2016
DOI: 10.1016/j.jtice.2015.06.017
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Preparation, characterization of corn stalk xanthates and its feasibility for Cd (II) removal from aqueous solution

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Cited by 22 publications
(7 citation statements)
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“…After the addition of NaOH and CS2 to cellulose, new uptake appeared in 1161 cm -1 and 1110 cm -1 (Figure 2c), which showed the typical uptake of cellulose xanthate (-O -C (= S) -S). Additionally, the wide and high bending vibration absorption of CH2 (1429 cm -1 ) confirmed that a substitution reaction had occurred mainly in the C-6 hydroxyl cellulose group (Zheng & Meng, 2016). FTIR spectra of beads (Figure 2d and 2e) showed a new absorption at 819 cm -1 for ACX-0 beads and 815 cm -1 or ACX-3, which was assumed to be an absorption of Zn-O bonds.…”
Section: Cellulose Contentmentioning
confidence: 76%
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“…After the addition of NaOH and CS2 to cellulose, new uptake appeared in 1161 cm -1 and 1110 cm -1 (Figure 2c), which showed the typical uptake of cellulose xanthate (-O -C (= S) -S). Additionally, the wide and high bending vibration absorption of CH2 (1429 cm -1 ) confirmed that a substitution reaction had occurred mainly in the C-6 hydroxyl cellulose group (Zheng & Meng, 2016). FTIR spectra of beads (Figure 2d and 2e) showed a new absorption at 819 cm -1 for ACX-0 beads and 815 cm -1 or ACX-3, which was assumed to be an absorption of Zn-O bonds.…”
Section: Cellulose Contentmentioning
confidence: 76%
“…The FTIR of microfiber cellulose ( Figure 2b) showed a reduction in absorption intensity at wave numbers 3471, 2929, and 1641 cm -1 , which showed that the absorption of lignin compounds in the sample was reduced. On the other hand, the absorption at wave number 1045 cm -1 was shown to increase, demonstrating the absorption of C-O-C cellulose groups (Zheng and Meng, 2016). After the addition of NaOH and CS2 to cellulose, new uptake appeared in 1161 cm -1 and 1110 cm -1 (Figure 2c), which showed the typical uptake of cellulose xanthate (-O -C (= S) -S).…”
Section: Cellulose Contentmentioning
confidence: 94%
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“…Com relação ao xantato de celulose de sisal modificado com álcool láurico, observa-se um evento endotérmico entre 225 e 250°C que pode está relacionado ao processo de dissociação do agente modificante, álcool láurico [17]. Observa-se ainda que nas curvas de DSC que tanto a celulose de sisal pura quanto o xantato de celulose de sisal modificado com álcool láurico apresentam declive endotérmico a partir da temperatura de 350°C que pode está relacionado à degradação de ambas as amostras [17][18][19][20]. Caracterização da morfologia da celulose de sisal bruta e modificada a partir de xantato de celulose por microscopia ótica A Figura 10 (a-d) mostra imagens de microscopia ótica obtidas por meio do equipamento USB Digital Microscope 20x-800x, com ampliação de 20x e 400x, da celulose de sisal bruta e do xantato de celulose de sisal modificado.…”
Section: Caracterização Térmica Da Celulose De Sisal Modificada a Parunclassified
“…Bioadsorption is considered a viable Cr (VI) and Hg (II) removal technique, because it removes large percentages of agroindustrial residual origin adsorbents that do not require care or maintenance, are not expensive, easy to process and highly available [25, 26, 27, 28, 29,]. Among the materials widely studied and with excellent results for the removal of heavy metals, are: corn huskTejada-Tovar et al, [30]; Zheng and Meng, [31], pine sawdust [32], bagasse of palm and yam [33], cassava and lemon peel [34], cane bagasse [35], walnut shell [36], coffee leaf [37], orange and cocoa shells [38,39], Mangifera sawdust [40],tea residue [41], Cayota urens waste [42], tusa corn stalks [43], , plantain peel [24], among others.…”
Section: Introductionmentioning
confidence: 99%