Modification of Surface Hollow Fiber Membrane Ultrafiltration for
Processing Produced Water
Malikhatul Hidayah
Department of Chemical Engineering, Diponegoro University,
Semarang, Indonesia
Keywords: Modification, Surface, Hallow, Fiber, Membrane, Ultrafiltration, Produced.
Abstract: Produced water classified in the wastewater would require water treatment before being discharged into water
bodies. One of the alternative technologies that could be used for the processing of produced water is a
membrane technology that can be used as a source of new water well for irrigation agriculture, industrial
water, and water Therefore, studies for treating produced water using hollow fiber membrane ultrafiltration
has. Making the surface modification of hollow fiber ultrafiltration membrane can increase the viscosity and
concentration as well as in the coagulation process is a hybrid joining hollow fiber ultrafiltration membrane
allows for better elimination of contaminants present in raw water, which is very important for the quality.
1 INTRODUCTION
1.1 Research Background
Produced water is a byproduct of water brought to the
surface during oil and gas collection, which includes
formation water, injection water, and chemicals are
added to the drilling or oil or water separation
process. The produced water can pollute the
environment if not handled properly (Hidayat, 2007)
produced water contains organic and inorganic
materials potentially B3 (Toxic Substances and
Hazardous) that affect the environment and human
health. The rapid development of industry demand for
improved technology towards better, which
minimizes the weaknesses that can degrade
performance ultrafiltration membranes,
Ultrafiltration has been applied in water treatment
systems, among the available membrane module,
hollow fiber membranes are compact and self-
sufficient has been widely used as ultrafiltration
membrane configurations (Ramli et al. 2014) hollow
fiber ultrafiltration membrane has been recognized as
one of the most important processes applied in water
treatment systems because it uses low pressure
process that requires less energy and have a very
economic cost. Therefore, to identify the filtration
performance of the process is concentrated on hollow
fiber membrane applications, it is best to understand
and analyze the factors that can affect the
performance of hollow fiber ultrafiltration
membrane.
1.2 Problem Statement
Produced water classified in the wastewater would
require water treatment before being discharged into
water bodies. One of the alternative technologies that
could be used for the processing of produced water is
a membrane technology that can be used as a source
of new water well for irrigation agriculture, industrial
water and drinking water (Saputra et al. 2013),
therefore, various studies to treat water be produced
using hollow fiber membrane ultrafiltration was
performed (Yang et al. 2006) examines the creation
and characterization of poly Phthalazines ether
sulfone ketone (PPESK) ultrafiltration membrane
hollow fiber with thermal stability where the thermal
stability of high PPESK ultrafiltration membrane
hollow fibers with different morphologies and the
show has been prepared by dry / wet phase inversion
spinning method successfully. In addition, the
viscosity of the casting solution is highly dependent
on the content PPESK, who said, with the increase in
concentration viskositasdan content PPESK greatly
improve and become dependent shear-level.
(Konieczny et al., 2006) Researching on
Efficiency of the hybrid coagulation-ultrafiltration
water treatment process with the use of immersed
hollow-fiber membranes which Process hybrid
joining the coagulation membrane hollow fiber
Hidayah, M.
Modification of Surface Hollow Fiber Membrane Ultrafiltration for Processing Produced Water.
DOI: 10.5220/0010041302510257
In Proceedings of the 3rd International Conference of Computer, Environment, Agriculture, Social Science, Health Science, Engineering and Technology (ICEST 2018), pages 251-257
ISBN: 978-989-758-496-1
Copyright
c
2021 by SCITEPRESS – Science and Technology Publications, Lda. All rights reserved
251
ultrafiltration, such as UF, allowing for the
elimination of the better of contaminants present in
the raw water, which is very important for the quality.
Use of Fe2 (SO4) 3 coagulant determined as COD
and oxygen consumption of the use of FeCl3. In the
case of FeCl3, Improved Content chloride was
observed. Use of Fe2 (SO4) 3. This increase is not
significant for the quality of the treated water.
(Nabe et al. 1997) examines the polysulfone
ultrafiltration membrane surface modification and
fouling by BSA solution in which the surface energy
of the membrane, as measured by the contact angle,
used to characterize the different membranes.
