Page 494 - Polymer-based Nanocomposites for Energy and Environmental Applications
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Interplay of polymer bionanocomposites and significance of ionic liquids for heavy metal removal  447

           16.3.2 Enzymatic phosphorylation

           Enzymatic phosphorylation was carried out with respect to the method stated by Boz ˇic ˇ
           et al. [38] Concisely, reaction continues with 0.9 wt% of CNFSL/CNCBE phosphate
           buffer (pH 7.6) diffusion in the company of a 250 mM of MgCl 2 , 50 mM, ATP, and
           35 U/mL of hexokinase enzyme for 24 h at 30°C. After the protein deactivation, both
           phosphorylated products, phos-CNFSL and phos-cellulose nanocrystals (CNCBE),
           were cleaned numerous times (centrifuged at 6000 rpm for 4 min) with water, while
           no ATP absorption signal at 260 nm could be observed.


           16.4   Characterization techniques

           The primary goal of characterization was to investigate the properties of bio-
           nanocomposites that are either related to adsorption behavior toward metal ions or
           affecting it. The property variations of bionanocomposites after metal adsorption were
           also examined.


           16.4.1 Microscopy
           Morphologies of the materials would be examined by AFM (Nanoscope V, Veeco
           Instruments, Santa Barbara, California, the United States) and SEM (FEGSEM, Zeiss,
           Merlin). Tapping mode used to image all the AFM samples. A resonance frequency of
                                                                          1
           350 kHz was adjusted in the instrument and a spring constant at 10–200 nm .The
           diameter dimensions were measured with the help of Nanoscope V software. SEM
           images were observed with the help of secondary electron and InLens secondary elec-
           tron sensor with a voltage of 15 kV and a current of 15 pA. All sample coatings were
           performed by sputtering from tungsten anode, and the thickness of coatings was
           <10 nm. SemAfore software was used to calculate the diameter.


           16.4.2 Zeta potential
           Zetasizer nano-ZS Malvern (Worcestershire, the United Kingdom) at 25°C can be
           used to calculate the zeta potentials of the materials at different pH. All samples
           had constant concentrations of 0.05 wt%, and the calibration time for all the samples
           is 2 min. During the measurements, the Smoluchowski method was used to obtain the
           zeta potential. Vibro Viscometer SV-10 (Tokyo, Japan) was used to detect sample vis-
           cosities that were employed as a key parameter for zeta potential calculation.


           16.4.3 XRD
           Analysis of prepared films of CNF, CNC, and ChNC was conducted at a constant tem-
           perature with the help of step scanning on the Siemens X-ray diffractometer D5000
           (Berlin, Germany) to gauge the crystalline nature of the nanomaterials. The angle of
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