Research Article - (2017) Volume 7, Issue 1

Investigation on Nanocomposite Membranes for High Pressure CO2/CH4 Separation

Xuezhong He* and May-Britt Hägg
Department of Chemical Engineering, Faculty of Natural Sciences, Trondheim, Norway
*Corresponding Author: Xuezhong He, Department of Chemical Engineering, Faculty of Natural Sciences, Norwegian University of Science and Technology, NO-7491 Trondheim, Norway, Tel: +47 73593942, Fax: +47 73594080 Email:


The novel nanocomposite membranes were prepared for CO2/CH4 separation, and a good selectivity >30 at high pressure >30bar was obtained by testing a plate-and-frame module with a membrane area 110 cm2. The Joule- Thomson effect was found to have negligible influence on the temperature drop inside the membrane module due to the very high heat transfer coefficient for the membrane materials, which is different from the HYSYS simulation results. The water permeance was determined to be higher compared to CO2 permenace especially at high pressure, which indicated high water vapor content should be achieved in the feed gas to avoid the drying of the membrane and maintain high membrane separation performance in a real process. A two-stage membrane system was designed to purify CH4 from a 50% CO2/50% CH4 gas mixture, and the CH4 purity of 70% can be achieved in the 2nd stage. Process simulation using HYSYS integrated with ChemBrane indicated that a multi-stage membrane system is needed to achieve the industrial requirement on the production of sweet natural gas.

Keywords: Nanocomposite membranes; CO2 removal; High pressure natural gas; Process simulation


• Development of novel nanocomposite membrane

• Joule-Thomson effect on membranes for CO2/CH4 separation

• Water permeation behavior through nanocomposite membrane

• Two-stage membrane system testing at high pressure


CO2 is one of the major contaminants in natural gas streams. The removal of CO2 from high pressure natural gas stream is necessary prior to entering downstream units of the gas processing plants due to Health, Safety and Environment (HSE) concern, heating value specification, as well as plant and pipeline corrosion issues [1]. Chemical absorption is the state-of-the-art technology for CO2 removal in on-shore/off-shore natural gas plants, but membrane system shows great potential in this application due to the advantages of smaller footprint, being environmentally friendly, and process flexibility [2-4]. Membranes for natural gas processing were first commercialized in the 1980s for CO2 removal, and have been the dominant membrane gas separation process since then [5]. The commercial polymeric membranes for natural gas sweetening today are mostly made from cellulose acetate (CA, spiral-wound) and polyimides (PI, hollow fibers). CA membranes have relatively low CO2/CH4 selectivity under typical operating conditions in the field [6,7], but have fair-to-good tolerance to the contaminants such as benzene, toluene, ethylbenzene and xylene (BTEX) in natural gas streams [8,9] with relatively low cost. The PI membranes presented a little better performance with higher CO2/CH4 selectivity but are more sensitive to BTEX [10]. The use of membrane systems provides an economically and environmentally attractive way compared to the traditional amine absorption. However, the challenges related to membrane compaction and plasticization at high pressure operation directs to the development of novel membrane materials [11]. Wang et al. [12] and Suleman et al. [13] reviewed the latest technological advancements and major problems in polymeric membranes for CO2/CH4 separation, and pointed out that the feasible solution on the crosslinking of the membrane materials and/or introducing inorganic nanoparticles into the polymer matrix to enhance the mechanical strength at high pressure application. Different cross-linking methods such as thermal annealing, formation of semi-interpenetration polymer networks, and ultraviolet (UV) radiation have been discussed by Wind et al. [14]. They concluded that most of the preceding crosslinking methods involve the procedures that would be difficult to be applied in the commercial membrane manufacturing processes. Ma et al. reported that ester-crosslinked hollow fiber membranes can maintain a high CO2 permeance under highly aggressive feed pressures up to 55 bar for a 50/50% CO2/CH4 feed gas without CO2 plasticization [15]. Zhao et al. [16] reported the chemically crosslinked Matrimid® 5218 for CO2 separation, which provided better mechanical properties, better flexibility for higher elongation at break, compared to their non-crosslinked precursors. He et al. [11,17] used a physical cross-linking method (heat treatment) to increase the mechanical strength of the fixed-site-carrier (FSC) membranes by controlling heating temperature <120°C, which can maintain membrane morphology and minimize production cost. Developing mixed matrix membranes (MMMs) and hybrid membranes is another potential approach to strength the mechanical stability. Adams et al. prepared a 50% (vol.) Zeolite 4A/polyvinyl acetate (PVAc) MMMs for CO2 separation from natural gas [18]. They found that the prepared MMMs can approach the Robeson CO2/CH4 upper bound. Other type of Matrimid® 5218 based MMMs presented relatively good CO2/CH4 selectivity >50, and showed interesting for purification of natural gas [19,20]. The carbon nanotubes (CNTs) was added into the polyvinylamine (PVAm)/polyvinyl alcohol (PVA) blend membranes in the previous work [3,11]. The initial testing on the lab-scale membranes presented a very promising separation performance for CO2/CH4 separation at high pressure (up to 40bar). It was reported that process operating parameters significantly influenced the module performance. Thus, bench-scale module testing without sweep gas was conducted in this work to document the nanocomposite membrane performance in a more realistic way. Moreover, understanding the water transportation behavior inside the membrane matrix and Joule- Thomson (J-T) effect is crucial to identify the optimal process operation condition for natural gas sweetening. The objective of this work was to develop a novel high performance nanocomposite membrane for CO2 removal from moderate pressure natural gas, and identify the requirement on the appropriate pre-treatment.


