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Rejection of HA and antifouling performance with 3D GO-CNT composite membrane |
LIU Zhong-tao1,2, GUO Zhen-hua1, HU Cheng-zhi2,3, MA Ying-li1, SUN Jing-qiu2,3 |
1. School of Energy and Environment Engineering, Hebei University of Technology, Tianjin 300401, China; 2. Key Laboratory of Drinking Water Science and Technology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China; 3. University of Chinese Academy of Sciences, Beijing 100049, China |
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Abstract GO-CNT three-dimensional composite membrane was fabricated in order to achieve a high water flux and to mitigate humic acid (HA) fouling. The results exhibited that GO-CNT membranes had a rougher surface than GO membrane. The CNTs were intercalated in GO lamellas uniformity, constituting a 3D network structure. GO-20%CNT membrane with the loading of 30μg/cm2 achieved a rejection of over 90% on HA, and its water flux was improved to 2times higher than that of GO membrane. In acidic condition, the size of HA increased due to molecular aggregation, and the surface negative charge decreased due to protonation. So the rejection of HA during filtration through GO-CNT composite membranes improved but water flux decreased. The compression of electric double layer caused by the increased ion strength declined the Donnan effect, the results showed that the HA rejection of GO-CNT composite membrane decreased from 90.2% to 31.9%. The pure water flux of 3D GO-CNT composite membrane was decreased by 10.95% after filtering HA for 1hour, and the flux recovery rate was 99.68% after washing for 1hour. The composite membrane exhibited an excellent antifouling performance with flux recovery rate of 6.18%, which was much higher than reported GO membrane.
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Received: 12 May 2017
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[1] |
李方,孟蝶.氧化石墨烯:膜科学的机遇与挑战[J]. 膜科学与技术, 2015,(6):106-112.
|
[2] |
Han Y, Xu Z, Gao C. Ultrathin Graphene Nanofiltration Membrane for Water Purification[J]. Advanced Functional Materials. 2013,23(29):3693-3700.
|
[3] |
Cao K, Jiang Z, Zhao J, et al. Enhanced water permeation through sodium alginate membranes by incorporating graphene oxides[J]. Journal of Membrane Science, 2014,469:272-283.
|
[4] |
Lee W, Lee J U, Jung B M, et al. Simultaneous enhancement of mechanical, electrical and thermal properties of graphene oxide paper by embedding dopamine[J]. Carbon, 2013,65:296-304.
|
[5] |
Chae S R, Hotze E M, Badireddy A R, et al. Environmental implications and applications of carbon nanomaterials in water treatment[J]. Water Science and Technology, 2013,67(11):2582-2586.
|
[6] |
Zhang L, Lu Y, Liu Y, et al. High flux MWCNTs-interlinked GO hybrid membranes survived in cross-flow filtration for the treatment of strontium-containing wastewater[J]. Journal of Hazardous Materials, 2016,320:187-193.
|
[7] |
Gao S J, Qin H, Liu P, et al. SWCNT-intercalated GO ultrathin films for ultrafast separation of molecules[J]. Journal of Materials Chemistry, 2015,3(12):6649-6654.
|
[8] |
Cho J, Amy G, Pellegrino J. Membrane filtration of natural organic matter:factors and mechanisms affecting rejection and flux decline with charged ultrafiltration (UF) membrane[J]. Journal of Membrane Science, 2000,164(1):89-110.
|
[9] |
吴俊青,俞科静,钱坤.不同比例碳纳米管/石墨烯杂化材料的制备及性能[J]. 功能材料, 2015,(16):16133-16137.
|
[10] |
Phao N, Nxumalo E N, Mamba B B, et al. A nitrogen-doped carbon nanotube enhanced polyethersulfone membrane system for water treatment[J]. Physics and Chemistry of the Earth., 2013,66:148-156.
|
[11] |
Zhu L, Zhu L, Jiang J, et al. Hydrophilic and anti-fouling polyethersulfone ultrafiltration membranes with poly (2-hydroxyethyl methacrylate) grafted silica nanoparticles as additive[J]. Journal of Membrane Science, 2014,451:157-168.
|
[12] |
Hummers W S, Offeman R E. Preparation of Graphitic Oxide[J]. Journal of the American Chemical Society, 1958,80(6):1339.
|
[13] |
Verdejo R, Lamoriniere S, Cottam B, et al. Removal of oxidation debris from multi-walled carbon nanotubes.[J]. Chemical Communications, 2007,43(5):513-515.
|
[14] |
Yu P T, Paul D R, Tai S C. Free-standing graphene oxide thin films assembled by a pressurized ultrafiltration method for dehydration of ethanol[J]. Journal of Membrane Science, 2014, 458(9):199-208.
|
[15] |
Yang D, Velamakanni A, Bozoklu G, et al. Chemical analysis of graphene oxide films after heat and chemical treatments by X-ray photoelectron and Micro-Raman spectroscopy[J]. Carbon, 2009,47(1):145-152.
|
[16] |
Hung W, Tsou C, De Guzman M, et al. Cross-Linking with Diamine Monomers To Prepare Composite Graphene OxideFramework Membranes with Varying d-Spacing[J]. Chemistry of Materials, 2014,26(9):2983-2990.
|
[17] |
Wang Q, Gao B, Wang Y, et al. Effect of pH on humic acid removal performance in coagulation-ultrafiltration process and the subsequent effects on chlorine decay[J]. Separation and Purification Technology, 2011,80(3):549-555.
|
[18] |
Salehi E, Madaeni S S. Adsorption of humic acid onto ultrafiltration membranes in the presence of protein and metal ions.[J]. Desalination. 2010,263(1-3):139-145.
|
[19] |
赵媛媛,王志,王纪孝,等.含腐殖酸类有机物模拟废水超滤过程研究[J]. 膜科学与技术, 2006,(1):42-46.
|
[20] |
黄健,舒增年,张四海.亲水荷电超滤膜的制备及对腐殖酸的分离性能[J]. 中国环境科学, 2014,34(11):2831-2837.
|
[21] |
Lee J, Ye Y, Ward A J, et al. High flux and high selectivity carbon nanotube composite membranes for natural organic matter removal[J]. Separation and Purification Technology, 2016,163:109-119.
|
|
|
|