Streaming-potential measurements were obtained to
investigate the membrane surface. Surface roughness
of each membrane is also determined by the power of
the atom. (Prince et al. 2014) studied the synthesis
and characterization of PEG-Ag move PES hollow
fiber membrane ultrafiltration with antifouling
properties durable where modification of functional
PES hollow fiber membrane that has been done by
incorporating hydrophilic polyethylene glycol (PEG)
and nanoparticles of silver (Ag) through thermal
grafting. Poly (acrylonitrile-comaleic acid)
(PANCMA) is used as a chemical linker to attach
PEG and silver for the PES hollow fiber membrane.
Functional modifications using different analytical
techniques such as Fourier transform infrared (FTIR)
spectroscopy, energy-dispersive X-ray (EDX) study,
the water contact angle (CA), Fourier Emission
Scanning Electron Microscopy (FESEM), and
porometer. Subsequently, the membrane was tested
for purewater flux and antifouling property. The
contact angle of the data, it was identified that the new
surface modification can improve the hydrophilicity
of the membrane. Based on experimental data
generated less so maximum it is necessary to further
study if there are additional UF membrane.
(Chung et al. 2000) Researching on the
Influence of the shear rate in the spinnerets
morphology, separation performance and mechanical
properties of the hollow fiber membrane
ultrafiltration polyethersulfone.Where the hollow
fiber UF membranes are made of drug-containing
solution polyethersulfone (PES) / N-methyl-2-
pyrrolidone (NMP) / Diethylene Glycol (DG) with a
weight ratio of 13/45/42. Wet-spinning process was
deliberately chosen to make the hollow fibers without
attracting and water is used as an external coagulant.
Therefore, in the belief that the effects of gravity and
elongation at formation of stress fibers can be
significantly reduced and the orientation caused by
shear stress in a spinner which can be frozen into the
wet-spun fibers. The results showed that the high
shear rate in the spinner apparently resulting hollow
fiber UF membrane with a thicker and / or denser skin
due to greater molecular orientation. As a
consequence, when the shear rate increases, pure
water flux, the coefficient of thermal expansion
(CTE) and the end of the fiber elongation decreases,
but the storage modulus, tensile strength and Young's
modulus increases. For the first time, it was found that
there was a certain critical value of the shear rate
under the clear separation performance fiber
increased while the flux decreased dramatically with
increased shear rate but above the flux separation
slightly decreased while there was no change. (Ramli
et al. 2014) Researching about the factors that
influence the hollow fiber membrane ultrafiltration
water treatment in operational performance which the
initial processing as well as the transmembrane
pressure (TMP) can penetrate flux. These factors are
important as a reference point when evaluating the
operating performance of hollow fiber ultrafiltration
membranes. Thus, allowing a proper assessment and
better in choosing a water treatment system.
(Gholami et al. 2003) Researching on Effect of heat
treatment on the performance of hollow fiber
membrane ultrafiltration polyethersulfone (PES) in
which the hollow fiber membrane Polyethersulfone
(PES) prepared by the method of spinning the dry-wet
and then heated in an oven at different temperatures
to determine the effect of treatment Hot on the
performance of their ultrafiltration. Found that the
hollow-fiber membranes shrink by heat treatment, as
evidenced by a decrease in flux and increase the
separation of solutes, though no visible changes in
hollow-fiber dimensions.
Selection of the appropriate type of membrane
for produced water treatment is done by (Safitri et al.
2013) ultrafiltration technology for produced water
treatment wherein In this research, the processing of
produced water using ultrafiltration membranes.
which aims to determine the characteristics of the
beginning of produced water and the membrane
(functional groups on the membrane), knowing the
performance of the membrane represented by flux
and rejection, and assess the effect of ultrafiltration
on the characteristics of the end produced water
Therefore more research is needed on waste water
refining petroleum to know whether ultrafiltration
technology can be utilized for the processing of
petroleum refinery waste.
