DOI:
10.1039/D6TA01917J
(Paper)
J. Mater. Chem. A, 2026, Advance Article
MFU-4 as a benchmark molecular sieve for efficient CO2/CH4 separation in biogas upgrading
Received
4th March 2026
, Accepted 22nd May 2026
First published on 22nd May 2026
Abstract
The efficient separation of CO2 from CH4 is central to industrial biogas upgrading for the production of pipeline-quality biomethane. Kinetic, molecular sieve-based adsorption is preferred over thermodynamic approaches, making small-pore adsorbents such as CMS-3K and ion-exchanged ETS-4 the current industrial standard. Here, we show, through a combination of breakthrough experiments and computational analysis, that the ultra-microporous Zn triazolate MOF MFU-4 significantly surpasses these benchmarks. Its unique architecture, featuring alternating small and large cages connected by narrow, square-shaped pore gates, kinetically hinders CH4 diffusion while facilitating rapid CO2 transport and achieving high CO2 uptake, effectively overcoming the long-standing trade-off between CO2/CH4 selectivity and CO2 capacity. As a result, MFU-4 achieves CO2/CH4 kinetic selectivity up to twice that of ETS-4 and four times that of CMS-3K, with CO2 working capacities up to seven and four times higher, respectively, over the 100–500 kPa range, and an exceptional CO2 uptake of ∼7.4 mol kg−1 at 298 K and 500 kPa. These findings establish MFU-4 as an excellent molecular sieve for biogas upgrading, delivering performance far beyond current industrial standards.
1 Introduction
The upgrading of biogas, primarily a mixture of methane (CH4) and carbon dioxide (CO2), into pipeline-quality biomethane, a high-value natural-gas substitute, has emerged as a critical process for both renewable energy production and greenhouse-gas mitigation.1,2 Efficient removal of CO2 from the CH4-rich stream not only enhances the calorific value of the purified gas but also decreases volumetric flow, thereby, reducing transportation and compression costs while facilitating downstream processing and handling.3,4 With the growing pressure on circular economy principles and low-carbon energy solutions, adsorption-based technologies for CO2/CH4 separation have garnered substantial attention as energy-efficient alternatives to conventional energy-intensive approaches such as water scrubbing, amine absorption and cryogenic processes.4–6
In this context, several adsorbent materials have been explored for CO2/CH4 separation, predominantly leveraging thermodynamic (equilibrium-driven) selectivity, where CO2 is preferentially adsorbed due to its high polarizability and quadrupole moment which promote stronger interactions with the host frameworks compared to CH4. Among these, zeolites such as 13X,7–14 4A,11,15–18 5A,19–22 together with a wide variety of ion-exchanged derivatives,23–32 have long been regarded as benchmark adsorbents. Their prominence arises from well-defined microporous frameworks and strong CO2 affinity, which arises from specific interactions between CO2 molecules and extra-framework cations, as well as from confinement effects within their uniform pore structures. More recently, metal–organic frameworks (MOFs)33 have emerged as highly tunable alternative porous adsorbents, offering the unprecedented ability to precisely tailor pore size, shape and chemical functionality to enhance interactions with CO2. Representative examples include extended MOF-74 and its amine-grafted frameworks,34–40 which exhibit high CO2 uptake due to strong interactions with open metal sites and/or amine functionalities, as well as small-pore MOFs such as MIL-120(Al),41–43 CALF-20(Zn),44 and NbOFFIVE-1-Ni,45 where CO2 affinity is largely governed by molecular confinement within the pores.
Despite its advantages, this equilibrium-based adsorption strategy often entails substantial energy penalties during adsorbent regeneration and may lead to diminished CH4 recovery, particularly under cyclic operation. In such cases, processes such as Vacuum Pressure Swing Adsorption (VPSA) are typically required to fully regenerate and reset the adsorption bed, further increasing operational complexity and energy demand. These limitations highlight the need for the development of next-generation adsorbents and separation strategies that simultaneously deliver high selectivity, low regeneration energy requirements, and robust operational stability, thereby enabling more sustainable and economically viable biogas upgrading processes. Accordingly, kinetic separation mechanisms offer an attractive alternative to purely equilibrium-driven strategies. In this approach, selectivity originates from differences in diffusion rates or mass-transfer kinetics, driven by variations in adsorption strength and/or steric constraints imposed by the pore dimensions relative to molecular size. Faster-diffusing species are preferentially transported, enabling operation at high feed velocities and short cycle times. Importantly, because CH4 is only weakly adsorbed, regeneration requirements are significantly reduced, lowering purge demand and overall energy consumption.46,47 As a result, CH4 can be efficiently recovered in the raffinate stream with minimal losses to the adsorbent phase.
