Cross-stacked super-aligned carbon nanotube/activated carbon composite electrodes for efficient water purification via capacitive deionization enhanced ultrafiltration

Min Li , Shuai Liang , Yang Wu , Meiyue Yang , Xia Huang

Front. Environ. Sci. Eng. ›› 2020, Vol. 14 ›› Issue (6) : 107

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Front. Environ. Sci. Eng. ›› 2020, Vol. 14 ›› Issue (6) : 107 DOI: 10.1007/s11783-020-1286-1
RESEARCH ARTICLE
RESEARCH ARTICLE

Cross-stacked super-aligned carbon nanotube/activated carbon composite electrodes for efficient water purification via capacitive deionization enhanced ultrafiltration

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Abstract

• A high-performance electrode was prepared with super-aligned carbon nanotubes.

• SACNT/AC electrode achieved a ~100% increase in desalination capacity and rate.

• SACNT/AC electrode achieved a ~26% increase in charge efficiency.

• CUF process with SACNT/AC achieved an up to 2.43-fold fouling reduction.

• SACNT/AC imparts overall improved water purification efficiency.

The practical application of the capacitive deionization (CDI) enhanced ultrafiltration (CUF) technology is hampered due to low performance of electrodes. The current study demonstrated a novel super-aligned carbon nanotube (SACNT)/activated carbon (AC) composite electrode, which was prepared through coating AC on a cross-stacked SACNT film. The desalination capability and water purification performance of the prepared electrode were systematically investigated at different applied voltages (0.8–1.2 V) with a CDI system and a CUF system, respectively. In the CDI tests, as compared with the control AC electrode, the SACNT/AC electrode achieved an approximately 100% increase in both maximum salt adsorption capacity and average salt adsorption rate under all the applied voltage conditions, demonstrating a superior desalination capability. Meanwhile, a conspicuous increase by an average of ~26% in charge efficiency was also achieved at all the voltages. In the CUF tests, as compared with the control run at 0 V, the treatment runs at 0.8, 1.0, and 1.2 V achieved a 2.40-fold, 2.08-fold, and 2.43-fold reduction in membrane fouling (calculated according to the final transmembrane pressure (TMP) data at the end of every purification stage), respectively. The average TMP increasing rates at 0.8, 1.0, and 1.2 V were also roughly two times smaller than that at 0 V, indicating a dramatical reduction of membrane fouling. The SACNT/AC electrode also maintained its superior desalination capability in the CUF process, resulting in an overall improved water purification efficiency.

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Keywords

Carbon nanotube / Super aligned / Conductive membrane / Capacitive deionization / Ultrafiltration / Desalination

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Min Li, Shuai Liang, Yang Wu, Meiyue Yang, Xia Huang. Cross-stacked super-aligned carbon nanotube/activated carbon composite electrodes for efficient water purification via capacitive deionization enhanced ultrafiltration. Front. Environ. Sci. Eng., 2020, 14(6): 107 DOI:10.1007/s11783-020-1286-1

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References

[1]

Caldera U, Breyer C (2017). Learning curve for seawater reverse osmosis desalination plants: Capital cost trend of the past, present, and future. Water Resources Research, 53(12): 10523–10538

[2]

Chen G, Ma Z, Xiao K, Wang X, Liang S, Huang X (2019). Hierarchically textured superhydrophilic polyvinylidene fluoride membrane via nanocasting and post-fabrication grafting of surface-tailored silica nanoparticles. Environmental Science. Nano, 6(12): 3579–3589

[3]

Choi J, Dorji P, Shon H K, Hong S (2019). Applications of capacitive deionization: Desalination, softening, selective removal, and energy efficiency. Desalination, 449: 118–130

[4]

Guo X, Li C, Li C, Wei T, Tong L, Shao H, Zhou Q, Wang L, Liao Y (2019). G-CNTs/PVDF mixed matrix membranes with improved antifouling properties and filtration performance. Frontiers of Environmental Science & Engineering, 13(6): 81

[5]

Hassanvand A, Chen G Q, Webley P A, Kentish S E (2018). A comparison of multicomponent electrosorption in capacitive deionization and membrane capacitive deionization. Water Research, 131: 100–109

[6]