1.3 Research Objective
Research conducted aims are as follows:
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a. Reviewing the process of making hollow
ultrafiltration membrane made of Polyamide.
b. Making assess Phthalazines poly ether sulfone
ketone (PPESK) hollow fiber ultrafiltration
membranes with thermal stability.
c. Analyzing the performance of non-fouling
membranes Polyamide modified for produced
water treatment
d. Assessing the performance of the membrane
represented by flux and rejection, and assess the
effect of hollow ultrafiltration membranes for
water characteristics terproduksi
2 LITERATURE REVIEW
2.1 Membrane Ultrafiltration (UF)
Technology
Today, ultrafiltration (UF) technology is recognized
by the water industry as a very attrac- tive process for
producing drinking water, UF membranes are
physical barriers which are able to efficiently remove
suspended particles, turbidity, bacteria, colloids,
algae, parasites and viruses for clarification and
disinfection purposes. In comparison with
conventional processes such as coagulation,
flocculation, sedimentation and/or flotation, rapid
and slow sand filtration, UF tech- nology has many
advantages such as (1) superior quality of treated
water, (2) a much more compact system, (3) easier
control of operation and main- tenance, (4) fewer
chemicals, and (5) less pro- duction of sludge.
2.2 Membran
Membrane has several advantages, namely The
process of speciation can be either continuous or
batch, Low energy consumption, The process of
separation can take place at room temperature, Easy
to scale up, The nature of the membrane varies, and
easy to set, Does not require any additives and
Equipment is compact.
2.3 Classification of Membrane
According to Mulder (1996), the membrane is
classified into several categories as follows:
1. The type of membrane based on the
manufacture
a. Biological membranes eg skin cells,
kidneys, heart, etc. (Wenten, 1999).
b. The membrane synthesis into two types,
namely
Organic membrane is a membrane which
as its main composition of polymers and
macromolecules, for example: cellulose
acetate membrane (CA), polyacrylonitrile
(PAN), polyamide (PA) and others.
Inorganic membrane is composed of
inorganic compounds, eg ceramic
membranes (such as ZrO2 and γ-Al2O3),
membrane glass (like SiO2¬).
2. The type of membrane based on morphology is
divided into two types, namely:
a. Symmetric membrane is a membrane
having a pore size that is homogeneous,
b. An asymmetric membrane is a membrane
with a pore size outer side more tightly
with a thickness of between 0.1-0.5 μm
3. The type of membrane based on the principle of
separation. Based on the principle of the
separation, the membrane is divided into three
types, namely:
a. Porous Membrane: The membrane of
this type is applied to microfiltration,
ultrafitrasi, and nanofiltration.
b. The non-porous membrane with the
membrane of this type can separate
molecules that have more or less similar
size to one another.
c. The membrane carrier molecule is
determined by a very specific carrier that
facilitates transport specific.
4. Type membrane by function
a. Microfiltration, 0.05 to 10 μm<2 bar :
Separating suspensions and colloids
b. Ultrafiltration, 1-100 nm 1-10 bar :
Separating macromolecules
c. Nanofiltration, <2 nm 10-25 : Separating
bars soluble components having a low
molecular weight
d. Reverse osmosis, <2 nm , Brackish
water: 15-25 bar, Sea water: 40-80 bar
Separating dissolved components with low
molecular weight
2.4 Membrane Preparation Method
Membranes can be made from organic materials and
inorganic polymers such as ceramic, metal, and glass.
Several techniques can be used to make membranes
that sintering, stretching, track-etching, template
leaching and phase inversion (Mulder, 1996).
Modification of Surface Hollow Fiber Membrane Ultrafiltration for Processing Produced Water
253
2.5 Membrane Fouling
Adsorption or accumulation of certain components in
produced water on the membrane surface or in the
pores of the membrane which can result in decreased
efficiency of flux. Fouling is a limiting survival of a
membrane in the economic value of produced water
treatment (Ahmadun et al. 2009).
Fouling of the membranes can be classified into:
2.6 Irradiation with UV Rays
UV light on the membrane used to make membranes
become susceptible to the reaction, then the polymer
chain must contain a double bond, hydroxyl group, or
a benzene ring (Nunes and Peinemann, 2001). UV
light causes polymerization of the membrane.
However, in the presence of polymerization will
reduce pore size that will cause a reduction in
permeability (Susanto, 2007). Polymerization speed
depends on operating conditions such as the type of
UV light (wavelength and energy), the concentration
of monomer, the distance between the source of UV
and membrane, and the exposure time (Homayoonfal,
2010).