In this context, two materials have emerged as industrial benchmarks, illustrating the practical viability of diffusion-controlled separations for scalable biogas upgrading. The first is the carbon molecular sieve CMS-3K (commercially supplied by Takeda/Osaka Gas), which displays rapid CO2 adsorption, whereas CH4 uptake can require several days to reach equilibrium, reflecting pronounced kinetic hindrance for CH4 diffusion.48,49 This behavior originates from the ultra-small pore entrances of CMS-3K, whose dimensions closely approach the kinetic diameter of CH4, thereby imposing a strong mass-transfer resistance at the micropore apertures. CMS materials are currently deployed in industrial VPSA processes, including the METHAGEN systems commercialized by SysAdvance.50,51 The second benchmark material, the zeotype ETS-4 (Engelhard Titanosilicate-4), modified with alkaline-earth cations, similarly exploits precise pore-aperture tuning to introduce diffusion barriers or molecular sieving effects that restrict CH4 while favouring smaller or more rapidly diffusing species such as N2 or CO2.52–56 ETS-4 is widely implemented under the Molecular Gate® technology, a registered trademark of BASF Catalysts LLC and exclusively licensed to Guild Associates.57 Despite their clear industrial relevance, both materials exhibit relatively modest equilibrium CO2 adsorption capacities (<3 mol kg−1 at 500 kPa).48,49,56 Consequently, deep vacuum levels (10–20 kPa) are required during regeneration to achieve practical working capacities.58 This dependence on vacuum-intensive operation increases energy demand and process complexity, elevating both capital and operating expenditures (CAPEX and OPEX) and ultimately limiting overall process efficiency.
To overcome these limitations and move beyond the intrinsic trade-off between CO2/CH4 kinetic selectivity and CO2 uptake, alternative classes of materials must be explored. In this regard, ultra-small pore MOFs offer a unique platform to transcend this long-standing compromise, enabling the rational design of diffusion barriers or dynamic pore-gating mechanisms that selectively regulate molecular transport, enabling rapid CO2 diffusion while kinetically restricting CH4, all without sacrificing adsorption capacity within larger internal cavities. Guided by this design principle, we conducted a systematic examination of MOF structural databases and identified MFU-4(Zn)59 (Metal–Organic Framework Ulm University-4) as a particularly promising candidate. Its framework, constructed from Zn-based secondary building units interconnected by benzo[1,2-d:4,5-d′]bistriazolate ligands, features an alternating arrangement of small (∼4 Å) and large (∼12 Å) cages interconnected through ultranarrow, square-shaped pore apertures delimited by four chloride atoms with a limiting diameter of approximately 2.5 Å (Fig. 1a and b). This precise integration of confined apertures and spacious cavities creates an architecture ideally suited to impose strong kinetic constraints on CH4 diffusion while maintaining fast CO2 transport and high CO2 uptake within the larger cages.
 |
| | Fig. 1 (a) Pore network of MFU-4 with alternating large (yellow spheres) and small (green sphere) cages. (b) Square-shaped pore gate, with pore limiting diameter of 2.5 Å, separating the cages. (c) Equilibrium single-component CO2 adsorption isotherms on MFU-4 in the temperature range of 298–343 K. Filled symbols: single-component experimental data; open symbols: CO2 loadings obtained from binary breakthrough experiments; symbols and dashed: GCMC simulations; continuous lines: DSL thermodynamic model fit. (d) Microscopic mechanism of CO2 adsorption in MFU-4 illustrated by a representative GCMC snapshot from simulations at 100 kPa. Two CO2 molecules with the shortest MOF-CO2 distances for each adsorption site are highlighted—one adsorbed at the pore gate (OCO2 in orange; Cl–CCO2 distance: 4.1 Å) and one located inside the large cage (OCO2 in yellow; Cl–CCO2 distance: 6 Å). | |
To validate this concept, we employed a synergistic combination of advanced breakthrough experiments and computational methods, demonstrating that MFU-4(Zn) surpasses the industrial benchmark adsorbents CMS-3K and ETS-4 in CO2/CH4 separation.
2 Methodology
2.1 Synthesis and characterization
2.1.1 Synthesis. The H2-BBTA linker was synthesized according to previously reported procedures, starting from 1,5-dichloro-2,4-dinitrobenzene.59,60 MFU-4 was synthesized in solvothermal conditions by dissolving anhydrous ZnCl2 (136 mg, 1.00 mmol) and H2-BBTA (40 mg, 0.25 mmol) in 4 mL of DMF, transferring the solution to a screw-capped glass pressure tube, and heating at 140 °C for 3 days, followed by cooling to room temperature. The supernatant was removed, and the yellow microcrystalline solid was washed with DMF (3 × 1 mL) and dried in air to afford 65 mg (≈0.056 mmol, 28%) of MFU-4. The product consisted mainly of cubic microcrystals, with a smaller fraction of octahedral crystals, as observed by SEM (see Discussion below).
