Skip to main content
ACS AuthorChoice logoLink to ACS AuthorChoice
. 2016 Dec 16;121(2):1171–1181. doi: 10.1021/acs.jpcc.6b10363

Rational Design of a Low-Cost, High-Performance Metal–Organic Framework for Hydrogen Storage and Carbon Capture

Matthew Witman , Sanliang Ling , Andrzej Gladysiak §, Kyriakos C Stylianou §, Berend Smit †,§, Ben Slater , Maciej Haranczyk ∥,⊥,*
PMCID: PMC5253711  PMID: 28127415

Abstract

graphic file with name jp-2016-10363u_0009.jpg

We present the in silico design of a MOF-74 analogue, hereon known as M2(DHFUMA) [M = Mg, Fe, Co, Ni, Zn], with enhanced small-molecule adsorption properties over the original M2(DOBDC) series. Constructed from 2,3-dihydroxyfumarate (DHFUMA), an aliphatic ligand which is smaller than the aromatic 2,5-dioxidobenzene-1,4-dicarboxylate (DOBDC), the M2(DHFUMA) framework has a reduced channel diameter, resulting in higher volumetric density of open metal sites and significantly improved volumetric hydrogen (H2) storage potential. Furthermore, the reduced distance between two adjacent open metal sites in the pore channel leads to a CO2 binding mode of one molecule per two adjacent metals with markedly stronger binding energetics. Through dispersion-corrected density functional theory (DFT) calculations of guest–framework interactions and classical simulation of the adsorption behavior of binary CO2:H2O mixtures, we theoretically predict the M2(DHFUMA) series as an improved alternative for carbon capture over the M2(DOBDC) series when adsorbing from wet flue gas streams. The improved CO2 uptake and humidity tolerance in our simulations is tunable based upon metal selection and adsorption temperature which, combined with the significantly reduced ligand expense, elevates this material’s potential for CO2 capture and H2 storage. The dynamical and elastic stabilities of Mg2(DHFUMA) were verified by hybrid DFT calculations, demonstrating its significant potential for experimental synthesis.

Introduction

Porous materials have been extensively studied as potential adsorbents in energy and environmental applications including hydrogen storage and carbon capture.17 Among the various porous solids, metal–organic frameworks (MOFs), which are typically constructed from building blocks including inorganic metal (oxide) secondary building units (SBUs) and organic ligands, have attracted significant interest since their composition (i.e., chemical functionality) and structure (e.g., pore topology and sizes and internal surface areas) are highly tunable.8 Hence their performance for a given application can be systematically improved by rational materials design.914 With respect to hydrogen storage and carbon capture (e.g., from flue gas) applications, one of the most important factors which dictates the amount of H2 and CO2 that can be adsorbed in a MOF material is the adsorbate–adsorbent interactions, with MOF-74 being considered as one of the best performing MOFs because of the presence of a high density of open metal sites that interact strongly with H2 and CO2 molecules.1517

Despite the many advantages of MOFs that result from high tunability of chemistry and structure, the cost of MOF production is still a major factor that impedes their large-scale industrial applications. Apart from the capital investment in infrastructures, the cost of MOF production consists largely of raw materials (including metal salts and organic ligands) and processing, which include but are not limited to nonreusable organic solvents and cost associated with activation. For MOF-74 with a molecular formula M2(DOBDC) (M = Mg, Zn, Fe, etc. and DOBDC = 2,5-dioxido-1,4-benzenedicarboxylate), the major cost of raw materials comes from the organic ligand (i.e., DOBDC). Taking Mg-MOF-74 as an example, the cost of metal salts, usually MgCl2, can almost be neglected; i.e., it accounts for only a small percentage of the expense of organic ligands. Indeed, MOFs built from much cheaper organic ligands will need to be developed before they can be widely used in industry in large quantities. Generally speaking, larger and longer aromatic organic ligands are more expensive than smaller and shorter aliphatic ligands. However, the majority of the MOFs synthesized so far features aromatic organic ligands because the coordination-driven self-assembly of building blocks to produce porous crystalline MOFs requires the molecular precursor to be rigid and possess proper directionality.18 Such properties are more likely to appear in conjugated organic ligands, e.g., DOBDC and BDC (BDC = 1,4-benzenedicarboxylate), both of which are frequently used in the synthesis of MOFs. On the other hand, most of the aliphatic ligands are flexible and do not have sites to form directional metal–ligand bonds, and they are less likely to form porous and crystalline solids with metal centers. Therefore, aliphatic ligands are rarely employed in MOF synthesis. Nevertheless, there are still several MOFs based on aliphatic ligands,1921 including the commercially available aluminum fumarate (Basolite A520).22 However, there are no open metal sites in these MOFs, thereby limiting their CO2 and H2 storage potential at low and ambient pressures. It would be extremely useful to develop a MOF-74 analogue featuring both open metal sites, which lead to enhanced adsorbate–adsorbent interactions and higher gas uptake at ambient pressure, and cheap aliphatic linkers, which lower the overall raw materials cost. To the best of our knowledge, all the MOF-74 analogues which have been experimentally synthesized so far were constructed from longer, aromatic organic linkers and are therefore likely to be more expensive with limited improvement on gas adsorption capacity in low to ambient pressure regimes.