Preparation of nanocomposite membranes

Carbon nanotubes (CNTs, VGCF-X (D/L, 15 nm/3 μm) [11] reinforced nanocomposite membranes were prepared by coating a thin selective layer with controlled thickness on the top the commercial polysulfone (PSf) flat-sheet support (MWCO 20K, purchased from Alfa Laval)-See Figure 1. A certain amount of CNTs (1 wt.%) were added into the polymer solution and mixed by an ultrasonic mixer. Sonicated solution was then filtered using a syringe with a hydrophilic filter (Acrodisc® 5 μm) to remove any contaminants, polymer particles and the aggregated or not completely dispersed CNTs. The filtered solution was evenly casted on the top of the PSf supports. The nascent membranes were dried overnight in a vacuum oven, and then thermally cross-linked at 95 [11]. A 30 cm × 30 cm large flat-sheet nanocomposite membrane was prepared for the bench-scale module testing. The prepared nanocomposite membrane has a thin selective layer <1micron as shown from the SEM image (right in Figure 1: Using A Hitachi S-3400N scanning electron microscopy).


Figure 1: CNTs reinforced nanocomposite membranes.

Membrane performance testing

The membrane separation performance was measured by gas permeation testing. The prepared large flat-sheet membrane was cut into several sheets with a specific size (diameter, 12 cm), and each membrane area is 110 cm2(see left image in Figure 1). The high pressure bench-scale module (designed by PHILOS from South Korea involves three sheets (membrane area: 110-330 cm2) that can be operated individually or in other configurations such as parallel, series, and cascade [3]. The modules were then tested with the high pressure gas permeation rig [17]. The permeate gas composition was analyzed by a gas chromatograph (GC, from SRI Instruments Inc.), and the flow rate in feed and permeate were controlled/measured by Bronkhorst mass flow controller/meters. The gas permeance (m3(STP)/( of component i (Pi ) is calculated by


image (1)

image (2)

where Ji is the flux [m3(STP)/(m2.h)] of component i . pF and pP are feed and permeate pressure (bar), and xF,i is the feed concentration of component i. xR,i and yi are the retentate and permeate concentration of component i, respectively, which were measured by GC. q is the permeate volume flow (m3 (STP)/h), and A is the effective membrane area (m2). The selectivity is the ratio between the gas permeances of different compounds. According to eq. (1), the standard deviation of gas permeance can be estimated on the basis of permeate volume flow rate, driving force and membrane area, and a typical experimental error for gas permeance was calculated to be ± 4.6% [3]. Moreover, the CH4 loss is calculated based on the following equations,

image (3)

where qP and qF are the gas flow rate in feed and permeate streams (Nml/min). yCO2 and yCH4 are the CO2 and CH4 contents in the permeate stream.

