Membrane and Water Treatment, Vol. 11, No. 2 (2020) 97-109
DOI: https://doi.org/10.12989/mwt.2020.11.2.097 97
Copyright © 2020 Techno-Press, Ltd.
http://www.techno-press.org/?journal=mwt&subpage=7 ISSN: 2005-8624 (Print), 2092-7037 (Online)
1. Introduction
The increase of palm oil demand in recent years has
contributed to the rapid development of palm oil industry in
Malaysia. This has directly resulted in an increase of waste
produced during the palm oil processing. One of the major
wastes produced from palm oil processing is palm oil mill
effluent (POME), the largest source of industry wastewater
in Malaysia. It is estimated that Malaysia produces around
53 million tons of POME annually (Pogaku et al. 2015).
POME is a colloidal suspension that contains 95%–96%
water, 0.6%–0.7% oil, and 4%–5% solid. Direct discharge
of POME into the water body without proper treatment
could impose serious environmental problems to the
ecosystem, such as the change of soil properties, air
pollution, water pollution, and greenhouse gas emission, all
of which attribute to the high biological oxygen demand
(BOD), chemical oxygen demand (COD), oil and grease,
total solids, and noxious smell (Khatun et al. 2017).
Corresponding author, Senior Lecturer
E-mail: yh_teow@ukm.edu.my
The commonly used commercial methods for POME
treatment in Malaysia integrate anaerobic and aerobic
ponding systems. However, the integrated anaerobic and
aerobic ponding systems require large land area and long
retention time (around 20 to 200 days), which is the main
drawback of this POME treatment method (Zhang et al.
2008). Besides that, the treated POME through integrated
anaerobic and aerobic ponding systems is unable to meet
the industry’s wastewater discharge standards set by
relevant authority. As such, many studies have been carried
out by researchers to discover alternative and efficient
POME treatment method, including adsorption
(Mohammed et al. 2014), photocatalytic process (Alhaji et
al. 2016), biofilm reactor (Abu Bakar et al. 2018),
microalgae treatment (Takriff et al. 2016), and membrane
filtration (Ho et al. 2018). Among the aforementioned
treatment methods, membrane filtration showed the most
significant performance in POME treatment, with several
advantages of the membrane technology, such as small
footprint, consistent effluent quality, less chemical usage, as
well as easy maintenance and operation .A pilot-scale
integrated system that combined the sand filter and
activated carbon filter as pretreatment, coupled with
Thermo-responsive antifouling study of
commercial PolyCera® membranes for POME treatment
Teow Yeit Haan
1,2
, Loh Wei Chean
2
and Abdul Wahab Mohammad
1,2
1
Research Centre for Sustainable Process Technology (CESPRO), Faculty of Engineering and Built Environment,
Universiti Kebangsaan Malaysia, 43600 Bangi, Selangor, Malaysia
2
Department of Chemical and Process Engineering , Faculty of Engineering and Built Environment,
Universiti Kebangsaan Malaysia, 43600 Bangi, Selangor, Malaysia
(Received April 1, 2019, Revised November 29, 2019, Accepted December 20, 2019)
Abstract. Membrane fouling is the main drawback of membrane technology. Frequent membrane cleaning and membrane
replacement are, therefore, required to reduce membrane fouling that causes permeate flux reduction, lower rejection, or higher
operating pressure. Studies have proved that the alteration of membrane properties is the key controlling factor in lessening
membrane fouling. Among stimuli-responsive membranes, thermo-responsive membrane is the most popular, with a drastic phase
transition and swelling-shrinking behavior caused by the temperature change. In this study, the thermo-responsive ability of two
commercial membranes, PolyCera® Titan membrane and PolyCera® Hydro membrane, at different temperatures was studied on
the antifouling function of the membrane in palm oil mill effluent (POME) treatment. The evaluation of the membrane’s thermo-
responsive ability was done through three cycles of adsorption (fouling) and desorption (defouling) processes in a membrane
filtration process. The experimental result depicted that PolyCera® Hydro membrane had a higher membrane permeability of
67.869 L/m
2
.h.bar than PolyCera® Titan membrane at 46.011 L/m
2
.h.bar. However, the high membrane permeability of PolyCera®
Hydro membrane was compensated with low removal efficiency. PolyCera® Titan membrane with a smaller mean pore size had
better rejection performance than PolyCera® Hydro membrane for all tested parameters. On the other hand, PolyCera® Titan
membrane had a better hydrodynamic cleaning efficiency than PolyCera® Hydro membrane regardless of the hydrodynamic
cleaning temperature. The best hydrodynamic cleaning performed by PolyCera® Titan membrane was at 35°C with the flux
recovery ratio (FRR) of 99.17 ± 1.43%. The excellent thermo-responsive properties of the PolyCera® Titan membrane could
eventually reduce the frequency of membrane replacement and lessen the use of chemicals for membrane cleaning. This outstanding
exploration helps to provide a solution to the chemical industry and membrane technology bottleneck, which is the membrane
fouling, thus reducing the operating cost incurred by the membrane fouling .
Keywords: fouling; thermo-responsive; PolyCera® membrane; antifouling; POME treatment