Another popular approach to increase the gas adsorption capacity of MOFs is to synthesize MOFs with expanded pores and larger internal surface areas, e.g., by replacing the DOBDC linker in MOF-74 with longer linkers.23 We investigated the effectiveness of pore expansion in MOF-74 analogues in one of our recent high-throughput screening studies,24 whereby we developed a novel in silico crystal assembly algorithm that differed from previous approaches2529 to create a library of MOF-74 analogues which exhibit 1-D metal-oxide rod building units.30 We found that the gravimetric uptake of CO2 dropped significantly in MOF-74 analogues with higher pore volumes due to the spatial and gravimetric dilution of the open metal sites which serve as the strong adsorption sites for CO2 molecules. Thus, the increased pore volume in these analogues (which results from construction with extended ligands) sacrifices gravimetric uptake and further complicates synthesis by introducing more complex organic molecule building units and by potentially reducing mechanical stability. Therefore, larger pore sizes are not always desirable. While many efforts have been made to tune and improve upon the exceptional small molecule adsorption properties of the original MOF-74 framework,3135 we undertake a rational design approach to further improve the gas adsorption capabilities in MOF-74 analogues by increasing the density of open metal sites, e.g., by replacing the DOBDC linker with a smaller molecule. While DOBDC represents the smallest aromatic molecule that satisfies the topological requirement of MOF-74, an even smaller molecule can be identified from the thousands of aliphatic molecules which are smaller in size than DOBDC.

In this work, we rationally design in silico a MOF-74 analogue based on a cheaper and commercially available aliphatic ligand, i.e., DHFUMA (DHFUMA = 2,3-dihydroxyfumarate), and simulate its H2, CO2, and H2O adsorption properties, based on extensive previous work dedicated to describing the energetic interactions of small molecules in the MOF-74 framework.3640 Namely, we predict significantly improved H2 volumetric storage capacity, increased low-pressure CO2 adsorption, and higher CO2:H2O selectivity in the M2(DHFUMA) series than the M2(DOBDC) series. The cost (per mol) of DHFUMA is lower than that of DOBDC by more than 80% from the commercial vendor Sigma-Aldrich, and the volumetric density of open metal sites in M2(DHFUMA) is twice of that of M2(DOBDC). Typical protocols used to synthesize M2(DOBDC) have been tested and shown to result in a crystalline material that is not the desired M2(DHFUMA) product (see Supporting Information); however, calculation of the elastic constants and vibrational frequencies demonstrates the dynamical and mechanical stability of M2(DHFUMA) and provides justification that the material can be synthesized. M2(DHFUMA), if it can be synthesized in large quantities, has the potential to be a better candidate than M2(DOBDC) for industrial applications including hydrogen storage and carbon capture.

Methods

In Silico Crystal Design

Part of our recent work has focused on the in silico crystal design of 1-D rod MOFs.24 The building blocks of these MOFs are embedded in three-dimensional space by an optimization routine that is constrained by geometric rules that must hold for a 1-D rod MOF. Utilizing this method allows for facile substitution of DOBDC for DHFUMA into the MOF-74 framework and quickly creates an accurate starting crystal structure for DFT optimization. Figure 1 demonstrates the analogous connectivity groups in DHFUMA and DOBDC. We believe this to be the smallest possible ligand with which a MOF-74 analogue can be constructed. Dispersion-corrected DFT optimization was performed to relax the M2(DOBDC) and M2(DHFUMA) frameworks and obtain partial atomic charges for each unique atom type in the framework.

Figure 1.

Figure 1

DOBDC ligand and framework is visually compared to the DHFUMA ligand and framework. (1, 1′, 1″) oxygens connect to one metal rod in the MOF-74-type framework, and (2, 2′, 2″) connect to an adjacent metal rod. The distance between adjacent open metal sites is shown to be 2 Å shorter in the Mg2(DHFUMA) framework.

DFT Calculations

A majority of the periodic density functional theory calculations, including geometry and cell optimizations, have been performed using the CP2K code which uses a mixed Gaussian/plane-wave basis set.41,42 We have used both gradient-corrected (i.e., PBE43) and hybrid density functional (i.e., PBE044,45 with 25% Hartree–Fock exchange) methods. It is known that a correct description of the dispersion interactions is important to predict the MOF structures and host–guest interactions in MOFs.46,47 In this work, we have used one of the most popular pairwise additive descriptions of the dispersion interactions as developed by Grimme et al., i.e., the D3 method48 with the Axilrod–Teller–Muto three-body terms, in combination with the conventional PBE and PBE0 functionals. The same method was used in our previous work on MIL-53,49,50 UiO-66,51 and MOF-7424 types of MOFs, and we achieved very good agreement between theory and experimental results on structures and calorimetric measurements. We note that a hybrid functional is necessary here to provide a correct description of the electronic structures and host–guest interactions of MOF-74 materials featuring M2+ cations with unpaired electrons, including Mn2+, Fe2+, Co2+, Ni2+, and Cu2+. The Hartree–Fock exchange calculations, which are part of the hybrid DFT functional PBE0, were performed and significantly accelerated using the auxiliary density matrix method (ADMM),52 which enables us to consider relatively large systems (with the largest system containing 489 atoms) at the hybrid DFT level. The partial atomic charge analysis was performed using the REPEAT method proposed by Campana et al.,53 which was recently implemented into the CP2K code based on a restrained electrostatic potential framework.54 The REPEAT method calculates partial atomic charges from electrostatic potentials determined from DFT calculations, and only the grid points outside the van der Waals radii of each atom were included in the fitting. We have used partial atomic charges determined using the REPEAT scheme in our recent work on MOF-74, in which very good agreement was obtained between theory and experiment on the adsorption isotherms of CO2 molecules.24 The vibrational frequency and elastic constant calculations were performed using the CRYSTAL code55,56 with the B3LYP hybrid functional.57 More details of the calculations are included in the Supporting Information.

