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静电纺丝纳米纤维膜对多环芳烃的吸附:吸附动力学和机制。

Sorption of polycyclic aromatic hydrocarbons on electrospun nanofibrous membranes: sorption kinetics and mechanism.

机构信息

State Key Laboratory of Water Environment Simulation, School of Environment, Beijing Normal University, Beijing 100875, PR China.

出版信息

J Hazard Mater. 2011 Sep 15;192(3):1409-17. doi: 10.1016/j.jhazmat.2011.06.055. Epub 2011 Jun 24.

Abstract

Five types of nanofibrous membranes were prepared by electrospinning poly(ε-caprolactone) (PCL), poly(D,L-lactide) (PDLLA), poly(lactide-co-caprolactone) (P(LA/CL)), poly(D,L-lactide-co-glycolide) (PDLGA) and methoxy polyethylene glycol-poly(lactide-co-glycolide) (MPEG-PLGA), respectively. These electrospun nanofibrous membranes (ENFMs) were used to adsorb anthracene (ANT), benz[a]anthracene (BaA) and benzo[a]pyrene (BaP) from aqueous solution, and the sorption kinetics and isotherms of these PAHs on the five ENFMs were investigated. The pseudo-second-order model (PSOM) can well describe the sorption kinetics of the three PAHs on five ENFMs, and the partition-adsorption model (PAM) can interpret the sorption processes of PAHs on the ENFMs. PCL ENFMs, which had the largest surface areas (8.57 m(2)g(-1)), exhibited excellent sorption capacity for ANT at over 4112.3 ± 35.5 μg g(-1). Moreover, the hydrophobicity and pore volume of ENFMs significantly affected the sorption kinetics and sorption capacity of the PAHs. The main sorption mechanisms of three PAHs on the PDLLA ENFMs included hydrophobic interactions and pore-filling, while those of PCL, P(LA/CL) and PDLGA ENFMs were dominated by the hydrophobic interactions. The sorption mechanisms of MPEG-PLGA ENFMs primarily included pore-filling, hydrogen bonding interactions and hydrophobic interactions. Additionally, π-π bonding interaction was also deduced to be involved in all of ENFMs sorption systems.

摘要

五种类型的纳米纤维膜通过静电纺丝聚(ε-己内酯)(PCL)、聚(D,L-丙交酯)(PDLLA)、聚(丙交酯-己内酯)(P(LA/CL))、聚(D,L-丙交酯-乙交酯)(PDLGA)和甲氧基聚乙二醇-聚(丙交酯-乙交酯)(MPEG-PLGA)分别准备。这些静电纺纳米纤维膜(ENFMs)用于从水溶液中吸附蒽(ANT)、苯并[a]蒽(BaA)和苯并[a]芘(BaP),并研究了这些 PAHs 在五种 ENFMs 上的吸附动力学和等温线。准二级模型(PSOM)可以很好地描述三种 PAHs 在五种 ENFMs 上的吸附动力学,而分配吸附模型(PAM)可以解释 PAHs 在 ENFMs 上的吸附过程。PCL ENFMs 具有最大的比表面积(8.57 m2g-1),对 ANT 的吸附容量超过 4112.3±35.5μg g-1。此外,ENFMs 的疏水性和孔体积显著影响了 PAHs 的吸附动力学和吸附容量。三种 PAHs 在 PDLLA ENFMs 上的主要吸附机制包括疏水相互作用和孔填充,而在 PCL、P(LA/CL)和 PDLGA ENFMs 上则主要由疏水相互作用主导。MPEG-PLGA ENFMs 的吸附机制主要包括孔填充、氢键相互作用和疏水相互作用。此外,还推断π-π键合相互作用也参与了所有 ENFMs 吸附体系。

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