Results and Discussion

Membrane material performance

A single module mounted the prepared membrane (membrane area of 110 cm2) was tested with a 3000Nml/min 10 vol.%CO2-90 vol. %CH4 mixed gas at 30°C and different feed pressures. The membrane system run at a low stage-cut, and the results are shown in Table 1. The CO2/CH4 selectivity >30 was found within the testing pressure window ranges 10-30bar. The CO2 permeance decrease with the increase of feed pressure due to the less water content in the feed gas stream and the low relative humidity (RH) in the retentate at higher pressure. The developed nanocomposite membranes showed good separation performance at operating pressure up to 30bar, but the gas permeance decreases with the increase of feed pressure. Thus, other alternative membrane materials (e.g. Carbon membranes) should be pursued for high pressure (60-90bar) natural gas sweetening in the future work.

Experimental condition Membrane performance
Feed pressure, bar Temperature °C Feed flow, Nml/min Retentate RH, % CO2 permeance, m3(STP)/ (m2·h·bar) CH4 permeance, m3(STP)/ (m2·h·bar) CO2/CH4 selectivity
10 30 3000 84 0.302 0.00775 39
20 30 3000 77 0.183 0.00528 34.6
30 30 3000 70 0.112 0.00343 32.7

Table 1: Membrane performance tested with a 10%CO2-90%CH4 mixed gas without sweep gas.

Investigation on Joule-Thomson effect

Temperature may decrease inside a membrane module when condensable gases (e.g., CO2) pass through a membrane from the high pressure feed side to the low pressure permeate side due to the Joule- Thomson (J-T) effect. HYSYS simulation integrated with ChemBrane was conducted (Simulation basis: area 330 cm2, PCO2=0.066 m3 (STP)/(, SCO2/CH4=19.4, feed flow 3000 Nml/min 10%CO2-90%CH4, sweep flow 50 Nml/min, permeate pressure 1.2bar) to predict temperature drop over a membrane using generic ComThermo package with Sour Peng-Robinson model in the vapor phase (see Figure 2). The results showed that permeate temperature decreased to 13.6°C at a feed temperature and pressure 30°C and 30 bar, respectively. Thus, the water vapor may condense inside the membrane matrix and/or on the membrane surface, which can potentially form a water film and decrease the gas separation performance. A gas stream with a high CO2 concentration transport through a membrane at high pressure may present a much significant temperature drop. Therefore, the feed line side should be super-heated to avoid water condensation inside the membrane and on the membrane surface as illustrated in Figure 3.


Figure 2: HYSYS Simulation on membrane unit for CO2/CH4 separation.


Figure 3: Illustration of Joule-Thomson effect.

If the system was operated at 30°C, the feed stream should be preheated to >45°C so that the temperature inside membrane module is higher than the dew point even with the J-T effect as illustrated in Figure 3. A thermocouple was inserted into the module to measure the temperature inside the membrane module. The sensor was initially put under the ceramic support inside the module, but no temperature difference was detected as the ceramic support is too thick which could hinder the heat transfer. Thus, the temperature drop inside the membrane matrix does not immediately influence the temperature on the bottom of the support. Therefore, the sensor was then directly installed in the permeate side of the membrane to detect the exact permeate temperature. However, there is still no temperature difference found. It was suspected that membrane material has very high heat transfer coefficient, and thus difficult to detect the temperature drop in a real process. Employing the computational fluid dynamics (CFD) modelling to simulate the temperature profile inside matrix should be conducted to further validate this experimental results in the future work.

Water vapor permeation

Deng et al. reported that membrane performance of the PVAm/PVA blend FSC membranes significantly depended on the relative humidity in the gas streams [21], and higher CO2 permeance was found at a high relative humidity due to the enhanced contributions from facilitated transport mechanism where CO2 reacts with the amino functional groups in the swelled (humidified) membranes. The influences of water vapor content (calculated from the relative humidity at a given pressure and temperature) on the membrane performance was reported in the previous work [11]. The lower absolute water vapor content decreases at higher feed pressure could cause the reduction on CO2 permeance besides the membrane compaction and carrier saturation. Water permeation of the prepared membrane (110 cm2) was tested at 30°C and different pressures (sweep gas 50 Nml/min at 1.2bar), and the results are shown in Table 2 and Figure 4. It can be found that both CO2 flux and water flux increase with the increase of feed pressure. It was worth noting that the water vapor permeance was found to be much higher compared to the CO2 permeance, especially at high pressure. Therefore, high water vapor content in a gas stream should be achieved to avoid the drying of the membranes at high stage cut operation-this will be the challenges related to process design and operation.

