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Frontiers of Chemical Science and Engineering

ISSN 2095-0179

ISSN 2095-0187(Online)

CN 11-5981/TQ

Postal Subscription Code 80-969

2018 Impact Factor: 2.809

Front. Chem. Sci. Eng.    2022, Vol. 16 Issue (11) : 1606-1615    https://doi.org/10.1007/s11705-022-2200-0
RESEARCH ARTICLE
Highly hydrophobic oil−water separation membrane: reutilization of waste reverse osmosis membrane
Zihan Liu1,2, Yang Luo1,2, Lianchao Ning1,2, Yong Liu1, Ming Zhang1,2()
1. School of Chemistry and Chemical Engineering, Tianjin University of Technology, Tianjin 300384, China
2. Center of Membrane Materials and Engineering Technology, Tianjin University of Technology, Tianjin 300384, China
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Abstract

The increasing applications of seawater desalination technology have led to the wide usage of polyamide reverse osmosis membranes, resulting in a large number of wasted reverse osmosis membranes. In this work, the base nonwoven layer of the wasted reverse osmosis membrane was successfully modified into the hydrophobic membrane via surface deposition strategy including TiO2 and 1H,1H,2H,2H-perfluorooctyltrichlorosilane (PFOTS), respectively. Various techniques were applied to characterize the obtained membranes, which were then used to separate the oil–water system. The optimally modified membrane displayed good hydrophobicity with a contact angle of 135.2° ± 0.3°, and its oil–water separation performance was as high as 97.8%. After 20 recycle tests, the oil–water separation performance remained more than 96%, which was attributed to the film adhesion of the anchored TiO2 and PFOTS layer on the surface. This work might provide a new avenue for recycling the wasted reverse osmosis membrane used in oily wastewater purification.

Keywords oil–water separation      wasted reverse osmosis membrane      hydrophobic modification     
Corresponding Author(s): Ming Zhang   
Online First Date: 01 November 2022    Issue Date: 13 December 2022
 Cite this article:   
Zihan Liu,Yang Luo,Lianchao Ning, et al. Highly hydrophobic oil−water separation membrane: reutilization of waste reverse osmosis membrane[J]. Front. Chem. Sci. Eng., 2022, 16(11): 1606-1615.
 URL:  
https://academic.hep.com.cn/fcse/EN/10.1007/s11705-022-2200-0
https://academic.hep.com.cn/fcse/EN/Y2022/V16/I11/1606
Fig.1  Schematic illustration of the fabrication process and oil–water separation performance of the modified membrane.
Membrane numberFactor Index
CT/ (g?L–1)t1/ minCP/ (mL?L–1)t2/ min CA/ (° )Fo/ (L·m?2·h?1)Ro/ %
M10.12551.005108.7236.1497.9
M20.125100.5010125.8237.3697.6
M30.125150.7515129.7231.4897.5
M40.25050.7510131.6190.2497.2
M50.250101.0015133.3184.9897.4
M60.250150.505134.3192.6297.9
M70.50050.5015125.8193.3299.3
M80.500100.755128.7188.6798.2
M90.500151.0010134.1170.2795.6
Tab.1  Programme of the orthogonal experiment
IndexParameterCTt1CPt2
CAK1121.4122.0125.4123.9
K2133.1129.3128.6130.5
K3129.6132.7130.0129.6
R11.710.74.66.6
PriorityCT > t1 > t2 > CP
FoK1234.99206.56197.13205.81
K2189.28203.67207.77199.29
K3184.09198.12203.46203.26
R523.1412.2719.097.20
PriorityCT > CP > t1 > t2
RoK197.6798.1398.2798.00
K297.5097.7397.6396.80
K397.7097.0096.9798.07
R0.201.131.301.27
PriorityCP > t2 > t1 > CT
Tab.2  Results of the orthogonal experiment
Fig.2  SEM images of modified membrane M1–M9.
Fig.3  Low-resolution SEM images of (a) M0, (b) TiO2-loaded membrane and (c) TiO2 + PFOTS-modified membrane, and high-resolution SEM images of (d) M0, (e) TiO2 loaded membrane and (f) TiO2 + PFOTS-modified membrane.
Fig.4  EDS images of the (a) unmodified membrane, (b) TiO2 + PFOTS-modified membrane. (c, d) EDS mapping images of C, O elements on the unmodified membrane, and (e–i) C, O, F, Ti, Si elements on the modified membrane.
Fig.5  Physicochemical characterization: (a) FTIR spectra of the pristine (M0) and modified membrane (MB); (b) XPS spectra of the pristine (M0) and modified membrane (MB); high-resolution C 1s spectrum of (c) M0 and (d) MB.
Fig.6  Wettability of the hydrophobic coating with various solutions and CA of MB.
Fig.7  The oil/water separation process of (a) petroleum ether/water system; (b) carbon tetrachloride/water system; (c) petroleum ether water/carbon tetrachloride system, the water is blue (methyl blue dyeing), and the oil is orange-red (Sudan III dyeing).
Fig.8  (a) Separation efficiencies of MB for carbon tetrachloride/ water system with different cycles. (b) The FRR of MB for three oil testing systems with different cycles.
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