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了解水中特定微塑料与有毒染料“刚果红”之间的相互作用。

Understanding the interaction between selected microplastics and the toxic dye "Congo red" in water.

作者信息

Nadarajah Kannan, Jeganathan Yanushiya, Ramakrishnan Shri Lasha, Bandala Erick R

机构信息

Department of Agricultural Engineering, Faculty of Agriculture, University of Jaffna, Sri Lanka.

Department of Agricultural Engineering, Faculty of Agriculture, University of Jaffna, Sri Lanka.

出版信息

Chemosphere. 2025 Mar;372:144097. doi: 10.1016/j.chemosphere.2025.144097. Epub 2025 Jan 24.

Abstract

This study thoroughly investigated the adsorption of Congo Red (CR) dye onto various microplastics (MPs), including high-density polyethylene (HDPE), polyvinyl chloride (PVC), low-density polyethylene (LDPE), polypropylene (PP) and polyethylene terephthalate (PET). Initial adsorption capacities (q) revealed that HDPE had the highest value (21.90 mg/g), followed by PVC (4.2 mg/g), LDPE (3.7 mg/g), PP (3.1 mg/g) and PET (2.8 mg/g). Based on these findings, HDPE and PVC were selected for detailed analysis. Adsorption experiments were conducted under controlled conditions: CR concentration of 100 mg/L, adsorbent dosage of 2 g/L, pH of 5, and temperature of 303 K. Isotherm studies indicated that HDPE followed the Freundlich model (R - 0.99), while PVC was best described by the Redlich-Peterson model (R - 0.97). Kinetic analysis showed that HDPE adhered to the Bangham model (reliable ((R = 0.9267, 0.950, 0.988, and 0.988) R values obtained for all the concentrations), highlighting pore-filling mechanisms. The conclusion, supported by FTIR analysis, indicates no significant changes in HDPE's functional groups after the adsorption. In contrast, PVC followed a pseudo-second order kinetic model (reliable R values (0.999, 0.765, 0.956, 0.972) obtained for all the concentrations), suggesting chemisorption, confirmed by FTIR changes in the C-Cl bonds. The optimal pH for adsorption was 5 for HDPE and 4 for PVC. Both processes were exothermic with intraparticle and film diffusion identified as rate-limiting steps. Maximum adsorption capacities (q) were 110.1 mg/g for HDPE and 8.1 mg/g for PVC. Desorption experiments were conducted only for HDPE due to PVC's lower adsorption. The highest desorption for HDPE occurred at pH 4 (5.7 mg/L) with an adsorbent dosage of 2 g/L. This study underscores the dual environmental threat posed by MPs, which not only adsorb organic pollutants like CR but also release them under certain conditions. While this research advances our understanding of MPs as pollutant carriers, future work should focus on their desorption behavior in complex, real-world environments. Further studies on other organic pollutants and microplastic types in real wastewater systems are also recommended.

摘要

本研究深入调查了刚果红(CR)染料在各种微塑料(MPs)上的吸附情况,这些微塑料包括高密度聚乙烯(HDPE)、聚氯乙烯(PVC)、低密度聚乙烯(LDPE)、聚丙烯(PP)和聚对苯二甲酸乙二酯(PET)。初始吸附容量(q)表明,HDPE的值最高(21.90 mg/g),其次是PVC(4.2 mg/g)、LDPE(3.7 mg/g)、PP(3.1 mg/g)和PET(2.8 mg/g)。基于这些发现,选择HDPE和PVC进行详细分析。吸附实验在受控条件下进行:CR浓度为100 mg/L、吸附剂用量为2 g/L、pH值为5、温度为303 K。等温线研究表明,HDPE符合Freundlich模型(R = 0.99),而PVC用Redlich-Peterson模型描述最佳(R = 0.97)。动力学分析表明,HDPE符合Bangham模型(所有浓度下获得的可靠(R = 0.9267、0.950、0.988和0.988)R值),突出了孔隙填充机制。FTIR分析支持的结论表明,吸附后HDPE的官能团没有显著变化。相比之下,PVC遵循准二级动力学模型(所有浓度下获得的可靠R值(0.999、0.765、0.956、0.972)),表明发生了化学吸附,这通过C-Cl键的FTIR变化得到证实。HDPE的最佳吸附pH值为5,PVC为4。两个过程均为放热过程,颗粒内扩散和膜扩散被确定为限速步骤。HDPE的最大吸附容量(q)为110.1 mg/g,PVC为8.1 mg/g。由于PVC的吸附量较低,仅对HDPE进行了解吸实验。HDPE在pH值为4(5.7 mg/L)、吸附剂用量为2 g/L时解吸率最高。本研究强调了微塑料带来的双重环境威胁,微塑料不仅吸附CR等有机污染物,还会在某些条件下释放它们。虽然这项研究增进了我们对微塑料作为污染物载体的理解,但未来的工作应侧重于它们在复杂现实环境中的解吸行为。还建议对实际废水系统中的其他有机污染物和微塑料类型进行进一步研究。

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