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Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

Postal Subscription Code 80-973

2018 Impact Factor: 3.883

Front. Environ. Sci. Eng.    2019, Vol. 13 Issue (2) : 23    https://doi.org/10.1007/s11783-019-1103-x
RESEARCH ARTICLE
Comparison of CNT-PVA membrane and commercial polymeric membranes in treatment of emulsified oily wastewater
Gang Yi, Xinfei Fan, Xie Quan(), Shuo Chen, Hongtao Yu
Key Laboratory of Industrial Ecology and Environmental Engineering (Ministry of Education), School of Environmental Science and Technology, Dalian University of Technology, Dalian 116024, China
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Abstract

CNT-PVA membrane was fabricated and compared with polymeric membranes.

The separation performance was evaluated by homemade and cutting fluid emulsions.

The three membranes show similar oil retention rates.

CNT-PVA membranes have higher permeation fluxes compared with polymeric membranes.

CNT-PVA membrane shows higher fouling resistance.

Membrane separation is an attractive technique for removal of emulsified oily wastewater. However, polymeric membranes which dominate the current market usually suffer from severe membrane fouling. Therefore, membranes with high fouling resistance are imperative to treat emulsified oily wastewater. In this study, carbon nanotube-polyvinyl alcohol (CNT-PVA) membrane was fabricated. And its separation performance for emulsified oily wastewater was compared with two commercial polymeric membranes (PVDF membrane and PES membrane) by filtration of two homemade emulsions and one cutting fluid emulsion. The results show that these membranes have similar oil retention efficiencies for the three emulsions. Whereas, the permeation flux of CNT-PVA membrane is 1.60 to 3.09 times of PVDF membrane and 1.41 to 11.4 times of PES membrane, respectively. Moreover, after five consecutive operation circles of filtration process and back flush, CNT-PVA membrane can recover 62.3% to 72.9% of its initial pure water flux. However, the pure water flux recovery rates are only 24.1% to 35.3% for PVDF membrane and 6.0% to 26.3% for PES membrane, respectively. Therefore, CNT-PVA membrane are more resistant to oil fouling compared with the two polymeric membranes, showing superior potential in treatment of emulsified oily wastewater.

Keywords Oily wastewater      Microfiltration      Carbon nanotube membrane      Commercial polymeric membrane     
Corresponding Author(s): Xie Quan   
Issue Date: 15 March 2019
 Cite this article:   
Gang Yi,Xinfei Fan,Xie Quan, et al. Comparison of CNT-PVA membrane and commercial polymeric membranes in treatment of emulsified oily wastewater[J]. Front. Environ. Sci. Eng., 2019, 13(2): 23.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-019-1103-x
https://academic.hep.com.cn/fese/EN/Y2019/V13/I2/23
Oil content Surfactant Mean size Zeta potential
Hexadecane 1:1000(V/V) SDS, 0.02 g/L ~300 nm -45 mV
Soybean oil 1:1000(V/V) SDS, 0.02 g/L ~350 nm -42 mV
Mobil 1:1000(m/m) / ~240 nm -71 mV
Tab.1  The properties of the prepared O/W emulsion
Fig.1  Membrane model (a) and filtration tests system in a dead-end mode (b).
Fig.2  Digital  images of CNT-PVA membrane (a), PVDF membrane (b) and PES membrane (c). SEM images of the surface of CNT-PVA membrane (d), PVDF membrane (e) and PES membrane (f).
Fig.3  Pore  size distributions (a) and pure water permeation fluxes (b) of CNT-PVA membrane, PVDF membrane and PES membrane.
Fig.4  Pure  water contact angles of CNT membrane (a), PVDF membrane (b) and PES membrane (c).
Fig.5  Comparison  of oil concentration in filtrate and oil retention rate of CNT-PVA membrane, PVDF membrane and PES membrane.
Fig.6  Permeation  flux as a function of running time of CNT-PVA membrane, PVDF membrane and PES membrane for filtration of hexadecane-in-water emulsion (a), soybean oil-in-water emulsion (b) and Mobil emulsion (c).
Fig.7  SEM  images of the surfaces of CNT-PVA membrane (a), PVDF membrane (b) and PES membrane (c) before (0) and after emulsion filtration: Hexadecane-in-water emulsion (1), soybean oil-in-water emulsion (2) and Mobil emulsion (3).
Fig.8  Underwater oil contact angle of CNT-PVA  membrane (a), PVDF membrane (b) and PES membrane (c).
Fig.9  Change of permeation flux in the filtration of hexadecane-in-water emulsion (a), soybean oil-in-water emulsion (b) and Mobil emulsion (c). (In every circle, run for 30 min at 0.01 MPa and then back flush for 2 min under 0.02 MPa).
Fig.10  Normalized pure water flux after back flush in the filtration of hexadecane-in-water emulsion (a), soybean oil-in-water emulsion (b) and Mobil emulsion (c).
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