2022
DOI: 10.1016/j.chemosphere.2021.132472
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Effect of calcination temperature on morphology and phase transformation of MnO2 nanoparticles: A step towards green synthesis for reactive dye adsorption

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Cited by 67 publications
(31 citation statements)
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“…The effect of agitation speed on color removal was studied by varying the agitation speed from 0 to 225 rpm at 301 K. Figure S5 reveals that the color removal of RBBR increased from 43.78% to 97.42% with increasing agitation speed. The increase in adsorption efficiency may be due to increased turbulence attributable to the decrease in the thickness of the film resistance surrounding the particles of the WSBAC adsorbent, thus increasing external film diffusion and uptake of RBBR dye molecules [ 41 ]. This phenomenon may be explained by the increasing contact surface of the adsorbent-adsorbate solution, which leads to the transfer of dye molecules from the aqueous solution to the binding sites of the adsorbent [ 10 ].…”
Section: Resultsmentioning
confidence: 99%
“…The effect of agitation speed on color removal was studied by varying the agitation speed from 0 to 225 rpm at 301 K. Figure S5 reveals that the color removal of RBBR increased from 43.78% to 97.42% with increasing agitation speed. The increase in adsorption efficiency may be due to increased turbulence attributable to the decrease in the thickness of the film resistance surrounding the particles of the WSBAC adsorbent, thus increasing external film diffusion and uptake of RBBR dye molecules [ 41 ]. This phenomenon may be explained by the increasing contact surface of the adsorbent-adsorbate solution, which leads to the transfer of dye molecules from the aqueous solution to the binding sites of the adsorbent [ 10 ].…”
Section: Resultsmentioning
confidence: 99%
“…By contrast, the removal efficiency decreased with an increase in the initial TA concentration. This was also observed in the elimination of reactive blue 21 dye from manganese oxide nanoparticles [ 38 ]. The SBA-15/APTES samples revealed a higher adsorption capacity and removal efficiency as compared with those of SBA-15/PEHA.…”
Section: Resultsmentioning
confidence: 78%
“…[ 49 ] The surface morphology and size of bio‐MnNPs were determined by SEM (TM1000, Hitacchi, Tokyo, Japan) and TEM (1230JEOL, Akishema, Japan). [ 72 ] The samples were prepared on a carbon‐coated copper grid and an aluminum stub for SEM and TEM, respectively. The metallic fractions and elemental composition of bio‐MnNPs were characterized through EDS (Model EDS‐Oxford, Instruments, High Wycombe, Buckinghamshire, UK) at a working voltage of 20 KeV.…”
Section: Methodsmentioning
confidence: 99%