Abstract:A novel magnetic macroporous poly(glycidyl methacrylate-co-ethylene glycol dimethacrylate) (mPGME) was prepared by suspension copolymerization and functionalized with diethylenetriamine (mPGME-deta).
“…This area is also attributable to vibrations of bonds with FeSO 4 , more precisely, the SO 4 groups. 62–64 The same phenomenon is evident in PU918 supplemented with FeSO 4 (Fig. 7).…”
Section: Resultssupporting
confidence: 74%
“…62 and 63) in consideration of the change in absorbance at 1660 cm −1 , associated with a CO bond, a response in the band region of 1181 cm −1 , suggesting the formation of C–O, and a slight shift in the position of the carbonyl band at 1732 cm −1 . 62–64…”
Section: Resultsmentioning
confidence: 99%
“…62 and 63) in consideration of the change in absorbance at 1660 cm −1 , associated with a CO bond, a response in the band region of 1181 cm −1 , suggesting the formation of C-O, and a slight shift in the position of the carbonyl band at 1732 cm −1 . [62][63][64] In the case of the PUSU-based nanostructures doped with FeSO 4 and without the additive (Fig. 6), the presence of FeSO 4 is evident by the absorption band at 610-660 cm −1 .…”
Section: Supplementation Of the Polymer Nanostructure With An Adsorpt...mentioning
Polyurethane-based nanofibrous structures can be used as adsorbents for arsenic in water. Their adsorption capacity can be significantly increased by doping the structure with ferrous sulphate.
“…This area is also attributable to vibrations of bonds with FeSO 4 , more precisely, the SO 4 groups. 62–64 The same phenomenon is evident in PU918 supplemented with FeSO 4 (Fig. 7).…”
Section: Resultssupporting
confidence: 74%
“…62 and 63) in consideration of the change in absorbance at 1660 cm −1 , associated with a CO bond, a response in the band region of 1181 cm −1 , suggesting the formation of C–O, and a slight shift in the position of the carbonyl band at 1732 cm −1 . 62–64…”
Section: Resultsmentioning
confidence: 99%
“…62 and 63) in consideration of the change in absorbance at 1660 cm −1 , associated with a CO bond, a response in the band region of 1181 cm −1 , suggesting the formation of C-O, and a slight shift in the position of the carbonyl band at 1732 cm −1 . [62][63][64] In the case of the PUSU-based nanostructures doped with FeSO 4 and without the additive (Fig. 6), the presence of FeSO 4 is evident by the absorption band at 610-660 cm −1 .…”
Section: Supplementation Of the Polymer Nanostructure With An Adsorpt...mentioning
Polyurethane-based nanofibrous structures can be used as adsorbents for arsenic in water. Their adsorption capacity can be significantly increased by doping the structure with ferrous sulphate.
“…Based on our previous investigations [13,37], the synthesized amino-functionalized magnetic macroporous copolymer composite mPGMT-deta could be effective for adsorption of water contaminants, like radionuclides, cations and oxyanions, etc. A relatively high surface area combined with the possibility for introduction of different functional groups by the reaction with epoxide groups in GMA as well as easy separation of mPGMT-deta particles from metal salt solutions by an external magnetic field makes this composite potentially attractive as a magnetic adsorbent.…”
Section: Figure 8 Thermogravimetric Analysis Of Pgmt Mpgmt and Mpgmmentioning
Magnetic and non-magnetic macroporous crosslinked copolymers of glycidyl methacrylate and trimethylolpropane trimethacrylate were prepared by suspension copolymerization and functionalized with diethylenetriamine. The samples were characterized by mercury porosimetry, scanning electron microscopy with energy-dispersive X-ray spectroscopy (SEM-EDS), Fourier transform infrared spectroscopy analysis (FTIR-ATR), thermogravimetric analysis (TGA), X-ray diffractometry (XRD), atomic force microscopy (AFM), transmission electron microscopy (TEM) and SQUID magnetometry. The FTIR-ATR analysis of synthesized magnetic nanocomposites confirmed the presence of magnetite and successful aminofunctionalization. Non-functionalized and amino-functionalized nanocomposites exhibited superparamagnetic behavior at 300 K, with a saturation magnetization of 5.0 emu/g and 2.9 emu/g, respectively. TEM analysis of the magnetic nanocomposite has shown that magnetic nanoparticles were homogeneously dispersed in the polymer matrix. It was demonstrated that incorporation of magnetic nanoparticles enhanced the thermal stability of the magnetic nanocomposite in comparison to the initial non-magnetic macroporous copolymer.
“…The material that showed better performance in the initial adsorption tests was selected for further adsorption experiments, but first, the point of zero charge (pH PZC ) was determined to select the most appropriate pH for the subsequent tests. pH PZC was determined for the FA-AT7 material by the pH drift method. − A mass of 0.05 g was placed in contact with 20 mL of NaCl solutions (0.1 mol L –1 ), previously adjusted to the pH range from 2 to 12 for which was used 1 mol L –1 HCl or 1 mol L –1 NaOH solution was used. The solutions were stirred for 24 h at 200 rpm.…”
Parabens
are widely used as preservatives in food, pharmaceutical,
and cosmetic products. These compounds are known for their estrogen
agonist activity. This research investigates the synthesis of micro-
and mesoporous silica from coal fly ash at different pH values (13,
11, 9, and 7) as well as its use as an adsorbent for the removal of
parabens. The materials were characterized, and X-ray fluorescence
(XRF) analysis revealed that the fly ash acid treatment reduced the
presence of aluminum, iron, and calcium oxides and also that silica
synthesized at lower pH values (7 and 9) showed a higher SiO2 content. X-ray diffraction (XRD) and scanning electron microscopy
(SEM) analyses revealed microporous silica formation for silica synthesized
at pH 13 and mesoporous silica at pH 7, 9, and 11. Adsorption tests
were performed with materials, and FA-AT7 showed a higher adsorption
capacity. The effect of factors (A) adsorbent mass, (B) initial paraben
concentration, and (C) agitation rate on the adsorption process was
studied for the FA-AT7 adsorbent using a factorial experimental design.
Standardized Pareto charts revealed a negative effect of factor A,
positive effect of factor B, and negative interaction effects of factors
A–B for all studied parabens. Isotherms and multicomponent
kinetic studies were performed. A linear type-III isotherm was obtained,
and adsorption equilibrium was reached at approximately 10 min.
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