2.1.2 Characterization. The FT-IR spectrum of the non-activated pristine MFU-4 confirms the successful formation of the Zn–bistriazolate framework and provides clear evidence for the presence of residual guest molecules within the pores (Fig. S1). In particular, a strong absorption band at ∼1652 cm−1 is assigned to the C
O stretching vibration of DMF, indicating that DMF molecules remain confined within the framework after synthesis. Additional bands at ∼2918 and ∼2848 cm−1 corresponding to aliphatic C–H stretching further support the presence of occluded solvent molecules (see Section S1.1.1).The phase purity of the synthesized MFU-4 was confirmed by powder X-ray diffraction (PXRD). The PXRD pattern of the as-synthesized MFU-4 matches well with the simulated pattern generated from the reported single-crystal structure, with all characteristic reflections appearing at the same 2θ positions (Fig. S2). PXRD patterns recorded for materials after activation and CO2 adsorption remain the same as the pristine material indicating that MFU-4 maintains its structural integrity and exhibits excellent stability (Fig. S3).
The scanning electron microscopy (SEM) images of the as-synthesized MFU-4 (Fig. S4) reveal the presence of well-faceted microcrystalline particles exhibiting two distinct morphologies, namely predominantly blocky/cubic-shaped crystals together with a smaller fraction of octahedral crystallites. These morphologies are identified based on their characteristic geometrical features and faceted structures observed in SEM, which reflect different crystal growth habits under solvothermal conditions. The particle size lies in the micrometer range (∼0.5–5 µm), with most crystals typically between 1–3 µm. While an accurate quantitative phase fraction cannot be extracted from SEM images, the cubic morphology is clearly dominant, with octahedral crystals present in lower proportion. To further confirm that both morphologies correspond to the same phase, energy-dispersive X-ray (EDX) analysis was performed on individual crystals. The measured Zn and Cl atomic percentages (Zn ≈ 52.53 at%, Cl ≈ 47.47 at%) correspond to Zn
:
Cl ratios of ∼1
:
0.85 and ∼1.09 for cubic and octahedral crystals, respectively, which are in good agreement with the expected MFU-4 stoichiometry. This confirms that both morphologies belong to the same framework rather than different phases or impurities.
Thermogravimetric analysis (TGA) was performed to evaluate the purity, thermal behavior, and guest (DMF) content of MFU-4 in its as-synthesized form. The TGA profile exhibits a characteristic multistep weight-loss behavior consistent with previous reports and aligns well with the formulation [Zn5Cl4(BBTA)3]·3DMF·6H2O (Fig. S5). Three distinct weight-loss steps are observed. An initial weight loss of ∼9 wt% below ∼80 °C is attributed to the removal of surface-adsorbed moisture and residual lattice water. A second weight loss of ∼18 wt% in the temperature range of 120–300 °C corresponds to the release of approximately three DMF molecules per formula unit, in good agreement with the theoretical DMF content (∼17.18 wt%), confirming that the as-synthesized material is obtained in a solvated state. At higher temperatures (above ∼420 °C), a major weight loss (∼49 wt%) is observed due to framework decomposition. After activation at 250 °C, the TGA curves recorded for MFU-4 following CO2 and N2 sorption measurements (Fig. S6) differ significantly from those of the as-synthesized sample. In particular, the characteristic weight loss associated with DMF in the 120–300 °C range disappears, confirming the complete removal of pore-confined solvent molecules and the formation of the desolvated framework. However, a low-temperature weight loss remains and is significantly increased. This behavior arises from the re-adsorption of moisture upon exposure of the activated sample to ambient air. Once DMF is removed, the internal pore volume becomes fully accessible, enhancing the affinity of the framework toward water. Quantitatively, the low-temperature weight loss increases from ∼9 wt% in the as-synthesized sample to approximately 25–27 wt% in the activated sample, clearly indicating substantial water uptake after activation. This increase reflects the replacement of DMF by adsorbed water molecules within the accessible pores. Importantly, the absence of the intermediate weight-loss step confirms that no DMF remains after activation, and the observed low-temperature loss is solely due to physically adsorbed moisture. This behavior is consistent with literature reports on activated MOFs, where exposure to air leads to rapid water uptake and increased low-temperature mass loss (see Section S1.1.4).
2.2 Fixed bed breakthrough experiments
The single-component adsorption equilibrium data of CO2 was measured using a chromatographic technique based on dynamic fixed-bed breakthrough experiments. The experimental setup comprises three main sections: (1) gas preparation, (2) adsorption, and (3) analysis. In the gas preparation section, he carrier gas and CO2 were fed through mass flow controllers, while system pressure was set by back-pressure regulators. The adsorption section contained a stainless-steel column filled with the agglomerated MFU-4 and placed inside a temperature-controlled water bath. The outlet from the fixed bed was directed to the analytical section, where a gas chromatograph equipped with a thermal conductivity detector (TCD) which continuously monitored the CO2 concentration. For CO2/CH4 binary breakthrough experiments, the same procedure was applied. In this case, the feed gas mixture was set in the gas preparation section, and a pre-programmed six-port valve periodically directed aliquots of the outlet stream to a packed column for peak separation before analysis by the TCD detector. Further details on the setup, procedure, and operating conditions are provided in the SI.