Classical Simulations and Pore Characterization

A critical component in the classical molecular simulation of nanoporous materials is the parametrization of classical potential energy functions (or force fields) that can accurately describe the energetics of host−guest systems. Many times off-the-shelf force fields such as UFF58 or Dreiding59 are used in lieu of a more accurate alternative, but this approach breaks down with MOFs that contain complex electronic structure features such as open metal sites.37 Several different approaches have been used specifically to generate force fields which successfully describe gas interactions in MOF-74 type frameworks which contain these open metal sites.37,60,61 Pham et al. used a many-body polarization approach to classically capture the complex H2–open metal site interactions in the Mg2(DOBDC) framework and later extended their force field development to the entire metal series.40,62 In this work, the model of Pham was used to model H2 adsorption in Mg2(DOBDC) and Mg2(DHFUMA), and we refer the reader to these publications for further details. The grand canonical Monte Carlo (GCMC) simulations of H2 with many-body polarization were calculated with the RASPA2 software package.63

Mercado et al. used a recently developed approach to parametrize the potential energy surface for the isoreticular series M2(DOBDC) [M = Mg, Mn, Fe, Co, Ni, Zn] such that classical molecular simulation of CO2 and H2O could be performed for the entire metal series for the first time.39 The parametrization was peformed by calculating DFT single-point energies along the path of minimum repulsion between unique guest–host pairwise types to accurately capture the repulsive behavior between the guest and the excess electon density at the open metal sites. We adopt this force field parametrization for studying the adsorption properties of CO2 and H2O in DHFUMA and refer the reader to this publication for specific details and the parameters themselves. The unique types assigned to each atom in the DHFUMA crystal structure and their correspondence to the atom types of Mercado’s force field are shown in the Supporting Information, in addition to a justification for the transferability of the force field. GCMC simulations were executed to calculate adsorption isotherms and isosteric heats of adsorption of the frameworks under consideration. An annealing minimization scheme was used to determine the classical binding energy of adsorbates in all analogues. In this scheme, an NVT ensemble Monte Carlo simulation consisting of one asorbate molecule is successively quenched from T = 298 K to T = 1 K. The potential energy of the final configuration in the T = 1 K simulation then corresponds to the classical binding energy. The porosity characterization of all frameworks was performed with the Zeo++ application using the high accuracy settings.64,65

Results

Porosity Characterization

The channel geometry of the Mg analogues of the DHFUMA and DOBDC series were analyzed by Zeo++ to demonstrate the differences in porosity which are later shown to have a significant impact on the adsorption properties of the two frameworks. A probe radius of 1.65 Å was used which corresponds to the kinetic diamter of CO2. Table 1 summarizes these important geometric quantities. We note that the distance between the centers of two metal rods opposite each other in a single hexagon of DHFUMA, i.e., the approximate diameter of a single channel, is equal to 12.6 Å. When accounting for the Van der Waal’s radii of the framework atoms in DHFUMA, the largest free and included spheres are close to half of this diameter as shown in Table 1. Interestingly, the typical diameter of single-wall carbon nanotubes (SWNTs), depending on the chirality indices, can range from 6.2 (n + m = 8) to 12.2 (n + m = 18) for the lowest energy tube for each combination of chirality indices.66 We have therefore designed a MOF with a channel geometry that is essentially comparable to a SWNT but with a significantly higher degree of chemical diversity due to the presence of oxygens and open metal sites decorating the inside of the channel. The proximity and increased volumetric density of open metal sites in the DHFUMA structure compared to the DOBDC structure will later be shown to result in a new CO2 binding configuration. The volumetric densities of open metal sites in Mg2(DHFUMA) and Mg2(DOBDC) are 0.0084 Mg/Å3 and 0.0044 Mg/Å3, respectively. One in every six atoms in DHFUMA is an open metal site, whereas one in every nine atoms in DOBDC is an open metal site. With nearly two times the volumetric metal site density and one and a half times the molar metal site density of DOBDC (in addition to the reduced interatomic distance between adjacent Mg atoms in each channel), DHFUMA contains a spatial configuration of open metal sites that is more favorable for hydorgen storage and CO2 capture. Additional pertinent crystallographic data for Mg2(DOBDC) and Mg2(DHFUMA) are included in the Supporting Information.

Table 1. Accessible Surface Area (ASA), Accessible Volume (AV), Largest Included Sphere (DI), Largest Free Sphere (DF), Open Metal Site Volumetric Density (ρMg), and Open Metal Site Weight Percent of Two Frameworks: Mg2(DHFUMA) vs Mg2(DOBDC).

  ASA AV DI DF ρMg wt % Mg
ligand [m2/g] [cm3/g] [Å] [Å] [Mg/Å3] [%]
DOBDC 1782 0.350 11.8 11.1 0.0044 20.0
DHFUMA 1043 0.095 7.6 6.3 0.0084 25.2

Predictions on Material Stability

To verify whether M2(DHFUMA) is stable and therefore has the potential to be synthesized experimentally, we calculated the vibrational frequencies and elastic constants. Our calculated vibrational frequencies and the full elastic matrix of Mg2(DHFUMA) are shown in the Supporting Information. We find all the vibrational modes of Mg2(DHFUMA) have positive frequencies, demonstrating its dynamical stability. We further verify the elastic stability of Mg2(DHFUMA) against the Born stability criteria,67 and we find the calculated elastic constants of Mg2(DHFUMA) satisfy all the necessary and sufficient stability conditions (see the Supporting Information),68 demonstrating Mg2(DHFUMA) to be mechanically stable. We expect M2(DHFUMA) based on other metals to have the same behavior and suggest these materials have the potential to be synthesized in future experiments. The results of the mechanical and dynamical stability calculations are not surprising, especially since the metal oxide rod M–O coordination environment is identical to M2(DOBDC) and since DHFUMA is an experimentally validated ligand with a fully conjugated backbone exhibiting a planar geometry between the two connection groups (see Figure 1). The synthetic difficulties arise in finding the necessary reaction conditions to yield the correct crystalline M2(DHFUMA) product, the details of which are elaborated in the Supporting Information.

