Herein,
gum ghatti (GGTI)-
g
-[sodium acrylate (SA)-
co
-3-(
N
-(4-(4-methyl pentanoate))acrylamido)propanoate
(NMPAP)-
co
-4-(acrylamido)-4-methyl pentanoate (AMP)-
co
-
N
-isopropylacrylamide (NIPA)] (i.e.,
GGTI-
g
-TetraP), a novel interpenetrating tetrapolymer
network-based sustainable hydrogel, possessing extraordinary physicochemical
properties and excellent recyclability, has been synthesized via grafting
of GGTI and in situ strategic protrusion of NMPAP and AMP during the
solution polymerization of SA and NIPA, through systematic multistage
optimization of ingredients and temperature, for ligand-selective
superadsorption of hazardous metal ions (M(II)), such as Sr(II), Hg(II),
and Cu(II). The in situ allocation of NMPAP and AMP via N–H
and C–H activations, grafting of GGTI into the SA-
co
-NMPAP-
co
-AMP-
co
-NIPA (TetraP)
matrix, the effect of comonomer compositions on ligand-selective adsorption,
crystallinity, thermal stabilities, surface properties, swellability,
adsorption capacities (ACs), mechanical properties, and the superadsorption
mechanism have been apprehended via extensive microstructural analyses
of unloaded and/or loaded GGTI-
g
-TetraP1 and GGTI-
g
-TetraP2 bearing SA/NIPA in 8:1 and 2:1 ratios, respectively,
using Fourier transform infrared (FTIR),
1
H/
13
C/DEPT-135 NMR, X-ray photoelectron spectroscopy (XPS), thermogravimetric
analysis, differential scanning calorimetry, X-ray diffraction, field
emission scanning electron microscopy, rheological analysis, and energy-dispersive
X-ray spectrometry, along with measuring % gel content, pH at point
of zero charge (pH
PZC
), and % graft ratio. The thermodynamically
spontaneous chemisorption has been inferred from FTIR, XPS, fitting
of kinetics data to pseudo-second-order model, and activation energies.
The chemisorption data have exhibited excellent fitting to the Langmuir
isotherm model. For Sr(II), Hg(II), and Cu(II), ACs were 1940.24/1748.36,
1759.50/1848.03, and 1903.64/1781.63 mg g
–1
, respectively,
at 293 K, 0.02 g of GGTI-
g
-TetraP1/2, and initial
concentration of M(II) = 500–1000 ppm.