2.3 Modelling and numerical simulations
The Aspen Adsorption v11 package61 was employed to numerically simulate the binary breakthrough experiments. Input data for these simulations were obtained from adsorption equilibrium data (experimental for CO2 and simulated for CH4), modelled using the Dual-Site Langmuir (DSL) isotherm.62 To analyze mass transfer kinetics, a linear driving force (LDF) model was applied,63 which is based on the solid-phase concentration gradient and has been satisfactorily validated in previous studies.64,65 Complete details of the assumptions, model equations, parameter correlations, and numerical procedures used to solve the partial differential equations (PDEs) are provided in the SI.
2.4 Molecular simulations and quantum calculations
The crystal structure of MFU-4 was geometry-optimized using periodic density functional theory (DFT) as implemented in the Vienna Ab initio Simulation Package (VASP).66 Calculations were performed using the Perdew–Burke–Ernzerhof (PBE) exchange–correlation functional67 in conjunction with projector-augmented wave (PAW) pseudopotentials68 and Grimme's D3 dispersion correction with Becke–Johnson damping.69,70 Both atomic positions and lattice parameters were relaxed using the conjugate-gradient algorithm with a plane-wave energy cutoff of 600 eV. Convergence criteria of 10−6 eV for the total energy and 0.01 eV Å−1 for atomic forces were applied. Brillouin-zone sampling was carried out using a 2 × 2 × 2 Monkhorst–Pack k-point mesh.71 The electronic charge density of the optimized structure was subsequently used to derive atom-centered partial charges using the DDEC6 method, as implemented in the Chargemol package.72–75
Grand canonical Monte Carlo (GCMC) simulations were first performed to predict the single component adsorption isotherms of CO2 and CH4 in MFU-4 at three temperatures (298 K, 313 K, and 343 K) and pressures up to 500 kPa. CO2 and CH4 were modeled using the EPM2 (ref. 76) and TraPPE united-atom77 force fields, respectively, while Lennard-Jones (LJ) parameters for the framework atoms were taken from the Universal Force Field (UFF).78 LJ interactions between the adsorbates and the octahedrally coordinated Zn atoms were excluded, as these metal centers are deeply shielded within the Kuratowski-type nodes and are effectively inaccessible to guest molecules. Lorentz–Berthelot mixing rules were applied for cross-interactions. Simulations were performed in a 2 × 2 × 2 supercell, employing a cutoff distance of 12 Å for both van der Waals and electrostatic host–guest interactions. Long-range electrostatic interactions were treated using the Ewald summation method. For each pressure point, 2 × 107 Monte Carlo cycles were used for both equilibration and production. All GCMC simulations were performed using Complex Adsorption and Diffusion Simulation Suite (CADSS).79 The adsorption enthalpies at zero coverage for CO2 and CH4 were also calculated using the revised Widom's test particle insertion method.80 The LJ parameters and partial charges for the atoms of MFU-4 and both adsorbates are provided in Tables S2 and S3, respectively.
The energy barrier associated with crossing the pore gate of MFU-4, which separates alternating large and small cages, was evaluated for both CO2 and CH4 using climbing-image nudged elastic band (CINEB)81 calculations as implemented in the Quickstep module of the CP2K package.82 The calculations employed the PBE functional with D3/Becke–Johnson dispersion correction, together with triple-ζ valence polarized (TZVP) Gaussian basis sets83 and Goedecker–Teter–Hutter (GTH) pseudopotentials84,85 for all atoms. An auxiliary plane-wave cutoff of 500 Ry was used. To model migration across the pore gate, a supercell containing two unit cells along the a-direction was constructed. The initial and final states were generated by placing a single adsorbate molecule (CO2 or CH4) on either side of the pore gate, followed by full relaxation of atomic positions. The minimum-energy pathway was resolved using seven intermediate images, with a force convergence criterion of 5 × 10−4 hartree.