Feed pressure Flux, L/(m2·h) Permeance, m3(STP) /(m2·h·bar) Selectivity
CO2 H2O CO2 H2O* CO2/CH4 H2O/CO2
1.5 26.3 1.28 0.544 0.53 59.7 1
2 34.1 1.78 0.495 0.74 55.1 1.5
3 51 2.6 0.432 1 48.4 2.3
4 67 3.7 0.339 1.54 44.6 3.9
5 82.2 4.43 0.335 1.85 42.2 5.2
6 96.4 5.48 0.334 2.29 40.4 6.9
8 122.7 6.85 0.289 2.92 37.8 10.1
10 147.4 8.39 0.257 3.52 36.1 13.7
15 198.7 11.46 0.212 4.36 32.2 20.6
*:H2O permeance is calculated based on water flux and water vapor pressure difference between the feed and permeate sides.

Table 2: Membrane separation performance tested at 30°C.


Figure 4: Dependence of water and CO2 flux on feed pressure tested at 30°C, permeate pressure 1.2bar, sweep gas 50 Nml/min.

Two-stage membrane system

The high pressure bench-scale module involves three sheets that can be operated individually, or in parallel, series and cascade configurations. Testing with different membrane areas from a single sheet (110 cm2) to the whole module (330 cm2) at 10 bar and 30°C was reported by He et al. [11]. Both CO2 permeance and CO2/CH4 selectivity decrease with the increase of membrane area, and a better performance was reported in the vacuum operation compared to the sweep gas operation. In order to test the actual membrane separation capability for CO2 removal from natural gas, a two-stage membrane system related to the retentate was designed (see Figure 5) and tested at 30°C and 10bar with different feed flow rates (a synthetic gas mixture: 50% CO2-50% CH4) without sweep gas. The CH4 purity was improved from 50% to 70% at feed flow of 300-500 Nml/min as shown in Table 3. Further purification using extra stages is usually required to achieve the separation requirement of CH4 purity >96%. Moreover, the methane loss was found relatively high, recycling of the first stage permeate is needed to meet the requirement of low methane loss (i.e. <2%). The experimental results provided the input for process design on a full-scale natural gas sweetening plant using membrane technology.


Figure 5: Schematic diagram of a two-stage membrane in cascade related to retentate, permeate streams in the two stages can be measured separately.

Feed flow, Nml/min 1st stage 2nd Stage Total CH4 loss, %
PCO2, Nm3/(m2·h·bar) SCO2/CH4 Retentate CH4 purity, % PCO2, Nm3/(m2·h·bar) SCO2/CH4 Retentate CH4 purity, %
500 1.17E-01 27.3 58.8 0.145 32.3 70.4 3.8
300 8.54E-02 30.8 60.8 0.00958 35.2 73.4 4.1

Table 3: Separation performance of a two-stage cascade membrane unit.


The high performance nanocomposite membranes were prepared for CO2/CH4 separation at high pressure. The high CO2/CH4 selectivity >30 was tested out at the feed pressure up to 30bar with acceptable CO2 permeance. This high separation performance attributes to the combination of the Fickian diffusion and facilitated transport contribution from the developed membranes. However, the facilitated transport contribution is significantly dependent on the available carrier amount and water vapor content. Thus, the membrane performance was still found to decrease with the increase of feed pressure due to the lower water vapor content in the gas stream. Moreover, the water permeance was quite higher, especially more than one order of the CO2 permeance at high pressure. Thus, how to maintain high water vapor content at high pressure operation is crucial, and will be a challenge to engineering design. The membrane materials were found to have high heat transfer coefficient and the Joule-Thomson effect has negligible influence on temperature drop inside membrane module. The testing results from the two-stage cascade membrane system with bench-scale modules indicated that CH4 purity was improved from 50% to 70%, and the membrane performance in the second stage was better due to a lower feed CO2 concentration. The experimental results indicated that multi-stage membrane system related to the retentate is need to achieve high CH4 purity in the sweet natural gas when processing a high CO2 content (e.g. 50%) sour natural gas, which could be used to guide the process design in commercial applications.


The authors acknowledge the projects of NaGaMa (#210421) and CO2Hing (#267615) from the Research Council of Norway for the funding of this work.


Citation: He X, Hägg MB (2017) Investigation on Nanocomposite Membranes for High Pressure CO2/CH4Separation. J Membr Sci Technol 7:169.

Copyright: © 2017 He X, et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.