Enhanced H2 Storage Potential

The doubling of the volumetric density of open metal sites results in a factor of 2 increase in the simulated volumetric H2 storage capacity of Mg2(DHFUMA) over Mg2(DOBDC) at cryogenic temperatures. Utilizing the many-body polarization scheme implemented in the RASPA2 package and the polarizable model of Pham et al.40 to compute H2 potential energy interactions in Mg2(DOBDC), we simulate the adsorption isotherms of both Mg2(DOBDC) and Mg2(DHFUMA) at 77 K. We assumed that the force field is transferable and adopt all model parameters of Pham with the exception of the frameworks’ partial atomic charges for which we use the values derived from our REPEAT analysis which are summarized in the Supporting Information. Figure 2(a) demonstrates a good agreement of our isotherm with the theoretical isotherm of Pham et al. and the experimental isotherm of Dietzel et al. (data extracted from ref (40) and ref (69), respectively) for Mg2(DOBDC) at 77 K. Our simulated isotherm as generated by RASPA2 slightly overpredicts the gravimetric uptake (by ∼20% at 1 bar) shown by the experimental results and simulated by Pham et al. which we further discuss in the Supporting Information.

Figure 2.

Figure 2

H2 isotherms computed at T = 77 K. (a) Mg2(DOBDC) isotherms computed in this work, by Pham et al. (extracted from ref (40)), and measured by Dietzel et al. (extracted from ref (69)) and the predicted Mg2(DHFUMA) assuming a transferable force field. Isotherms are in units of amount adsorbed per framework mass. (b) Mg2(DHFUMA) and Mg2(DOBDC) simulated isotherms from this work in units of amount adsorbed per framework volume.

Since the weight compositions of Mg in DHFUMA (25.2 wt %) and DOBDC (20.0 wt %) differ slightly, the amount of H2 loaded per framework weight in DHFUMA is marginally better than DOBDC at low pressure but does not represent a remarkable improvement as shown in Figure 2(a). The strong H2–open metal site interactions dominate the adsorption at low temperatures and pressures, and weak H2–H2 interactions are not sufficient to provide the strong cooperative binding effects observed with CO2 which are later discussed in the section on enhanced CO2 heat of adsorption. In other words, H2 gravimetric adsorption is not significantly improved in DHFUMA at low pressures, and the framework displays H2 saturation behavior at significantly lower pressures than in DOBDC as one would expect from the reduced channel volume. Nevertheless, the advantage of Mg2(DHFUMA) for H2 storage lies exactly in this reduced channel volume and the doubling of volumetric open metal site density. As can be seen from Figure 2(b), the H2 storage capacity on a volumetric basis (in which the amount loaded is expressed per total volume of adsorbent) is approximately twice that of Mg2(DOBDC). Not only would a Mg2(DHFUMA)-based storage device require half the volume to achieve approximately the same H2 storage by weight percent but also the ligand is drastically cheaper. At the cryogenic temperature of 77 K and extremeley low pressure of 0.5 bar, Mg2(DHFUMA) is predicted to achieve a volumetric uptake of 41.5 g H2/L which is sufficient to surpass the DOE’s 2020 H2 volumetric storage target of 40 g H2/L. We note that Mn-BTT (BTT3– = 1,3,5-benzenetristetrazolate), one of the best performing MOFs for volumetric hydrogen uptake, has been reported to achieve uptake of 43 g H2/L but at the higher pressure of 1.2 bar.4

DFT Predicted Binding Geometries and Energies

We list our calculated lattice parameters of the all the MOFs considered in this work in Table 2, and we compare the data on M2(DOBDC) with available experimental results (taken from ref (36); see references therein) from which we find that the errors of our theoretically predicted lattice parameters of M2(DOBDC) are within ∼1%. We also find that for the same metal the a lattice parameter of M2(DHFUMA) is proportionally smaller than that of M2(DOBDC) by 27–29%, and the c lattice parameter of M2(DHFUMA) is almost the same as that of M2(DOBDC), with the biggest difference to be only 0.16 Å (Cu and Zn). Indeed, the decreased unit cell volume of M2(DHFUMA), i.e., by ∼50% in comparison with M2(DOBDC), is mainly due to the shortening of the lattice parameter along the a and b axes, and a direct result of that is the doubling of the density of open metal sites. We will see that the shortening of the a lattice parameter and the doubling of the density of open metal sites in M2(DHFUMA) have a significant effect on the optimal binding configuration of CO2 in M2(DHFUMA).

Table 2. Lattice Parameters (in Å) of M2(DOBDC) and M2(DHFUMA) from Theory and Experiment.

  DHFUMA (theory)
DOBDC (theory)
DOBDC (expt)
a/a
metal a c a c a c (theory)
Mg 18.86 6.88 26.17 6.95 25.89 6.87 72%
Mn 18.70 7.14 26.22 7.01 26.23 7.04 71%
Fe 18.93 6.75 26.11 6.85 26.10 6.85 73%
Co 18.67 6.77 25.91 6.82 25.89 6.81 72%
Ni 18.59 6.65 25.73 6.75 25.72 6.74 72%
Cu 18.85 6.13 25.84 6.29 26.00 6.26 73%
Zn 19.01 6.72 26.18 6.88 25.93 6.84 73%