Hu C Z, Li M Q, Sun J Q, Liu R P, Liu H J, Qu J H (2019). NOM fouling resistance in response to electric field during electro-ultrafiltration: Significance of molecular polarity and weight. Journal of Colloid and Interface Science, 539: 11–18

[7]

Huotari H M, Trägårdh G, Huisman I H (1999). Crossflow membrane filtration enhanced by an external DC electric field: A review. Chemical Engineering Research & Design, 77(5): 461–468

[8]

Jones K L, O’Melia C R (2000). Protein and humic acid adsorption onto hydrophilic membrane surfaces: Effects of pH and ionic strength. Journal of Membrane Science, 165(1): 31–46

[9]

Jung Y T, Narayanan N C, Cheng Y L (2018). Cost comparison of centralized and decentralized wastewater management systems using optimization model. Journal of Environmental Management, 213: 90–97

[10]

Kamali M, Suhas D P, Costa M E, Capela I, Aminabhavi T M (2019). Sustainability considerations in membrane-based technologies for industrial effluents treatment. Chemical Engineering Journal, 368: 474–494

[11]

Li Y, Chen N, Li Z, Shao H, Qu L (2020). Frontiers of carbon materials as capacitive deionization electrodes. Dalton Transactions (Cambridge, England: 2003), 49, 5006–5014

[12]

Liang S, Li M, Cao J, Zuo K, Bian Y, Xiao K, Huang X (2019). Integrated ultrafiltration–capacitive-deionization (UCDI) for enhanced antifouling performance and synchronous removal of organic matter and salts. Separation and Purification Technology, 226: 146–153

[13]

Liang S, Xiao K, Wu J, Liang P, Huang X (2014). Mechanism of membrane filterability amelioration via tuning mixed liquor property by pre-ozonation. Journal of Membrane Science, 454: 111–118

[14]

Liang S, Xiao K, Zhang S, Ma Z, Lu P, Wang H, Huang X (2018). A facile approach to fabrication of superhydrophilic ultrafiltration membranes with surface-tailored nanoparticles. Separation and Purification Technology, 203: 251–259

[15]

Lin S (2020). Energy efficiency of desalination: Fundamental insights from intuitive interpretation. Environmental Science & Technology, 54(1): 76–84

[16]

Liu K, Sun Y, Chen L, Feng C, Feng X, Jiang K, Zhao Y, Fan S (2008). Controlled growth of super-aligned carbon nanotube arrays for spinning continuous unidirectional sheets with tunable physical properties. Nano Letters, 8(2): 700–705

[17]

Liu K, Sun Y, Liu P, Lin X, Fan S, Jiang K (2011). Cross-stacked superaligned carbon nanotube films for transparent and stretchable conductors. Advanced Functional Materials, 21(14): 2721–2728

[18]

Liu L, Lopez E, Dueñas-Osorio L, Stadler L, Xie Y, Alvarez P J J, Li Q (2020). The importance of system configuration for distributed direct potable water reuse. Nature Sustainability,

[19]

Lu J Y, Wang X M, Liu H Q, Yu H Q, Li W W (2019). Optimizing operation of municipal wastewater treatment plants in China: The remaining barriers and future implications. Environment International, 129: 273–278

[20]

Ma J X, Dai R B, Chen M, Khan S J, Wang Z W (2018). Applications of membrane bioreactors for water reclamation: Micropollutant removal, mechanisms and perspectives. Bioresource Technology, 269: 532–543

[21]

Ma Z, Zhang S, Chen G, Xiao K, Li M, Gao Y, Liang S, Huang X (2019). Superhydrophilic and oleophobic membrane functionalized with heterogeneously tailored two-dimensional layered double hydroxide nanosheets for antifouling. Journal of Membrane Science, 577: 165–175

[22]

Mekonnen M M, Hoekstra A Y (2016). Four billion people facing severe water scarcity. Science Advances, 2(2): e1500323

[23]

Omosa I B, Wang H T, Cheng S P, Li F T (2012). Sustainable tertiary wastewater treatment is required for water resources pollution control in Africa. Environmental Science & Technology, 46(13): 7065–7066

[24]

Patel S K, Qin M, Walker W S, Elimelech M (2020). Energy efficiency of electro-driven brackish water desalination: Electrodialysis significantly outperforms membrane capacitive deionization. Environmental Science & Technology, 54(6): 3663–3677