2.7 Membrane Characterization
Modified
The analysis used to determine the performance of the
membrane can be seen from the parameter flux
(permeability), rejection (selectivity), and the
structure of membrane morphology (Mulder, 1996).
2.8 Hollow Fiber Membrane
Hollow Fiber Membrane (HFM) is a membrane that
can be used to transfer gas and steam hydrophobic (ie
volatile and semivolatile organic compounds)
between two liquids, usually gas (air) and water
(liquid).Membranes are often used in the industry is
an asymmetric membrane.
2.8.1 Advantages of Hollow Fiber
Hollow fiber membrane is one of the most popularly
used in the industry. This is due to several useful
features that make it attractive for the industry.
Among others are:
a. Energy needs: In the filtration process no phase
change involed. Consequently, it is not
necessary latent heat. This makes hollow fiber
membranes have the potential to replace several
operating units which consume heat, such as
distillation or evaporation column.
b. There is no product waste: Since the principal
base is hollow fiber filtration, do not generate
waste from operation unless the unwanted
components in the feed stream. This can help to
reduce operating costs for dealing with garbage.
c. large surface per unit volume: Hollow fiber
membrane surfaces have large volumes per
module. Therefore, the smaller the size of the
hollow fiber membranes than other types but
can provide higher performance.
d. Flexible: Hollow fiber membranes are flexible,
able to perform filtering in 2 ways, both are
"inside-out" or "outside-in".
e. Low operating costs: hollow fiber requires
lower operating costs compared to other types of
operating unit.
f. However, it also has some drawbacks that cause
application problems. Among the drawbacks
are:
g. Membrane fouling: Hollow fiber membrane
fouling more often than other membranes
because of the configuration. contaminated feed
would increase the rate of membrane fouling,
esapecially for hollow fibers.
2.8.2 Asymmetric Hollow Fiber Membrane
Applications
Asymmetric Hollow Fiber Membranes can be applied
for CO2 Separation of Hydrocarbons and
Fluorocarbons. High-pressure carbon dioxide
separation of fluorocarbons is essential in the
production of fluoropolymers such as poly
(tetrafluoroethylene). Plasticize typical polymeric
membranes under high pressure CO2 partial
conditions. Based on the measured performance of
the separation of CO2 / C2H2F2 and CO2 / C2H4
mixture, the selectivity of CO2 / C2 F4 mixture is
greater than 100. The long-term stability studies show
that membranes provide separation stable for 5 days
at 1250 psi partial pressure of CO2, thus making the
membrane approaches interesting.
2.9 Polyimide
Aromatic polyimides are typically used for
applications in high temperature, because the material
can maintain high strength in continuous use at
temperatures above 300 ° C for short periods.
Continuous film, foil, sheet, fabric or laminate is
particularly desirable for use in high temperature
electrical insulation for thermal stability and
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durability of the resin. While the resin substrate imide
can be used for circuit boards fireproof, radomes, etc.,
the use of the most major, namely in the manufacture
of thin film to wrap the electric motor or the like,
where these materials can withstand high
temperatures long term without loss of mechanical or
electrical properties. Thermosetting polyimides are
very valuable as films, with fused-ring aromatic
groups contributes to high thermal stability. High
tensile strength in a wide temperature range,
dimensional stability, wear resistance, high dielectric
strength, chemical resistance, and radiation resistance
properties is desirable to use a lot of polyimides.
Polyimide films, such as "Kapton", has been found to
be used in electric motors are compact, in which the
high dielectric strength, and toughness are important,
as well as in insulation for aircraft wiring and
missiles, etc. In wrapping insulation film, flexibility
and elongation of the film is important for allowing
polyimide to conform to the shape of the substrate.
The film is made by casting can be solution-oriented
after removing at least part of the solvent, as the
evaporation of the film. Molecular orientation can be
done by stretching the film in the machine direction
orientation (MDO) and / or transverse direction
orientation (TDO) at a temperature of orientation.
Typical previous films made by this process can have
10% to 25% elongation before breaking under tensile
stress.