3 Results and discussion
The equilibrium single component CO2 adsorption isotherms of MFU-4 were derived from breakthrough experiments performed at 298 K, 313 K, and 343 K over pressures up to 500 kPa (see Table S4 and Fig. S8). The experimentally obtained equilibrium data are compared with the corresponding GCMC simulated adsorption isotherms in Fig. 1c. At all three temperatures, experimental and simulated isotherms are in good agreement and exhibit a characteristic IUPAC Type I profile typical of microporous adsorbents, with a steep increase in CO2 uptake at low partial pressures followed by a gradual approach to saturation.86 The moderately rounded “knee” of the isotherm suggests the presence of more than one adsorption environment. The DSL model provides a robust description of the experimental data over the entire pressure range, indicating that CO2 adsorption can be rationalized by two families of adsorption sites with comparable affinities but different saturation capacities (see Table S6 for the fitted parameters). This interpretation is supported by the analysis of GCMC configurations which reveals two distinct adsorption sites, one near the Cl atoms delimiting the pore gates and a second situated within the larger cages (Fig. 1d) (see Fig. S10 for more details). The isosteric heat of adsorption (Qst) for CO2, estimated using the Clausius–Clapeyron relation (Fig. S12), remains essentially constant over the investigated loading range, at ∼24.7 kJ mol−1 in line with the previously reported experimental values (∼24.4 kJ mol−1)87 and our simulated adsorption enthalpy at infinite dilution (∼24 kJ mol−1).
Adsorption of CH4 in MFU-4 could not be detected using the flow chromatographic method, most likely due to its extremely slow diffusion within the MOF, resulting in breakthrough times that occur almost simultaneously with the gas residence time in the fixed bed. To validate this hypothesis, DFT-CINEB calculations were performed to quantify the energy barriers for guest migration across the pore gates of MFU-4. Minimum energy pathways (MEPs) were determined by positioning a guest molecule on either side of an individual pore gate as the initial and final states. The resulting MEPs for CH4 and CO2 crossing the pore gate are shown in Fig. 2a and b, respectively. CH4 faces a substantial energy barrier of ∼53 kJ mol−1, with a well-defined transition state at the centre of the gate. This large barrier reflects severe steric hindrance, as the spherical CH4 molecule (kinetic diameter ∼3.8 Å) must pass through a square aperture with a pore limiting diameter of only ∼2.5 Å. In contrast, the MEP for CO2 shows the pore gate as a local energy minimum rather than a transition state. The square gate provides confinement-enhanced stabilization for the linear CO2 molecule, consistent with GCMC simulations that identify the gate region as the primary adsorption site. Transport of CO2 between adjacent cages is therefore not limited by an enthalpic barrier but is instead controlled by entropic constraints arising from confinement and molecular orientation. These findings suggest that MFU-4 can achieve size selective CO2 adsorption over CH4 via a predominantly kinetically controlled mechanism.
 |
| | Fig. 2 Minimum-energy pathways for (a) CH4 and (b) CO2 migration across the pore gate (highlighted by thicker sticks) from the large cage to the small cage of MFU-4, obtained from DFT-based CINEB calculations. The molecules are represented only by their respective center of mass (carbon atom) for convenience of visualization. For CH4, points A, B, and C represent the initial state, transition state, and final state, respectively. For CO2, points A′, B′, and C′ correspond to the initial state, a local energy minimum at the pore gate, and the final state. In both cases, A (A′) lies within the large cage, B (B′) at the center of the pore gate, and C (C′) at the center of the smaller cage. | |
As a further step, we experimentally investigated the competitive adsorption of CO2 and CH4 under dynamic flow conditions. Accordingly, breakthrough experiments were performed for CO2/CH4 mixtures of 50
:
50 and 10
:
90 at total pressures of 100 and 500 kPa in the same range of temperature covered in the single-component adsorption measurements (see Table S7 for experimental conditions) under typical biogas upgrading conditions for PSA cyclic adsorption. These feed compositions provide a simple and industry-relevant reference condition, where the selected pressure interval reflects practical CO2 capture and upgrading conditions of the feed to produce pure CH4, near room temperature and at atmospheric to moderately elevated pressures relevant for cyclic PSA operation. It should be noted that, although raw biogas streams may contain trace contaminants such as H2S and water, these species are typically removed during upstream conditioning, including desulfurization and dehydration steps (e.g., guard beds). This is standard practice in commercial biogas upgrading systems, ensuring that the feed entering the adsorption unit is effectively dry and free of contaminants that could compromise the performance of the core process. In contrast to post-combustion streams, which are often treated directly under humid conditions, biogas streams are routinely pre-conditioned prior to separation.
Representative breakthrough curves for CO2/CH4 mixtures at 298 K are shown in Fig. 3. In all cases, CH4 elutes almost immediately at the residence time of the gas in the column, indicating that the bulk CH4 stream bypasses the adsorbent due to strong diffusional limitations as revealed by the DFT-derived MEPs. By contrast, CO2 exhibits a clear and well-defined adsorption front, with the expected breakthrough around the stoichiometric time linked to the adsorption equilibrium concentration that relates to the feed saturation at equilibrium conditions. Moreover, the quantification of CO2 loading from the mixture breakthrough curves (shown as empty markers in Fig. 1c) reveals that the CO2 uptake under binary flow conditions closely matches the corresponding single-component values indicating, no competitive adsorption with CH4. This one-to-one correspondence demonstrates that CH4 does not effectively compete for adsorption sites, and CO2 adsorption proceeds as if CH4 were absent, a hallmark of a kinetically selective adsorption mechanism. Dilution of CO2 in the feed from 50
:
50 to 10
:
90 has only a minor effect on the breakthrough profiles: the CO2 front remains sharp and CH4 continues to elute at the space time of the gas in the bed. Increasing the total pressure from 100 to 500 kPa proportionally enhances CO2 uptake, consistent with the equilibrium isotherm, while leaving the kinetic exclusion of CH4 unaffected. This kinetically selective behavior was confirmed by multiple adsorption/desorption cycles performed for a CO2/CH4 feed composition of 50
:
50 vol%, which yielded highly reproducible breakthrough curves (Fig. S15). The CO2 adsorption capacity remained essentially unchanged over ten consecutive cycles, while CH4 continued to behave as a non-adsorbing component, indicating the absence of CH4 accumulation in the material and no loss of separation performance.
