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Molecular structure of sodium alginate.

Molecular structure of sodium alginate.

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The performance of a new adsorbent, sodium alginate-graft-poly(methyl methacrylate) in the form of calcium cross-linked beads has been evaluated for the removal of Pb2+ from aqueous solution. Characterization of the adsorbent was performed using Fourier transform infrared spectroscopy, scanning electron microscopy and laser diffraction technique. T...

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... the materials are cheap, non- toxic, biocompatible, and abundant in nature. Alginic acid or its salts called alginates are among the polysac- charides that occur in the cell walls of a large number of algal species. It is a copolymer consisting the resi- dues of β-1,4-linked-D-mannuronic acid (M-block) and α-1,4-linked-L-guluronic acid (G-block) (Fig. 1) [14]. Sodium alginate possesses metal sequestering proper- ties and can effectively sequester the dissolved metal ions in solutions quickly. It is an ideal material for the treatment of wastewater that contained heavy metal ions, due to its high content of carboxyl (COOH) and hydroxyl (OH) functional groups, which have high affinity ...

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... In contrast, sodium alginate (SA) is the sodium salt of alginic acid, a polymer with many free hydroxyl and carboxyl groups dispersed along the polymer's backbone chain. The linear, anionic polysaccharide is made up of two types of 1,4-linked hexuronic acid residues: β -d-mannuronopyranosyl (M) and α-l guluronopyranosyl (G), which are arranged in blocks of repeating M residues (MM blocks), blocks of repeating G residues (GG blocks), and blocks of mixed M and G residues (MG-blocks) [48]. ...
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... It is made up of 1 → 4 linked β-d-guluronic (G), and α-lmannuronic (M) molecule [7,8]. Polymeric segment -M-G blocks are combined to form uronic acids ( Fig. 1) [9]. ...
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... In very dilute solutions, these methods are not only unsuccessful for water remediation but also to be very high cost for removal of Pb(II). Therefore, many approaches have been reported to develop more effective techniques for removing lead from wastewater, for instance, liquid extraction, membrane cleaners, and adsorption [3,[6][7][8]. ...
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... [61]. [65]. ...
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... This is composed of 1 ? 4 linked b-D-guluronic (G) and a-L-mannuronic (M) [12][13][14][15]. The uronic acids are linked by -M-G sequence randomly (Fig. 1) [16]. Alginate is an anionic (COO-) polymer which is suitable for coordination formation. ...
... Y.O.IWAKI et.al observed a conductivity value 8.7 9 10 -5 S cm -1 in SA with acetic acid (CH 3 COOH) and a conductivity value 3.1 9 10 -4 S cm -1 in SA with LiClO 4 [16]. A.F.Fuzlin et.,al reported a conductivity value of 7.46 9 10 -5 S cm -1 for alginate with LiBr [4]. ...
... This indicates that the increases of crystalline nature of the polymer electrolyte. 16.5 weight loss), the initial weight loss is due to evaporation of moisture in the polymer electrolytes. ...
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... While grafting, reductive amination, sulfonation, esterification, and oxidation methods are achieved for the modification of hydroxyl groups, esterification, Ugi reaction, and amidation methods are used for modification of carboxyl groups (Yang et al., 2011). Some recent studies with SA graft polymers for heavy metal adsorption were given as follows: SA-g-poly(methyl methacrylate) with Pb(II) adsorption capacity of 526 mg.g −1 (Salisu et al., 2016); kaolin/SA-g-polyacrylic acid-co 2-acrylamido-2-methyl-1-propane sulfonic acid with Cd(II), Zn(II), and Pb(II) adsorption capacities of 69.9, 139.8, and 834.7 mg.g −1 , respectively (Zhu et al., 2015); SA-g-polyacrylamide/graphene oxide hydrogel with Cu(II) and Pb(II) adsorption capacities of 68.76 and 240.69 mg.g −1 , respectively (Jiang et al., 2020); SA-g-diphenylamine with Co(II) adsorption capacity of ~ 92 mg.g −1 (Ahmed et al., 2021). Also, the max adsorption capacities of heavy metals for some SA consisting polymers were listed as follows: SA-polyaniline nanofibers: 73.34 mg.g −1 for Cr(VI) (Karthik & Meenakshi, 2015), SA/graphene oxide aerogel: 98.0 mg.g −1 for Cu(II) and 267.4 mg.g −1 for Pb(II) (Jiao et al., 2016); chitosan/SA/Ca ion double network hydrogel: 70.83, 81.25, and 176.50 mg. ...
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... Alginates, as a natural polysaccharide extracted from the brown algae of marine (Phaeophyceae), are compounded by L-guluronate (G) and R-D-mannuronate (M) units at various ratios and sequences in the (1→4) chain depending on the age of the plant and the source of alginate ( Figure 6) [17,18,83]. By the addition of calcium ions, the formation of gels involving the G blocks is carried out, so the higher gel strength, the higher concentration of G units [17,84]. ...
... Chemical structure of sodium alginates. Reprinted from[83]. Copyright 2016 Taylor & Francis. ...
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... The percentage grafting, G(%) decreased when the initiator amount was increased above 0.2g. This could be attributed to more free-radical generation that eventually may lead to premature termination (by coupling) of the growing radicals at higher concentration (16). It was observed that the highest percentage grafting was acheived at acrylic acid concentration of 5 g and KPS concentration of 0.2 g. ...
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... The effect of initial concentration of Pb 2+ and Cu 2+ metal ions on the percentage removal by the composite beads was investigated in the range of 50-300 mg/L and the results were shown in Fig. 6.The removal percentage was found to be high at lower concentration of the metal ions, but eventually decrease with the increased in the initial concentration. This can be attributed to the exhaustion of available active sites on the adsorbent required for the high initial concentration of the metal ions adsorption (Salisu et al., 2016). ...
... This could be attributed to increase the surface porosity of the adsorbent as a result of interaction with the acid. A similar trend was reported on the adsorption and desorption of alginate beads using HCl (Salisu et al., 2016). The result showed that the alginate composite beads maintained good adsorption capacity for several cycles. ...