2.10 Ultrafiltration Membrane
Operating membrane separation process can be
defined as two or more components of the fluid flow
through a membrane. The membrane serves as a
barrier (Barrier) is a highly selective thin between the
two phases, it can only skip certain components and
hold the other components of a fluid flow that passed
through the membrane (Mulder, 1996). Membrane
process involves feed (liquid and gas), dangaya thrust
(drivingforce) due to the pressure difference (ΔP), the
concentration difference (ΔC) and the energy
difference (AE). Ultrafiltration membrane process
(UF) is an effort that uses the membrane separation
with different thrust force of pressure is strongly
influenced by the size and distribution of pore
membranes (Malleviale., 1996). The separation
process occurs in particles of colloidal size range. The
membrane operates at a pressure antara1-5bar and
permeability limits ARE1 0-50l / m2.jam.bar.
Applied Membrane Technology is to generate clean
water with your water quality requirements. The raw
water is inserted kebejana containing a semi-
permeable membrane, with a tekanan.Ini gave the
physical process of separating solute from solvent.
The membrane only traversed solvent, while
dissolved, either electrolytes or organic, will be
rejected (rejection), also prakits to remove organic
substances. Other contaminants such as colloidal
right retained by the pore structure that acts as a filter
(sieve) nominal BM molecule used for ultrafiltration
membrane has a porous membrane structure and
asymmetric. Membrane advantages compared with
conventional treatment in drinking water treatment,
among others (Wenten.1996) Requiring lower energy
for operation and maintenance, design and
construction of small-scale system, the equipment is
modular so easy in-scaleup and do not need extreme
conditions (temperature and pH). However,
membranes have limitations such as the occurrence of
the phenomenon of concentration polarization,
fouling, which is a barrier for water volumeprocessed
generated and also the limitations of the age of the
membrane.
2.11 Produced Water Treatment
Produced water is water from underground rock
structure on the source of the oil has been dragged to
the ground along with the gas and oil in the
exploration and production of fossil fuels. Produced
water can be derived from the exploration and
production of oil well offshore (offshore) or on land
(on-shore). During this time produced water is a
byproduct of the largest and regarded as waste in the
process of exploration and production of oil and gas.
The average ratio of the amount of produced water
with oil in oil wells in the world reached 3: 1. The
amount of produced water will increase as the old age
of exploration and production of oil wells. The
content of produced water depends on the
geographical location of oil wells, the type of rock
structures under the ground, the type of hydrocarbon
that is produced, as well as various additive
compounds that are used during the exploration and
production takes place.
2.12 Future Direction
The research to be undertaken to achieve the goal of
the research is expected. The research is divided into
three stages, namely the manufacture of Polyamide
membranes, characterization stage, and the stage of
membrane application for processing produced water.
Polyamide membranes at the stage of manufacture
begins by making a print solution that consists of
Polyamide polymer with composition 18 wt%;
additives PEG 1500 and 4000, each with a
Modification of Surface Hollow Fiber Membrane Ultrafiltration for Processing Produced Water
255
concentration of 1 wt%, 3 wt%, 5 wt%; and acetone
as the solvent. Printing membranes using phase
inversion methods. This method is done by printing
the membrane on the glass plate using a casting knife,
and then the membrane is irradiated with UV light by
varying the time for 10, 20, 30 minutes. Furthermore,
the membrane is inserted into the coagulation bath
with distilled water as non-solvent for 1 hour,
followed by immersion in a different coagulation bath
for 24 hours. The membranes were dried in an oven
at a temperature of 40-50 ° C for 24 hours. The next
stages were characterized by determination of flux
and rejection, Scanning Electron Microscopy (SEM)
and Fourier Transform Infrared (FTIR). After that
tested the application of membranes for water
treatment produced.
Research Design Diagram:
3 CONCLUSION
Based on literature study that has been described
above, To Modify and analyze the factors that can
affect the performance of hollow fiber ultrafiltration
membrane is one of the processes are applied in water
treatment systems because it uses low pressure
process that requires less energy and have a very
economic cost. Use of the membrane can be formed
in a variety of configurations and sizes, Configuration
hollow fiber membrane has the advantage of a
compact design with a surface area of the membrane
is very high, therefore, produce better productivity
with support mechanisms that can be returned to the
separation of produced water provides good
flexibility as well as easy handling during module
fabrication operation
REFERENCES
Ahmadun, F., Pendashteh, A. & Chuah, L., 2009.Journal of
Hazardous Materials. , 170, pp.530–551.