 |
| | Fig. 3 CO2/CH4 binary mixtures breakthrough curves on MFU-4 at 298 K. Conditions for each panel are: (a) CO2/CH4 50 : 50 at 100 kPa, (b) CO2/CH4 50 : 50 at 500 kPa, (c) CO2/CH4 10 : 90 at 100 kPa, and (d) CO2/CH4 10 : 90 at 500 kPa. Data are plotted as component molar fraction (left y-axis) versus total moles fed per unit mass of adsorbent. Symbols represent experimental data, and continuous lines represent numerical simulations. | |
To further quantify the kinetic discrimination between CO2 and CH4, the breakthrough experiments were modeled using the Aspen Adsorption software, with the simulated profiles shown as continuous lines in Fig. 3. In these simulations, the mass-transfer coefficient of CH4 (kLDF(CH4)) at 100 kPa was systematically varied to capture the experimentally observed inert-like behavior of CH4 with MFU-4. The kLDF(CH4) parameter was progressively reduced until agreement with the experimental breakthrough data was achieved. For kLDF(CH4) ≤ 1.0 × 10−4 s−1, the predicted CH4 breakthrough curves become insensitive to further decreases in kLDF and fully overlap with the experimental profiles, indicating that this value corresponds to a limiting diffusivity below which CH4 breakthrough occurs essentially at the gas residence time in the fixed bed. By contrast, the CO2 breakthrough curve profile is well reproduced with a kLDF(CO2) value of 1.5 × 10−1 s−1, which is approximately three orders of magnitude greater than the one for CH4. This trend confirms that the transient column response is governed almost exclusively by CO2 diffusion and adsorption inside the framework, while CH4 behaves effectively as a dynamically non-adsorbing component, supporting that CO2/CH4 separation in MFU-4 is kinetically-governed giving rise to a molecular sieve separation of both components. Aspen Adsorption allows the kLDF to incorporate combined temperature and pressure dependencies, following an Arrhenius-type expression for temperature and a first-order dependency on total pressure (eqn (S7)). Within this framework, the kLDF coefficients employed for the breakthrough simulations at 500 kPa were obtained by scaling those determined at 100 kPa by a factor of five. Importantly, using the same kLDF(CO2)/kLDF(CH4) ratio yields excellent agreement with the experimental breakthrough profiles at 500 kPa (Fig. 3b and d), demonstrating that the pronounced difference in diffusion kinetics between CO2 and CH4 is preserved at elevated pressure. This result further confirms that CO2/CH4 separation in MFU-4 remains kinetically governed under elevated pressure conditions relevant to industrial operation, with CH4 continuing to behave as a dynamically non-adsorbing component.
Breakthrough curves at 313 and 343 K, together with their corresponding dynamic simulations, are equally provided in Fig. S13 and S14. Although increasing the temperature reduces the overall CO2 uptake, the qualitative features of the breakthrough profiles remain unchanged: CH4 elutes at the space time of the gas in the bed whereas CO2 is selectively adsorbed. The numerical simulations accurately reproduce these experimental profiles, reinforcing the conclusion that MFU-4 maintains strong kinetic sieving behavior over a wide range of operating conditions relevant to natural gas upgrading and biogas purification strategies, especially by PSA. The full set of kinetic parameters for the CO2 and CH4 simulations (including k∞, Ei, and kLDF at each temperature and pressure) are provided in Table S8.
