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The possibility of using the prepared composite as a based stationary phase for removal of arsenic (III) from waste water was evaluated.
The binding of HIgG to MEL-A was further confirmed using the prepared composite, considered to minimize the limitation presumed in the ELISA assay.
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Scanning electron microscopy (SEM; JSM-5600, JEOL Ltd., Tokyo, Japan) was used to observe the surface state and structure of the prepared composite using an electron microscope.
The prepared composite membrane using dispersion of PWS through the ESF-BP has superior characteristics and voltage current responses in the PEMFC rather than using CsPW.
The prepared composite was used for methyl green adsorption.
The prepared composite was characterized using scanning electron microscopy (SEM), X-ray diffractometer (XRD) and Brunauer Emmett Teller (BET) techniques.
The Surface area of the prepared composite was measured using BET method.
X-ray diffraction, Fourier transform infrared spectroscopy, and transmission electron microscopy were used to study the morphological characteristics of the prepared composite material.
The prepared composite scaffold was characterized using SEM, XRD, FTIR and TGA.
The prepared composite scaffolds were characterized using SEM, FT-IR and XRD studies.
The prepared composite material was characterized using XRD, XPS, SEM, EDS, FTIR, XRF, Raman, BET surface area and TGA/DTA.
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