Position：Home >> Abstract

Study on dye desalination by positively charged nanofiltration membrane
Authors： LI Xia1,2, YUE Xianyang1,2, YANG Hongying1,2, WANG Qing1,2, MEI Songlin1, ZHANG Qiushi1, WU Jianchao1, WU Wanhua1
Units： Zhongyuan University of Technology, Zhengzhou 450007, China; 2Henan Collaborative Innovation Center of Textile and Garment Industry, Zhengzhou 450007, China
KeyWords： nanofiltration membrane; positively charged; dye desalination; antifouling
ClassificationCode：TQ028.8
year,volume(issue):pagination： 2020, 40(5):62-69

Abstract：

 The self-made positively charged guanidine nanofiltration membrane was used for dye desalination. Results showed that the retention rate of congo red and reactive blue 19 with higher molecular weight was higher than 95% and 90%, respectively, followed by methyl orange with lower molecular weight. The retention of NaCl and Na2SO4 by the membrane is low, which indicated that the membrane can effectively separate dye and salt. The concentration of dyes and salts has an important effect on the separation performance of the membrane. With the increase of dye concentration, the membrane flux decreased, while the retention of congo red and NaCl changed little, the retention of methyl orange, reactive blue 19 and Na2SO4 increased slightly. The increase of inorganic salt concentration had little effect on the membrane flux, but led to the decrease of the rejections of dye and salt. For three simulated pollution systems, including congo red-NaCl, methyl orange-NaCl and reactive Blue 19-NaCl, after four pollution-cleaning cycles, all of the membrane showed relatively high fluxes, which demonstrated that the membrane had satisfactory antifouling performance. Furthermore, the membrane maintained good stability in the long-term filtration operation of methyl orange-NaCl system for 24 h.

Funds：
中国纺织工业联合会科技指导性计划项目（2018069）；河南省科技攻关项目（182102310660）；河南省高等学校重点科研项目（20B610008）；河南省质量技术监督局科技计划项目(2019NQ05)

AuthorIntro：
李霞（1985-），女，河南新乡，博士，讲师，从事聚合物膜的制备与应用研究，E-mail：lixiapiaoyi@163.com

Reference：

[1] Makhetha T A, Moutloali R M, Antifouling properties of Cu (tpa) @GO/PES composite membranes and selective dye rejection [J]. J Membr Sci, 2018, 554: 195-210.
[2] Gao H, Sun Y, Zhou J, et al. Mussel-inspired synthesis of polydopaminefunctionalized graphene hydrogel as reusable adsorbents for water purification [J]. ACS Appl Mater Interfaces, 2013, 5: 425-432.
[3] Lin J, Ye W, Zeng H, et al. Fractionation of direct dyes and salts in aqueous solution using loose nanofiltration membranes [J]. J Membr Sci, 2015, 477: 183-193.
[4] 张华宇, 罗芳颖, 江婷婷等, La/Y掺杂二氧化硅膜的制备及其对染料废水的分离性能研究[J]. 膜科学与技术, 2018, 38 (4): 113-119.
[5] Mohammad A W, Teow Y H, Ang W L, et al. Nanofiltration membranes review: Recent advances and future prospects [J]. Desalination, 2015, 356: 226-254.
[6] Cao X L, Yan Y N, Zhou F Y, et al. Tailoring nanofiltration membranes for effective removing dye intermediates in complex dye-wastewater [J]. J Membr Sci, 2020, 595: 117476.
[7] Xu P, Wang W, Qian X M, et al. Positive charged PEI-TMC composite nanofiltration membrane for separation of Li+ and Mg2+ from brine with high Mg2+/Li+ ratio [J]. Desalination, 2019, 449: 57-68.
[8] Li W, Shi C, Zhou A, et al. A positively charged composite nanofiltration membrane modified by EDTA for LiCl/MgCl2 separation [J]. Sep Purif Technol, 2017, 186: 233-242.
[9] Zhong P S, Widjojo N, Chung T S, et al. Positively charged nanofiltration (NF) membranes via UV grafting on sulfonated polyphenylenesulfone (sPPSU) for effective removal of textile dyes from wastewater [J]. J Membr Sci, 2012, 417-418: 52-60.
[10] Wei X Z, Wang S X, Shi Y Y, et al. Application of positively charged composite hollow-fiber nanofiltration membranes for dye purification [J]. Ind Eng Chem Res, 2014, 53 (36): 14036-14045.
[11] Zheng Y P, Yao G H, Cheng Q B, et al. Positively charged thin-film composite hollow fiber nanofiltration membrane for the removal of cationic dyes through submerged filtration [J]. Desalination, 2013, 328: 42–50.
[12] 韩子龙, 李俊俊, 叶谦等, N,N′-双（3-氨丙基）甲胺为单体的荷正电复合纳滤膜的制备与表征 [J]. 膜科学与技术, 2016, 36 (4): 24-29.
[13] Li X, Cao Y M, Yu H J, et al. A novel composite nanofiltration membrane prepared with PHGH and TMC by interfacial polymerization [J]. J Membr Sci, 2014, 466: 82-91.
[14] AlVentos-Delara E, Barredo-Damas S, Zuriaga-Agustf E, et al. Ultrafiltration ceramic membrane performance during the treatment of model solutions containing dye and salt [J]. Sep Purif Technol, 2014, 129(129): 96-105.
[15] Sójka-Ledakowicz J, Koprowski T, Machnowski W, et al. Membrane filtration of textile dyehouse wastewater for technological water reuse [J]. Desalination, 1998, 119 (1-3): 1-10.
[16] Wang L, Wang N X, Zhang GJ, et al. Covalent crosslinked assembly of tubular ceramic-based multilayer nanofiltration membranes for dye desalination [J]. Aiche J, 2013, 59 (10): 3834-3842.
[17] Kiln T H, Park C, Kim S. Water recycling from desalination and purification process of reactive dye manufacturing industry by combined membrane filtration [J]. J Clean Prod, 2005, 13(8): 779-786.
[18] Wei X, Kong X, Sun C, et al. Characterization and application of a thin-film composition nanofiltration hollow fiber membrane for dye desalination and concentration [J]. Chem Eng J, 2013, 223 (5): 172-182.
[19] Wang X L, Zhang C, Ouyang P, The possibility of separating saccharides from a NaCl solution by using nanofiltration in diafiltration mode [J]. J Membr Sci, 2002, 204(1-2): 271-281.

Service：
【Download】【Collect】

《膜科学与技术》编辑部 Address: Bluestar building, 19 east beisanhuan road, chaoyang district, Beijing; 100029 Postal code; Telephone：010-80492417/010-80485372; Fax：010-80485372 ; Email：mkxyjs@163.com

京公网安备11011302000819号