Baker, 2014.Membrane Technology and Applications (2nd
edition).Universiti Malaysia Sabah, 1, p.13.
Chung, T.-S., Qin, J.-J.&Gu, J., 2000. Effect of shear rate
within the spinneret on morphology, separation
performance and mechanical properties of
ultrafiltration polyethersulfone hollow fiber
membranes.Chemical Engineering Science, 55(6),
pp.1077–1091. Available
Gholami, M. et al., 2003.The effect of heat-treatment on the
ultrafiltration performance of polyethersulfone (PES)
hollow-fiber membranes.Desalination, 155(3), pp.293–
301. Available at:
Hidayat, S., 2007.Penyisihan Senyawa Organik Limbah Air
Terproduksi Pada Reaktor Batch Menggunakan Bakteri
Indogenous Dan Penambahan Nutrisi.artikel, 1, pp.3–
6.
Kerja, C., 2009. Uji Kinerja Membran Ultrafiltrasi Dengan.
Jurnal Sains Materi Indonesia, 11(1), pp.6–9.
Konieczny, K., Sakol, D. & Bodzek, M., 2006.Efficiency
of the hybrid coagulation-ultrafiltration water treatment
process with the use of immersed hollow-fiber
membranes.Desalination, 198(1-3), pp.102–110.
Nabe, A., Staude, E. & Belfort, G., 1997.Surface
modification of polysulfone ultrafiltration membranes
and fouling by BSA solutions.Journal of Membrane
Science, 133(1), pp.57–72.
Prince, J.A. et al., 2014. Synthesis and characterization of
PEG-Ag immobilized PES hollow fiber ultrafiltration
membranes with long lasting antifouling properties.
Journal of Membrane Science, 454, pp.538–548.
Available at:
Ramli, R., Bolong, N. & Yasser, A.Z., 2014. Review on the
Factors Affecting Ultrafiltration Hollow Fiber
Membrane Operational Performance in Water
Treatment. Universiti Malaysia Sabah, 1, pp.1–10.
Rana, D. et al., 2005. Development and characterization of
novel hydrophilic surface modifying macromolecule
for polymeric membranes. Journal of Membrane
Science, 249(1-2), pp.103–112. Available at:
Saputra, A.D., Syarfi & Khairat, 2013.Pencucian Secara
Kimia Membran Ultrafiltrasi Sistem Aliran Cross Flow
pada Proses Penyaringan Air Terproduksi.teknik Kimia,
1, pp.1–9.
Shi, X. et al., 2014. Journal of Water Process Engineering
Fouling and cleaning of ultrafiltration membranes : A
review. Journal of Water Process Engineering, 1,
pp.121–138.
Polyamid
a
PEG1500,PEG4000(1wt%,3
wt%
,
5wt%
)
Polyamidemembranes
manufacture
Pre‐treatment
IrradiatingUV
A
Membrane
Characterization:
• Flux and
rejection
Morphology
Anal
y
sis
Membrane
applications
(Processing of
Purpos
e1
Purpos
e2
Purpose3
Purpos
e4
ICEST 2018 - 3rd International Conference of Computer, Environment, Agriculture, Social Science, Health Science, Engineering and
Technology
256
Wang, Z. et al., 2014. Membrane cleaning in membrane
bioreactors : A review. , 468, pp.276–307.
Yang, Y. et al., 2006. Preparation and characterization of
poly(phthalazinone ether sulfone ketone) hollow fiber
ultrafiltration membranes with excellent thermal
stability. Journal of Membrane Science, 280(1-2),
pp.957–968.
Yuan, T. et al., 2014. Polysulfone membranes clicked with
poly ( ethylene glycol ) of high density and uniformity
for oil / water emulsion puri fi cation : Effects of
tethered hydrogel microstructure. Journal of Membrane
Science, 470, pp.112–124.
Zhang, X. et al., 2015. Influences of the structure
parameters of multi-walled carbon
nanotubes(MWNTs) on PVDF/PFSA/O-MWNTs
hollow fiber ultrafiltration membranes. Journal of
Membrane Science, 499, pp.179–190. Available at:
Modification of Surface Hollow Fiber Membrane Ultrafiltration for Processing Produced Water
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