The performance of MFU-4 was evaluated against the two industrially established benchmark adsorbents CMS-3K and ETS-4, using CO2 adsorption equilibrium uptake, kinetic selectivity (Habgood formulation, eqn (S10)) and working capacity (100–500 kPa, eqn (S11)) as key performance metrics. Fig. 4a reports the single component CO2 adsorption isotherms for MFU-4 at near-ambient temperature and the same data reported previously for the benchmark adsorbents ion exchanged ETS-4 and CMS-3K. The comparison highlights that MFU-4 exhibits a much higher CO2 uptake across the entire pressure range. In particular, MFU-4 reaches a CO2 loading of ∼7.4 mol kg−1 at 500 kPa, substantially exceeding the uptakes of CMS-3K, Ba-ETS-4 and Sr-ETS-4 which remain below 3.0 mol kg−1 over the same pressure range. This superior uptake directly translates into outstanding CO2 working capacities for both (50
:
50) and (10
:
90) CO2/CH4 mixture feeds over the 100–500 kPa range at 298 K. For a (50
:
50) mixture, MFU-4 delivers a working capacity of 3.93 mol kg−1, exceeding those of CMS-3K (0.94 mol kg−1) and ETS-4 variants (<0.60 mol kg−1) by more than fourfold and six-fold, respectively (Fig. 4b and c). Remarkably, even under the more demanding 10
:
90 feed composition, MFU-4 retains a high working capacity of 1.52 mol kg−1, outperforming CMS-3K and ETS-4 by approximately two- to fourfold, highlighting its attractiveness under industrially relevant conditions.
 |
| | Fig. 4 Comparison of MFU-4 performance (this work) with benchmark adsorbents (ETS-4 variants,54–56 CMS-3K48) for CO2/CH4 separation at near-ambient temperature. (a) Equilibrium single-component CO2 adsorption isotherms at 298 K. (b–c) CO2 working capacity versus kinetic selectivity for (b) 50 : 50 and (c) 10 : 90 CO2/CH4 mixtures. | |
Decisively, this exceptional CO2 working capacity is coupled with an unprecedented level of kinetic selectivity. MFU-4 attains a kinetic selectivity of 67, outperforming Ba-ETS-4 and Sr-ETS-4 by approximately 90–150% and exceeding CMS-3K by more than 300% (see Table S9 for detailed values). Achieving such simultaneous superiority in both uptake swing and kinetic discrimination is extremely rare in microporous adsorbents and, to date, has not been realized by any industrial benchmarks. In existing technologies based on ETS-4 and CMS-3K, comparable working capacities can only be approached through vacuum-assisted regeneration, which substantially increases the energy penalty and operating costs of VPSA processes.
Beyond this direct comparison with industrial benchmarks, a broader evaluation against representative adsorbents reported for biogas upgrading, primarily governed by thermodynamic separation mechanisms, further highlights the distinctive performance of MFU-4 (see Table S10). In terms of CO2 adsorption capacity, at 298 K and 100 kPa, MFU-4 exhibits an uptake of 3.61 mol kg−1, which is higher than that of silica-based materials (∼0.3–1.0 mol kg−1),88–90 periodic mesoporous organosilicas (PMOs, ∼0.5–1.2 mol kg−1),91 pillared clays (∼0.5–1.5 mol kg−1),92 and typical activated carbons (∼1.7–2.5 mol kg−1).93–96 With respect to other MOFs, MFU-4 shows a mixed uptake profile: it outperforms several materials, including MIL-101(Cr) (1.49 mol kg−1),97 IITKGP-21a (1.86 mol kg−1),98 CAU-10 (up to 2.3 mol kg−1),99 ZU-301 (2.41 mol kg−1),100 MIL-53 and MIL-125(Ti) (up to 2.64 mol kg−1),9,97,101 UiO-66(Zr) (up to 2.69 mol kg−1),101 and others,102,103 while remaining comparable to MIL-100 (up to 3.5 mol kg−1),101 MIL-120(Al) (3.56 mol kg−1),43 and MIL-160(Al) (3.89 mol kg−1).104 However, lower CO2 uptake is observed when compared to TAMOF-1,105 ZJU-8a,106 Cu-BTC,101 UTSA-16/120,107,108 SIFSIX-type materials,108 with values collectively spanning 4.0–5.5 mol kg−1, as well as Mg-MOF-74 (8.32 mol kg−1),36 known for its exceptional CO2 adsorption capacity. A similar trend is observed for zeolites, where MFU-4 exhibits higher uptake than DDR (1.37 mol kg−1),109 Na-ZSM-5 (1.39 mol kg−1),110 silicalite-1 (1.69 mol kg−1),109 beta (2.05 mol kg−1),109 and 5A (3.06 mol kg−1),20 while remaining lower than 4A (4.29 mol kg−1),15 13X (4.58 mol kg−1),7 NaX (4.82 mol kg−1),101 and NaY (5.44 mol kg−1).111 Importantly, at higher pressure (500 kPa), the experimental CO2 uptake of MFU-4 reaches ∼7.36 mol kg−1, exceeding the capacity of several materials that outperform it at lower pressure, thereby highlighting its strong adsorption capability across the range relevant for practical applications. Under these conditions, In terms of CO2 uptake, MFU-4 is only surpassed by a limited number of MOFs, such as ZJU-8a,106 Cu-BTC,101 and Mg-MOF-74,36 with reported values ranging from 10.5 to 12.9 mol kg−1.
