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FT-IR and 13C NMR results confirmed the modification of LEP-1b into SeLEP-1b.
When compared with the spectrum of OAMB biomass (Fig. 3a) additional absorption peaks were noted which confirmed the modification.
Morphological and thermal characterization by scanning electron microscopy and thermal gravimetric analysis confirmed the modification by urea.
FTIR spectroscopy confirmed the modification through introduction of peaks characteristic of ester linkages between sulfosuccinic acid and vinyl alcohol.
It confirmed the modification of TiO2-NTs substrate greatly improved the electrocatalytic degradation of organic pollutant, using phenol as the target contaminant.
Elemental analysis of MCT β-CD powder had shown about 3.7% N2 present in MCT β-CD, whereas, 0% was available in native β-CD; that confirmed the modification of β-CD with monochlorotriazine group.
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X-ray photoelectron spectroscopy was also applied to confirm the modification of MNPs.
Compositional analysis and electrokinetic behavior were investigated to confirm the modification of the TiO2 surface with P2O5.
In order to confirm the modification process, the FTIR spectra analysis was utilized, as shown in Fig. 3b.
TEM characterization was used to present the microtopography and microstructure of the In2S3/ZnO core/shell nanosheets, which further confirms the modification of the ZnO overlayer on In2S3.
In order to confirm the modification of the MNPs' surface, the FT-IR spectroscopy of the prepared MNPs@SiO2 and CTMS-MNPs@SiO2 materials was obtained (Figure 3B).
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