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用于从水中去除双氯芬酸钠的多孔碳的简便合成

Facile Synthesis of Porous Carbon for the Removal of Diclofenac Sodium from Water.

作者信息

Mao Naqing, Huang Lijin, Shuai Qin

机构信息

Faculty of Materials Science and Chemistry, Engineering Research Center of Nano-Geomaterials of Ministry of Education, China University of Geosciences (Wuhan), 388 Lumo Road, Hongshan District, Wuhan 430074, P. R. China.

出版信息

ACS Omega. 2019 Sep 6;4(12):15051-15060. doi: 10.1021/acsomega.9b01838. eCollection 2019 Sep 17.

DOI:10.1021/acsomega.9b01838
PMID:31552347
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC6751710/
Abstract

In this work, a series of porous carbon materials (PCs) were obtained at different carbonization temperatures (800, 900, 1000, and 1100 °C) by a simple and fast solvent-free method. Moreover, the feasibility of PCs as reliable and efficient adsorbents to capture diclofenac sodium (DCF) from the water was evaluated. Notably, porous carbon (PC) prepared at 1000 °C (PC-1000) was found to be the best candidate for the adsorption of DCF. Remarkably, adsorption equilibrium was achieved within 3 h, which followed a pseudo-second-order kinetic model with a high correlation coefficient ( > 0.994). Furthermore, experimental data obtained from adsorption isotherm indicated that the capture of DCF onto PC-1000 followed the Langmuir adsorption model ( > 0.997), wherein its maximum adsorption capacity was calculated to be 392 mg/g. In addition, based on the results obtained from the zeta potential of PC-1000 under different pH and the adsorbed quantity of DCF along with functional groups created on the surface of PC-1000, electrostatic and H-bonding interactions were proposed as the possible adsorption mechanisms. Due to its high stability and excellent reusability, PC-1000 has been testified as a promising candidate for removing DCF from contaminated water.

摘要

在本工作中,通过一种简单快速的无溶剂方法,在不同碳化温度(800、900、1000和1100℃)下获得了一系列多孔碳材料(PCs)。此外,还评估了PCs作为可靠且高效的吸附剂从水中捕获双氯芬酸钠(DCF)的可行性。值得注意的是,发现在1000℃制备的多孔碳(PC-1000)是吸附DCF的最佳候选材料。显著的是,在3小时内达到了吸附平衡,其遵循具有高相关系数(>0.994)的准二级动力学模型。此外,从吸附等温线获得的实验数据表明,DCF在PC-1000上的捕获遵循朗缪尔吸附模型(>0.997),其中其最大吸附容量经计算为392mg/g。此外,基于在不同pH下PC-1000的zeta电位以及DCF的吸附量和PC-1000表面产生的官能团所获得的结果,提出静电和氢键相互作用作为可能的吸附机制。由于其高稳定性和优异的可重复使用性,PC-1000已被证明是从受污染水中去除DCF的有前景的候选材料。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ae85/6751710/770b6676a673/ao9b01838_0009.jpg
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https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ae85/6751710/4c4e2107600b/ao9b01838_0007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ae85/6751710/e8e8d96170ba/ao9b01838_0008.jpg
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https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ae85/6751710/770b6676a673/ao9b01838_0009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ae85/6751710/d794c380717a/ao9b01838_0002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ae85/6751710/94c202d301aa/ao9b01838_0004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ae85/6751710/8770559d49ae/ao9b01838_0005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ae85/6751710/b0dcbbaca85e/ao9b01838_0006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ae85/6751710/4c4e2107600b/ao9b01838_0007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ae85/6751710/e8e8d96170ba/ao9b01838_0008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ae85/6751710/fbb835b3604c/ao9b01838_0001.jpg
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https://cdn.ncbi.nlm.nih.gov/pmc/blobs/ae85/6751710/770b6676a673/ao9b01838_0009.jpg

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