In terms of adsorption energetics, MFU-4 presents a moderate CO2 affinity (i.e. Qst of 24.7 kJ mol−1), which, relative to high-capacity MOFs, is comparable to that of ZJU-8a (19.5–21.9 kJ mol−1),106 while remaining significantly lower than that of Mg-MOF-74 (45.3–72.7 kJ mol−1).36 This further highlights the favorable balance between adsorption strength and regenerability of MFU-4. In terms of CO2/CH4 selectivity, MFU-4 exhibits a high value of 67 when evaluated using the Habgood formulation (eqn (S10)), a kinetic-based approach that integrates both equilibrium and kinetic contributions. This value already lies within the upper range of materials collected in Table S10. It is important to note that different approaches are commonly used to evaluate thermodynamic selectivity (see Section S3.2), leading to a wide range of reported values depending on the method employed. To enable a more consistent comparison with materials governed by equilibrium-based separation mechanisms, it is instructive to consider selectivity values derived from breakthrough experiments, which better reflect practical operating conditions. In this context, high selectivities for CO2/CH4 mixtures (∼50
:
50 vol%) have been reported for materials such as zeolite 13X (88),9 MIL-120 (89.3),43 and NH2-MIL-53(Al) (207)9 at 100 kPa and 298–303 K. In the case of MFU-4, a fundamentally different behavior is observed. Breakthrough experiments reveal that CH4 is effectively excluded from the framework due to severe diffusion limitations, resulting in negligible adsorption of this component. Consequently, when selectivity is evaluated directly from dynamic adsorption data, it can be considered essentially infinite for MFU-4.
Taken together, these results demonstrate that MFU-4 represents a step change in adsorbent performance for biogas upgrading, uniquely overcoming the long-standing trade-off between CO2/CH4 selectivity and uptake. By combining high working capacity, moderate adsorption energetics, and effectively infinite kinetic selectivity under dynamic conditions, MFU-4 enables high-efficiency separations without reliance on energy-intensive vacuum operation, setting it apart from both industrial benchmarks, such as CMS-3K and ETS-4, and state-of-the-art materials reported in the literature. Beyond separation performance, scalability and synthesis cost are critical considerations for industrial application. In this context, MFU-4 can be synthesized via relatively straightforward solvothermal methods using commercially available precursors, and its components are, in principle, amenable to scale-up. However, there are no detailed studies on the industrial scalability and the production cost of this MOF. As commonly observed in MOF chemistry, the cost associated with ligand and synthesis can be significantly reduced through the development of optimized synthetic routes and bulk production strategies.
4 Conclusions
In summary, we demonstrate that the ultra-microporous Zn triazolate MOF MFU-4 acts as an exceptionally efficient kinetic molecular sieve for CO2/CH4 separation, decisively outperforming industrial benchmark adsorbents such as CMS-3K and ion-exchanged ETS-4. Owing to its favorable architecture, which combines ultra-narrow pore gates with large cavities, MFU-4 uniquely delivers both high kinetic selectivity and high CO2 working capacity, thereby explicitly breaking the long-standing trade-off between selectivity and uptake that constrains conventional molecular sieves. For a 50
:
50 CO2/CH4 mixture, MFU-4 achieves a CO2 working capacity of 3.93 mol kg−1, more than four and six times higher than CMS-3K (0.94 mol kg−1) and ETS-4 variants (<0.60 mol kg−1), respectively, while simultaneously reaching an exceptional kinetic selectivity of 67. This unprecedented combination enables efficient cyclic PSA operation over the industrially relevant 100–500 kPa pressure range without the need for vacuum-assisted regeneration. Together, these results establish MFU-4 as a showcase for the development of next-generation MOF adsorbent that redefines performance limits for energy-efficient biogas upgrading. Ongoing efforts should be now directed toward exploring alternative, more scalable synthesis approaches (e.g., reflux-based methods) of MFU-4 to enable larger-scale production while maintaining material performance in order to facilitate its industrial translation.
Conflicts of interest
There are no conflicts to declare.
Data availability
Raw experimental and computational data and simulation files are available from the corrresponding authors upon reasonable request.
Supplementary information (SI): characterization of MFU-4; detailed description of the experimental and computational adsorption studies; additional experimental and computational results; benchmarking of MFU-4 against reported adsorbents. See DOI: https://doi.org/10.1039/d6ta01917j.
Acknowledgements
Adriano Henrique and José A. C. Silva acknowledge Portuguese national funds through FCT/MCTES (PIDDAC): CIMO UID/00690/2025 (https://doi.org/10.54499/UID/00690/2025) and UID/PRR/00690/2025 (https://doi.org/10.54499/UID/PRR/00690/2025); SusTEC, LA/P/0007/2020 (DOI: https://doi.org/10.54499/LA/P/0007/2020). Guillaume Maurin thanks Institut Universitaire de France for the Senior Chair.
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