Taking Mg as an example, we show our theoretical optimized binding configuration of CO2 in Mg2(DOBDC) and Mg2(DHFUMA) in Figures 3a and 3b, respectively. From Figure 3, we can find that a single CO2 molecule has very different binding modes in Mg2(DOBDC) and Mg2(DHFUMA). In Mg2(DOBDC), one terminal oxygen of CO2 binds to Mg of Mg2(DOBDC) with a short binding distance of 2.33 Å, while the other terminal oxygen of CO2 is aligned with the DOBDC linker and points toward the open pore space of Mg2(DOBDC). However, in Mg2(DHFUMA), because of the much shorter interchain Mg···Mg distance (i.e., 6.03 Å in comparison with 8.26 Å in Mg2(DOBDC)), both terminal oxygens of CO2 are able to bind to two neighboring Mg2+ cations simultaneously, with similar binding distances (i.e., 2.59–2.60 Å). Such a unique binding mode results in a much enhanced binding energy of CO2 in Mg2(DHFUMA), i.e., 50.1 kJ/mol, which is 20% (8.8 kJ/mol) stronger than that in Mg2(DOBDC). We show a detailed comparison of the binding energies and relevant O···M binding distances of CO2 in M2(DOBDC) and M2(DHFUMA) with different metals in Table 3, in which we also list available experimental data on CO2 adsorption in M2(DOBDC).70 We further looked at the adsorption of a single H2O molecule in both M2(DOBDC) and M2(DHFUMA) with different metals, and we show a detailed comparison of the binding energies and relevant O···M binding distances in Table 4. Interestingly, the binding energies of a single H2O molecule in M2(DOBDC) and M2(DHFUMA) with the same metal are almost identical. Taking Mg as an example, the binding energies of H2O are 88.6 and 87.4 kJ/mol in Mg2(DOBDC) and Mg2(DHFUMA), respectively. This is because H2O has only one central oxygen, and it interacts with both Mg2(DOBDC) and Mg2(DHFUMA) through a single-contact O···Mg interaction. Comparing the whole series of CO2 and H2O adsorption in M2(DOBDC) and M2(DHFUMA) with different metals, we can find that the trend is the same; CO2 tends to have much stronger binding in M2(DHFUMA) than that in M2(DOBDC) with the same metal, while H2O tends to have almost the same binding strength in M2(DHFUMA) and M2(DOBDC) with the same metal. This would lead to improved selectivity of CO2 in a CO2:H2O mixture in M2(DHFUMA) than that in M2(DOBDC).

Figure 3.

Figure 3

DFT optimized binding configurations of CO2 in (a) Mg2(DOBDC) and (b) Mg2(DHFUMA).

Table 3. Binding Energies (in kJ/mol) and Relevant O···M Binding Distances (in Å) of CO2 in M2(DOBDC) and M2(DHFUMA) from Theory and Experiment.

  DHFUMA (theory)
DOBDC (theory)
DOBDC (expt)
Eb – Eb
metal Eb dO···M Eb dO···M Eb dO···M (theory)
Mg 50.1 2.59/2.60 41.3 2.33 43.5 2.27 8.8
Mn 40.5 2.64/2.75 29.2 2.57 31.7 2.51 11.3
Fe 40.9 2.56/2.76 30.0 2.43 33.2 2.29 10.9
Co 41.1 2.49/2.79 29.3 2.43 33.6 2.23 11.8
Ni 46.1 2.46/2.69 34.8 2.32 38.6 2.29 11.3
Cu 32.0 2.69/2.80 19.9 2.74 22.1 2.86 12.1
Zn 37.6 2.76/2.83 31.3 2.66 26.8 2.43 6.3

Table 4. Binding Energies (in kJ/mol) and Relevant O···M Binding Distances (in Å) of H2O in M2(DOBDC) and M2(DHFUMA) from Theory.

  DHFUMA (theory)
DOBDC (theory)
metal Eb dO ··M Eb dO···M
Mg 87.4 2.19 88.6 2.16
Mn 73.5 2.26 73.3 2.29
Fe 77.5 2.20 77.1 2.21
Co 79.4 2.17 78.9 2.17
Ni 89.2 2.12 89.4 2.11
Cu 68.1 2.22 62.5 2.24
Zn 74.9 2.22 68.4 2.23

Enhanced CO2 Adsorption

We demonstrate in the Supporting Information that the force field of Mercado can reproduce the ab initio potential energy landscape of CO2 in our set of analogues as shown by the agreement of both binding energies and binding geometries. With confirmation of the force field’s tranferability, Henry coefficients of the M2(DOBDC) and M2(DHFUMA) structures were computed at temperatures of 313.0 and 400.0 K, shown in Table 5. An order of magnitude increase is observed in DHFUMA structures over DOBDC structures for a given metal substitution. It is also worthwhile to note that, for a given metal substitution, the M2(DHFUMA) structure achieves the same order of magnitude (and only slightly lower) Henry coefficient at 400 K as its DOBDC counterpart at 313 K in all frameworks except for the Mg analogues. This large decrease in the free energy of a single adsorbed CO2 molecule in DHFUMA is a direct result of the decreased potential energy of the one molecule per two open metal sites binding mode, which has been demonstrated in our DFT optimization and GCMC simulations. GCMC simulations were utilized to simulate the CO2 uptake in M2(DOBDC) and M2(DHFUMA) structures and calculate isotherms for each material. The higher density of open metal sites and enhanced binding energy results in larger uptake at low pressures; however, the reduced channel volume results in quicker saturation of the DHFUMA adsorbent. The CO2 isotherms in Mg2(DOBDC) and Mg2(DHFUMA) in Figure 4 visualize this trend. Thus, at low pressures DHFUMA performs significantly better in total CO2 uptake but performs worse in total uptake at higher pressures. A detailed view of all CO2 isotherms is provided in the Supporting Information. Due to the favorable enhancement of the binding energy, DHFUMA analogues are able to capture significantly more CO2 in any pressure range relevant to industrial CO2 capture from flue gas where PCO2 = 0.15 bar. Figure 5 demonstrates the excess amount of CO2 captured by each metal analogue of DHFUMA in comparison to its DOBDC analogues across a pressure range applicable to flue gas conditions. The excess value peaks at low pressures and then quickly drops to large negative values after the DHFUMA framework saturates with CO2. It is also significant that DHFUMA analogues continue to load approximately 2 mol/kg more CO2 at an elevated temperature of 400 K since high-temperature adsorption can be used to mitigate competitive water adsorption, as will be seen in later discussion.

