2021
DOI: 10.25100/iyc.v24i1.11139
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Effective adsorption of Tartrazine by modified biomaterial from wheat residues

Abstract: The use of adsorbents from wheat residues (WR), wheat cellulose (WC) and wheat cellulose (MWC) treated with Cetyl trimethyl ammonium chloride (CTAC) was studied in the removal of tartrazine in an aqueous solution. The effect of adsorbent dose (15, 25 and 35 mg) and initial concentration (40, 70 and 100 mg/L) was evaluated. WC was obtained by double alkaline extraction, and the modification was performed with CTAC at 25 %w. Adsorption tests were performed following a multifactorial experimental design 33, placi… Show more

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Cited by 4 publications
(2 citation statements)
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“…Figure 10B illustrates a decrease in adsorption capacity with the increase in bioadsorbent dose, contrary to the expected behavior where an increase in the dose typically leads to more active sites on the material's surface [8,18,22]. However, this observed behavior may be attributed to the following factors: (1) rapid saturation of the bioadsorbent, resulting in a decrease in adsorption capacity; (2) at higher bioadsorbent doses, there may be enhanced interaction between adsorbent particles, leading to excessive agglomeration and blocking of adsorption sites, thereby limiting the diffusion of the adsorbate from the solution to the adsorption sites and negatively affecting adsorption capacity; and (3) with an increase in the adsorbent quantity, the dye concentration in the solution may become relatively low compared with the present bioadsorbent, diminishing the adsorption capacity [58]. Figure 10B illustrates a decrease in adsorption capacity with the increase in bioadsorbent dose, contrary to the expected behavior where an increase in the dose typically leads to more active sites on the surface [8,18,22].…”
Section: Bioadsorbent Dose Variationmentioning
confidence: 99%
“…Figure 10B illustrates a decrease in adsorption capacity with the increase in bioadsorbent dose, contrary to the expected behavior where an increase in the dose typically leads to more active sites on the material's surface [8,18,22]. However, this observed behavior may be attributed to the following factors: (1) rapid saturation of the bioadsorbent, resulting in a decrease in adsorption capacity; (2) at higher bioadsorbent doses, there may be enhanced interaction between adsorbent particles, leading to excessive agglomeration and blocking of adsorption sites, thereby limiting the diffusion of the adsorbate from the solution to the adsorption sites and negatively affecting adsorption capacity; and (3) with an increase in the adsorbent quantity, the dye concentration in the solution may become relatively low compared with the present bioadsorbent, diminishing the adsorption capacity [58]. Figure 10B illustrates a decrease in adsorption capacity with the increase in bioadsorbent dose, contrary to the expected behavior where an increase in the dose typically leads to more active sites on the surface [8,18,22].…”
Section: Bioadsorbent Dose Variationmentioning
confidence: 99%
“…Among these, adsorption is a technology commonly used for dye removal due to its low implementation cost, easy handling, high effectiveness, contaminant recovery, and material reusability [19,20]. For this reason, various natural resources have been studied for their use as adsorbent materials [21], such as yucca screening [22], mesoporous Ziziphus Spina-Christi [23], commercial granular materials, the biomass from rice husks [24], wheat straw residues [25], coconut and peanut shells [26], modified cellulose based on straw residues [27], pine needle waste [28], orange peels [29], and olive stones [30], among others. Among all the materials used, activated carbon is one of the most applied and effective but more expensive materials [31,32].…”
Section: Introductionmentioning
confidence: 99%