[25]

Porada S, Zhao R, Van Der Wal A, Presser V, Biesheuvel P M (2013). Review on the science and technology of water desalination by capacitive deionization. Progress in Materials Science, 58(8): 1388–1442

[26]

Suss M E, Porada S, Sun X, Biesheuvel P M, Yoon J, Presser V (2015). Water desalination via capacitive deionization: what is it and what can we expect from it? Energy & Environmental Science, 8(8): 2296–2319

[27]

Tay M F, Liu C, Cornelissen E R, Wu B, Chong T H (2018). The feasibility of nanofiltration membrane bioreactor (NF-MBR) + reverse osmosis (RO) process for water reclamation: Comparison with ultrafiltration membrane bioreactor (UF-MBR) + RO process. Water Research, 129: 180–189

[28]

Wang L, Lin S H (2019). Theoretical framework for designing a desalination plant based on membrane capacitive deionization. Water Research, 158: 359–369

[29]

Wang S, Liang S, Liang P, Zhang X, Sun J, Wu S, Huang X (2015). In-situ combined dual-layer CNT/PVDF membrane for electrically-enhanced fouling resistance. Journal of Membrane Science, 491: 37–44

[30]

Wang Y, Lu D, Wang F, Zhang D X, Zhong J, Liang B H, Gui X C, Sun L (2020). A new strategy to prepare carbon nanotube thin film by the combination of top-down and bottom-up approaches. Carbon, 161: 563–569

[31]

Weigert T, Altmann J, Ripperger S (1999). Crossflow electrofiltration in pilot scale. Journal of Membrane Science, 159(1–2): 253–262

[32]

Wu G, Chen Y, Zhan H, Chen H T, Lin J H, Wang J N, Wan L Q, Huang F R (2020). Ultrathin and flexible carbon nanotube/polymer composite films with excellent mechanical strength and electromagnetic interference shielding. Carbon, 158: 472–480

[33]

Xiao K, Liang S, Wang X, Chen C, Huang X (2019). Current state and challenges of full-scale membrane bioreactor applications: A critical review. Bioresource Technology, 271: 473–481

[34]

Xu X, Tan H, Wang Z, Wang C, Pan L, Kaneti Y V, Yang T, Yamauchi Y (2019). Extraordinary capacitive deionization performance of highly-ordered mesoporous carbon nano-polyhedra for brackish water desalination. Environmental Science. Nano, 6(3): 981–989

[35]

Yan X, Xiao K, Liang S, Lei T, Liang P, Xue T, Yu K, Guan J, Huang X (2015). Hydraulic optimization of membrane bioreactor via baffle modification using computational fluid dynamics. Bioresource Technology, 175: 633–637

[36]

Zhang C Y, He D, Ma J X, Tang W W, Waite T D (2018). Faradaic reactions in capacitive deionization (CDI) - problems and possibilities: A review. Water Research, 128: 314–330

[37]

Zhang X B, Jiang K L, Feng C, Liu P, Zhang L, Kong J, Zhang T H, Li Q Q, Fan S S (2006). Spinning and processing continuous yarns from 4-inch wafer scale super-aligned carbon nanotube arrays. Advanced Materials, 18(12): 1505–1510

[38]

Zhao F, Ma Z, Xiao K, Xiang C, Wang H, Huang X, Liang S (2018). Hierarchically textured superhydrophobic polyvinylidene fluoride membrane fabricated via nanocasting for enhanced membrane distillation performance. Desalination, 443: 228–236

[39]

Zhao X, Wu Y, Zhang X, Tong X, Yu T, Wang Y, Ikuno N, Ishii K, Hu H (2019). Ozonation as an efficient pretreatment method to alleviate reverse osmosis membrane fouling caused by complexes of humic acid and calcium ion. Frontiers of Environmental Science & Engineering, 13(4): 55

[40]

Zhu X B, Dudchenko A V, Khor C M, He X, Ramon G Z, Jassby D (2018). Field-induced redistribution of surfactants at the oil/water interface reduces membrane fouling on electrically conducting carbon nanotube UF membranes. Environmental Science & Technology, 52(20): 11591–11600

[41]

Zhu Z, Peng D, Wang H (2019). Seawater desalination in China: An overview. Journal of Water Reuse and Desalination, 9(2): 115–132

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