Table 5. Henry Coefficients (KH) × 10–3 [mol/kg/Pa] of CO2 in the M2(DHFUMA) vs M2(DOBDC) Series at 313 and 400 K.

  DHFUMA
DOBDC
metal 313 K 400 K 313 K 400 K
Mg 10.7 0.22 1.56 0.064
Fe 1.8 0.07 0.20 0.017
Co 3.2 0.11 0.26 0.021
Ni 3.0 0.12 0.27 0.021
Zn 0.39 0.028 0.076 0.009

Figure 4.

Figure 4

Absolute CO2 adsorption in Mg2(DHFUMA) vs the absolute CO2 adsorption in Mg2(DOBDC) at 313 K. The DHFUMA structure significantly outperforms the DOBDC structure in CO2 uptake at low pressures but has far lower capacity of CO2 in the limit of saturation.

Figure 5.

Figure 5

Absolute CO2 adsorption in DHFUMA minus the absolute CO2 adsorption in DOBDC (a) at 313 K and (b) at 400 K. The pressure region in pink corresponds to the typical partial pressure of CO2 (P = 0.15 bar) in the exhaust from a coal-fired power plant. For each metal a temperature exists betweeen 313 and 400 K which maximizes the excess CO2 uptake in the DHFUMA structure.

Enhanced CO2 Heat of Adsorption

The isosteric heat of adsorption, ΔHAds, as a function of loading is a measure of the enthalpy gained on average by adsorbing one additional molecule in the adsorbent system at a specified loading. Conversely, the isosteric heat of desorption, ΔHDes, as a function of loading is the amount of enthalpy required to desorb one additional molecule at a specified loading. In Figure 6 we observe an interesting feature of CO2 adsorption in the DHFUMA structure that shows a monotonic increase in the heat of desorption as a function of loading from zero to saturation loading. A molecule that adsorbs when the framework is close to saturation (0.8–0.9 molec/M2+) releases nearly 10 kJ/mol more enthalpy than the first molecule to adsorb. In other words, the cooperative binding of CO2 is very strong (due to the proximity of the primary binding sites) and increases in strength monotonically with loading. This leads to the nonintuitive property that the enthalpy penalty to desorb CO2always decreases as the loading decreases from saturation to empty framework. Notably, Mg2(DHFUMA) does not exhibit this trend because the binding energy of one CO2 molecule is so strong that cooperative adsorption is only favorable enough to maintain a constant ΔHDes as a function of loading. The same phenomenon does not exist with the DOBDC series. Only a 1–2 kJ/mol increase in ΔHDes is observed in all DOBDC analogues between the limit of 0 loading and the inflection point at 1 molecule per open metal site. Thus, cooperative adsorption at loadings below 1 molecule per open metal site is negligible in the DOBDC frameworks when compared to the DHFUMA frameworks.

Figure 6.

Figure 6

Heat of desorption as a function of loading for the M2(DOBDC) and M2(DHFUMA) analogues. The DHFUMA structures, with the exception of the Mg analogue, exhibit a 7–10 kJ/mol increase in the ΔHDes between the limit of zero loading and saturation.

Optimizing CO2 Capture in Binary CO2:H2O Mixtures

Enhanced CO2 uptake in the range of partial pressures relevant to adsorption from a coal-fired flue stream does not necessarily indicate an improved potential for industrial-scale CO2 capture.71 A multitude of other factors must be considered such as CO2:H2O selectivity, compression work of the CO2-enriched waste stream, and the energy required for adsorbent regeneration, and these attributes can be quantified through a metric known as the parasitic energy.72 However, the deleterious effects of water on CO2 uptake are often overlooked when evaluating materials for CO2 capture potential via the parasitic energy.73 For this reason we investigated water adsorption in the DHFUMA and DOBDC series as well since creative strategies such as high-temperature adsorption and low-temperature desorption (HALD74) have been proposed to mitigate the parasitic energy when adsorbing CO2 from humid flue gas streams. Pure component water isotherms and binding geometries are shown in the Supporting Information.

More relevant to carbon capture, we performed a CO2:H2O binary mixture analysis to investigate each structure’s potential performance for carbon capture in the presence of water. GCMC simulations were performed at a fixed reservoir pressure of 0.15 bar, and the molar composition of CO2:H2O of the reservoir was varied at different temperatures. Note that N2 was not simulated in the mixture as its uptake in the MOF-74 framework series has been shown to be negligible in comparison to the uptake of CO2 and H2O at flue gas adsorption conditions.38,39 The same stepped feature of water adsorption occurs in this binary analysis as in the pure component H2O isotherms, and at a certain critical pressure, water condenses within the pore. In the case of this binary mixture analysis, the condensation of H2O is sufficient to entirely remove any adsorbed CO2 at equilibrium. Figure 7 demonstrates the loss in CO2 uptake capacity that occurs after the molar composition of water (at fixed total pressure) in the reservoir becomes too high.

Figure 7.

Figure 7

Mixture analysis of CO2 and H2O adsorption in the Mg analogues of DHFUMA and DOBDC. Each data point represents an equilibrated absolute adsorption loading from a GCMC simulation at 400 K and fixed total pressure of 0.15 bar, while the molar composition of H2O to CO2 is varied between simulations. For each analogue, two values are extracted, and (1) and (2) demonstrate the values extracted for Mg2(DHFUMA). (1) Corresponds to the CO2 uptake that is equal to 90% of the uptake in the limit of 0 mole fraction of H2O. (2) Corresponds to the H2O mole fraction at which the total CO2 uptake has decreased by 10%.

