淀粉-壳聚糖生物聚合物共混物对铁和硫酸盐离子的生态吸附

Rahma Boughanmi, Christine Steinbach, Niklas Gerlach, Marina Oelmann, Christoph Beutner, Simona Schwarz
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摘要

提供不含铁等重金属离子和硫酸盐等氧离子的安全饮用水已成为一个全球性问题。淀粉作为一种广泛使用的廉价生物材料,在各种科学研究中已经证明了其对水中重金属离子的吸附能力,但吸附率较低。因此,本文旨在制备一种以淀粉-壳聚糖共混物为基础的生物聚合物,以提高淀粉的吸附效率。采用低分子壳聚糖(ch60)和高分子壳聚糖(ch4000)两种壳聚糖对马铃薯淀粉进行改性。以马铃薯淀粉为原料制备了纳米马铃薯淀粉(n.ps),并对其进行壳聚糖改性。对样品的表面性能、形貌、粒度和结构进行了分析。此外,通过zeta电位和电荷密度对样品进行了研究,以确定吸附剂表面的电荷。此外,采用伪一阶(PFO)和伪二阶(PSO)表征了吸附动力学。采用Langmuir、Sips和Dubinin-Radushkevich吸附模型拟合了Fe2+/3+和SO42 -的吸附等温线。FeSO4溶液对Fe2+/3+的最大吸附量为:n.ps &为115 mg/g;Ch4000, 90 mg/g用于ps &Ch4000, 80mg /g用于n.p ps &Ch60和61 mg/g的ps &ch60。同样,对于SO42−,n.ps &Ch4000, 155 mg/g用于n.ps &Ch60, 137 mg/g的ps &Ch4000, ps &为97 mg/g;ch60。
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Ecological Sorption of Iron and Sulfate Ions onto Starch and Chitosan Biopolymer Blend
Providing safe drinking water free of heavy metal ions like iron and oxyanions like sulfate has become a worldwide issue. Starch, as one of the widely cheapest and available biomaterials, has demonstrated its capability to adsorb heavy metal ions from water in various scientific research, but in low adsorption rates. Therefore, this paper aims to prepare a biopolymer based on a starch–chitosan blend to raise the adsorption efficiency of starch. Two types of chitosan were used to modify potato starch (ps): low molecular chitosan (ch60) and high molecular chitosan (ch4000). Nano potato starch (n.ps) was prepared from potato starch and was also modified with both chitosans. The surface property, the morphology, the particle size, and the structure of the samples were analyzed. Moreover, the investigation of the samples by the zeta potential and charge density were evaluated to determine the charge of the adsorbents’ surface. Furthermore, the pseudo first order (PFO) and pseudo second order (PSO) were employed to examine the adsorption kinetic. The adsorption isotherms of Fe2+/3+ and SO42− were fitted employing Langmuir, Sips, and Dubinin-Radushkevich adsorption models. The maximum achieved sorption capacities from the FeSO4 solution for Fe2+/3+ were as follows: 115 mg/g for n.ps & ch4000, 90 mg/g for ps & ch4000, 80 mg/g for n.ps & ch60, and 61 mg/g for ps & ch60. Similarly, for SO42−, it was 192 mg/g for n.ps & ch4000, 155 mg/g for n.ps & ch60, 137 mg/g for ps & ch4000, and 97 mg/g for ps & ch60.
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