Omniphobic re-entrant PVDF membrane with ZnO nanoparticles
composite for desalination of low surface tension oily seawater
Bhaskar Jyoti Deka, Jiaxin Guo, Noman Khalid Khanzada, Alicia Kyoungjin An
*
School of Energy and Environment, City University of Hong Kong, Tat Chee Avenue, Kowloon, Hong Kong Special Administrative Region
article info
Article history:
Received 23 May 2019
Received in revised form
9 August 2019
Accepted 12 August 2019
Available online 13 August 2019
Keywords:
Omniphobic membrane
Zinc oxide nanoparticle
Membrane distillation
Re-entrant structure
Low surface tension oily seawater
desalination
Anti-wetting
abstract
In this study, an omniphobic membrane was fabricated by electrospraying fluorinated zinc oxide (ZnO)
nanoparticles (NPs) mixed with polyvinylidene fluoride-co-hexafluoropropylene (PVDF-HFP) on the
surface of an organosilane functionalized polyvinylidene difluoride (PVDF) membrane. Our results
revealed that the functionalized ZnO NPs membrane exhibited a rough hierarchical re-entrant
morphology with low surface energy which allowed it to achieve high omniphobic characteristics. It
was observed that the addition of 30% ZnO (w/w of PVDF-HFP) was found to be optimal and imparted a
high repulsive characteristic. The optimized PVDF/ZnO(30)/FAS/PVDF-HFP referred as cPFP-30Z mem-
brane exhibited a high contact angle values of 159.0 ± 3.1
, 129.6 ± 2.2
, 130.4 ± 4.1
and 126.1 ± 1.2
for
water, sodium dodecyl sulfate (SDS) saline solution (0.3 mM SDS in 3.5% NaCl), ethanol, and vegetable oil,
respectively. The low surface energy and high surface roughness (Ra) of optimised membrane was
assessed as 0.78 ± 0.14 mN m
1
and 1.37 mm, respectively. Additionally, in contrast with the commercial
PVDF membrane, the cPFP-30Z membrane exhibited superior anti-wetting/anti-fouling characteristics
and high salt rejection performance (>99%) when operated with a saline oil solution (0.015 v/v) and SDS
(0.4 mM) feed solutions.
© 2019 Elsevier Ltd. All rights reserved.
1. Introduction
Membrane distillation (MD), an emerging thermal-based tech-
nology, can be a viable option for the production of sustainable
high-quality water from super-saline brine, shale gas or oily
wastewater when provided with access to waste/low-grade heat or
solar energy sources (Alkhudhiri et al., 2012; Lee et al., 2017). As MD
is driven by the temperature and vapor pressure gradient in which
water evaporates from the hot feed side and travels through a hy-
drophobic membrane, the MD process is not affected by the feed
concentration. Therefore, in recent years, MD has expanded its
applications into different fields, including removal of volatile
organic compounds from solutions, cleaning of environmental
impurities, crystallization of valuable resources, biomedical, and
food processing applications (Barbe et al., 1998; Kujawski et al.,
2013; Motta et al., 2017; Villalba, 2013). However, while MD has
shown significant potential in a wide range of applications, major
hurdles such as wetting and fouling which result in flux decline and
poor permeate quality still limits its largescale industrial applica-
tion (Chen et al., 2017; Mishra et al., 2016; Rezaei et al., 2018; Wang
et al., 2018). Whilst existing commercial MD membranes undergo
severe wetting and fouling when dealing with organic and low
surface tension contaminants (Wang et al., 2016), omniphobic
membranes have gained attention due to their hydrophobic nature
and ability to repel traditionally problematic low surface tension
liquid substances, such as oil, surfactants, etc. (Lee et al., 2016b; Lin
et al., 2014; Wei et al., 2005).
The development of robust omniphobic membrane capable of
repelling both water and oil while maintaining high water flux will
therefore have remarkable scientific and commercial implications
(Pan et al., 2013; Sheen et al., 2008). The very first report on the
fabrication of an omniphobic membrane for MD application uti-
lized silica nanoparticles (Si-NPs), which were coated over a hy-
drophilic glass fibre membrane followed by surface fluorination.
However, the membrane showed a contact angle (CA) below 90
with ethanol and a low water flux of 15.8 ± 2.7 L m
2
h
1
(LMH) (Lin
et al., 2014). For a membrane to be omniphobic, the membrane
must demonstrate a CA for water and oil of nearly 140
and 110
,
respectively (Zheng et al., 2018). One method for achieving such
high CAs is by grafting fluoroalkylsilanes (FAS) onto the membrane
* Corresponding author.
E-mail address: alicia.kjan@cityu.edu.hk (A.K. An).
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Water Research
journal homepage: www.elsevier.com/locate/watres
https://doi.org/10.1016/j.watres.2019.114982
0043-1354/© 2019 Elsevier Ltd. All rights reserved.
Water Research 165 (2019) 114982