Yet at higher temeprature, the onset of the water step is shifted to a significantly higher mole fraction. A reduction in CO2 uptake capacity follows from this temperature increase, yet this uptake loss is mitigated in the DHFUMA structure due to the enhanced CO2 affinity. An entire summary of the mixture anlaysis for each structure at various temperatures is presented in the Supporting Information. From one mixture analysis at a specified temperature, we can extract two values of importance which are visualized in Figure 7: the water mole fraction just before water condensation occurs and the amount of CO2 loaded at that specific water mole fraction. These represent competing process design variables. To increase the water mole fraction at which condensation occurs, we must raise the temperature, which consequently reduces the amount of CO2 loaded. These two quantities are plotted for each analogue structure across a range of adsorption temperatures (313–400 K for M = [Co, Fe, Ni, Zn] and 400–473 K for M = [Mg]) in Figure 8. From a carbon capture process design perspective, the ideal material would be located in the top right corner of Figure 8 where the material loads large amounts of CO2 in the presence of extremely high water mole fractions. Since the x and y quantities of Figure 8 represent competing variables (but we desire to maximize both of them), we can interpret this summary as a problem of Pareto optimality, and a Pareto frontier can be observed for Co2(DHFUMA). This means that regardless of the adsorption temperature chosen for our capture process there is no material that can simultaneously achieve a higher water tolerance and CO2 uptake capacity at thermodynamic equilibrium than Co2(DHFUMA). Therefore, regardless of the selected operating temperature, Co2(DHFUMA) will have the best uptake and water tolerance as is easily visualized in Figure 8. In more physical terms, a Pareto optimal material in this context of CO2 capture in the presence of humidity will be the material which delicately balances two factors. First, CO2 uptake must remain the highest with increasing temperature, which fundamentally arises from the highest CO2 Henry coefficient, which in turn arises from the strength of CO2 interactions at the open metal site(s). Second, H2O condensation must occur at the highest water mole fraction, which arises from a combination of the weakest possible H2O interactions with the open metal site and the largest pore size. Hence we can see the competing nature of these two factors since the strengths of CO2 binding and H2O binding at the open metal site are highly correlated, and the advantage of DHFUMA becomes immediately clear since we selectively strengthen the binding energetics of CO2 across all metals due to the one molecule per two open metal site binding mode. Thus, we also notably observe that each M2(DHFUMA) represents a Pareto frontier over its DOBDC counterpart. For example, Ni2(DOBDC) cannot maximize either water tolerance or CO2 uptake above Ni2(DHFUMA) regardless of our specification of the adsorption temperature.

Figure 8.

Figure 8

Mixture analysis of all analogues demonstrating the competing nature of CO2 uptake and water tolerance. The y-axis corresponds to value (1) extracted from Figure 7, and the x-axis corresponds to value (2). The ideal material for CO2 capture would have a data point corresponding to 313 K at the top right corner of the plot.

Conclusions

We have demonstrated the in silico design of a new MOF-74 analogue based on the aliphatic DHFUMA ligand. We predict exceptional small-molecule adsorption properties via a combination of ab initio electronic structure calculations and classical molecular simulation techniques in conjunction with the extensive previous research efforts to create simulation methods that accurately predict guest molecule behavior in MOF-74-type frameworks. Namely we have predicted (1) a doubling of the volumetric storage capacity of H2 in Mg2(DHFUMA) over Mg2(DOBDC) at the cryogenic temperature of 77 K and pressures below 1 bar (and can meet the 2020 DOE target of 40 g/L at ∼0.5 bar); (2) a marked enhancement of CO2 uptake in low-pressure regimes over the DOBDC analogue series; and (3) a selective increase of CO2 binding energy (i.e., stronger CO2 binding with no change in H2O binding energy), the basis for which we propose an industrial-scale CO2 capture process inspired by the HALD scheme (see the Supporting Information). These enhancements are a direct result of the open metal site properties of the M2(DHFUMA) frameworks.

This material contains double the volumetric density of open metal sites over DOBDC analogues, leading to a remarkable simulated volumetric H2 storage capacity. Additionally, the distance between two adjacent open metal sites in each channel is reduced from 8.3 Å in DOBDC to 6.0 Å in DHFUMA. CO2 binds to two open metal sites in the M2(DHFUMA) framework, resulting in a significantly stronger binding energy than in M2(DOBDC). The confined pore channel results in significant cooperative adsorption of CO2, with an isosteric heat of adsorption that is ∼15 kJ/mol stronger at saturation than in the limit of zero loading. Furthermore, since H2O still can only bind to one open metal site in M2(DHFUMA), the ab initio calculated quantity of ΔEbind,H2O – ΔEbind,CO2 in the DHFUMA series is typically ∼10 kJ/mol higher than in the DOBDC series, indicating that the DHFUMA series has more selective CO2 binding energetics relative to H2O. This enhanced selectivity for CO2 is exploited in our classical GCMC simulations, and adsorption at high temperatures is proposed, allowing for a theoretical process by which CO2 can be captured in appreciable amounts (∼1–2 mol/kg) in the presence of nontrace amounts of water (∼0.1–1 mol %). The water tolerance and amount of CO2 captured is dependent on metal choice and adsorption temperature. Finally, an 80% decrease in ligand expense (per mol) suggests that an M2(DHFUMA) analogue may in the future represent an economically improved path forward for large scale H2 storage or CO2 capture from flue gas.

The theoretical work in this paper should motivate efforts to experimentally synthesize M2(DHFUMA) analogues and confirm our simulated volumetric H2 storage capacity and adsorption behavior of CO2:H2O mixtures. We note the synthesis of M2(DOBDC) is usually very challenging.31 Thus far, our efforts to synthesize M2(DHFUMA) are unsuccessful. However, we do not see any obvious reason why M2(DHFUMA) cannot be synthesized experimentally, considering the dynamical and mechanical stabilities of these materials as well as the availabilities and chemical stabilities of the metal and organic precursors. We also believe this framework could be useful for a variety of other separations or storage applications relevant to clean energy. In the future we plan to investigate a range of topics such as selective adsorption of components from light olefin mixtures which are small enough to fit into the DHFUMA channel network if the material can be synthesized.

