Metrohm), as shown in Figure 6, and the EIS fitting results of TNTs/SnO2-Sb electrodes with different substrate preparation voltages&amp;nbsp;was shown in Table 2.&amp;nbsp;5.&amp;nbsp;The electrocatalytic degradation of phenol was operated in a cylindrical reactor&amp;nbsp;containing&amp;nbsp;0.25 mol/L Na2SO4&amp;nbsp;with the addition of 100 mgL-1&amp;nbsp;artificial phenol wastewater. As-prepared samples measuring 20mm&amp;times;20mm were utilized as the working anode, while stainless steel plates of the same size served as the cathode, with a distance of 10 mm between them.&amp;nbsp;All degradation experiments&amp;nbsp;operated under a certain stirring speed and&amp;nbsp;10 mA/cm2&amp;nbsp;current density. The concentration variations of phenol were determined by UV-Vis spectrophotometry (TU-1810PC, PERSEE) as a function of electrolysis time. The logarithmic relationship between phenol concentration and electrolysis time was analyzed using a pseudo-first-order kinetics model. The kinetic rate constant (k) of the electrode for phenol degradation was determined using the equation : ln(C0/Ct)=kt, where C0&amp;nbsp;represents the initial concentration of phenol and Ct&amp;nbsp;is its concentration at a given time t.Electrochemical degradation of phenol on TNTs/SnO2-Sb electrodes with TNTs substrates under different preparation conditions (a) Variations of concentration of phenol with electrolysis time (b) The first-order kinetics curves of phenol degradation&amp;nbsp;was shown in Figure 7.6.&amp;nbsp;The wettability of TNTs substrates were examined by a contact angle test with absolute&amp;nbsp;ethyl alcohol. SnO2-Sb loading on different substrates was weighed by the balance.&amp;nbsp;The effect of preparation voltage of TNTs arrays on the contact angle of substrate surface and loading amount of SnO2-Sb&amp;nbsp;was shown in Table 3.&amp;nbsp;7.&amp;nbsp;The surface chemical environment&amp;nbsp;element was analyzed by XPS (PHI5700 ESCA) with Al K&amp;alpha; radiation (h&amp;upsilon;=1486.6eV), as shown in Figure 8&amp;nbsp;and Figure 9, and the XPS analysis of TNTs/SnO2-Sb electrodes with different substrate preparation voltages&amp;nbsp;was shown in Table 4.8.&amp;nbsp;The oxygen vacancy&amp;nbsp;concentration were detected by EPR (Bruker ER200D-SRC) measurement, as shown in Figure 10.9.&amp;nbsp;The presence of hydroxyl radicals (‧OH) generation in a Na2SO4&amp;nbsp;solution (0.25 mol/L) with terephthalic acid&amp;nbsp;(0.5 mmol/L) as the trapping agent was determined using fluorescence spectroscopy technology (FP-6500, JASCO).&amp;nbsp;The hydroxyl radicals generation ability on the SnO2-Sb electrode with different substrate preparation voltages&amp;nbsp;was shown in Figure 11.10.&amp;nbsp;The reactive radicals generated during electrochemical degradation of organics were detected by&amp;nbsp;using a free radical quenching experiment, with a quencher of p-benzoquinone for ‧OH, and isopropyl alcohol for&amp;nbsp;superoxide radical (‧O2-).&amp;nbsp;The quenching experiment of the active radicals on the SnO2-Sb electrodes with different substrate preparation voltages&amp;nbsp;was shown in Figure 12, and the computed result from the quenching experiment&amp;nbsp;was shown in Table 5.&amp;nbsp;</dc:description>
  <dc:subject>electrocatalytic; TNTs; SnO2-Sb</dc:subject>
  <dc:creator>Lisha YANG</dc:creator>
  <dc:creator>Yanming GUO</dc:creator>
  <dc:rights>RESTRICTED</dc:rights>
  <dc:type>dataset</dc:type>
  <dc:relation>http://www.doi.org/10.1016/s1872-5813(23)60390-1</dc:relation>
  <dc:publisher>Science Data Bank</dc:publisher>
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