Acknowledgments

M.W. and B. Smit were supported by the Center for Gas Separations Relevant to Clean Energy Technologies, an Energy Frontier Research Center funded by the U.S. Department of Energy, Office of Science, Basic Energy Sciences under Award # DE-SC0001015 for studies on statistical thermodynamic predictions of adsorption and in silico MOF assembly. B. Smit’s research has received funding from the European Research Council (ERC) under the European Union’s Horizon 2020 research and innovation programme (grant agreement No 666983, MaGic). S.L. and B. Slater were supported by EPSRC (EP/K039296/1 and EP/K038400/1) for studies on electronic structure calculations. M.H. was supported by the U.S. Department of Energy, Office of Basic Energy Sciences, Division of Chemical Sciences, Geosciences and Biosciences under Award DE-FG02-12ER16362 for studies on cheminformatic approaches to linker identification, and the Center for Advanced Mathematics for Energy Research Applications for the development of algorithms of structure assembly. K.S. was supported by the Swiss National Science Foundation (SNSF) with funding under the Ambizione Energy Grant n.PZENP2_166888 for studies on experimental synthesis. This research used resources of the National Energy Research Scientific Computing Center (NERSC), which is supported by the Office of Science of the U.S. Department of Energy under Contract No. DE-AC02-05CH11231. Part of the computational work was performed on ARCHER through our membership of the HPC Materials Chemistry Consortium funded by EPSRC (EP/L000202). S.L. thanks Furio Cora for help on CRYSTAL calculations.

Supporting Information Available

The Supporting Information is available free of charge on the ACS Publications website at DOI: 10.1021/acs.jpcc.6b10363.

  • Crystallographic data for Mg2(DOBDC) and Mg2(DHFUMA) (ZIP)

  • Additional computational details; calculated vibrational frequencies and elastic constants of Mg2(DHFUMA); structure files and charges; additional crystallographic data; force field parametrization details; CO2 force field transferability; CO2 isotherms; H2O isotherms; H2O:CO2 mixture analysis; attempted synthetic procedures (PDF)

Author Contributions

# M.W. and S.L. contributed equally to this work

The authors declare no competing financial interest.

Supplementary Material

jp6b10363_si_002.pdf (17.5MB, pdf)

References

  1. Zhou H. C.; Long J. R.; Yaghi O. M. Introduction to Metal-Organic Frameworks. Chem. Rev. 2012, 112, 673–674. 10.1021/cr300014x. [DOI] [PubMed] [Google Scholar]
  2. Liu J.; Thallapally P. K.; McGrail B. P.; Brown D. R.; Liu J. Progress in Adsorption-Based CO2 Capture by Metal–Organic Frameworks. Chem. Soc. Rev. 2012, 41, 2308–2322. 10.1039/C1CS15221A. [DOI] [PubMed] [Google Scholar]
  3. Mason J. A.; Veenstra M.; Long J. R. Evaluating Metal–Organic Frameworks for Natural Gas Storage. Chem. Sci. 2014, 5, 32–51. 10.1039/C3SC52633J. [DOI] [Google Scholar]
  4. Murray L. J.; Dinca M.; Long J. R. Hydrogen Storage in Metal–Organic Frameworks. Chem. Soc. Rev. 2009, 38, 1294–1314. 10.1039/b802256a. [DOI] [PubMed] [Google Scholar]
  5. Kreno L. E.; Leong K.; Farha O. K.; Allendorf M.; Van Duyne R. P.; Hupp J. T. Metal-Organic Framework Materials as Chemical Sensors. Chem. Rev. 2012, 112, 1105–1125. 10.1021/cr200324t. [DOI] [PubMed] [Google Scholar]
  6. Ranocchiari M.; van Bokhoven J. A. Catalysis by Metal–Organic Frameworks: Fundamentals and Opportunities. Phys. Chem. Chem. Phys. 2011, 13, 6388–6396. 10.1039/c0cp02394a. [DOI] [PubMed] [Google Scholar]
  7. Li J.-R.; Sculley J.; Zhou H.-C. Metal–Organic Frameworks for Separations. Chem. Rev. 2012, 112, 869–932. 10.1021/cr200190s. [DOI] [PubMed] [Google Scholar]
  8. Yaghi O. M.; O’Keeffe M.; Ockwig N. W.; Chae H. K.; Eddaoudi M.; Kim J. Reticular Synthesis and the Design of New Materials. Nature 2003, 423, 705–714. 10.1038/nature01650. [DOI] [PubMed] [Google Scholar]
  9. Xiang S.-C.; Zhang Z.; Zhao C.-G.; Hong K.; Zhao X.; Ding D.-R.; Xie M.-H.; Wu C.-D.; Das M. C.; Gill R.; et al. Rationally Tuned Micropores Within Enantiopure Metal-Organic Frameworks for Highly Selective Separation of Acetylene and Ethylene. Nat. Commun. 2011, 2, 204. 10.1038/ncomms1206. [DOI] [PubMed] [Google Scholar]
  10. Dawson R.; Adams D. J.; Cooper A. I. Chemical Tuning of CO2 Sorption in Robust Nanoporous Organic Polymers. Chem. Sci. 2011, 2, 1173–1177. 10.1039/c1sc00100k. [DOI] [Google Scholar]
  11. Das M. C.; Guo Q.; He Y.; Kim J.; Zhao C. G.; Hong K.; Xiang S.; Zhang Z.; Thomas K. M.; Krishna R.; et al. Interplay of Metalloligand and Organic Ligand to Tune Micropores Within Isostructural Mixed-Metal Organic Frameworks (M’MOFs) for Their Highly Selective Separation of Chiral and Achiral Small Mol. J. Am. Chem. Soc. 2012, 134, 8703–8710. 10.1021/ja302380x. [DOI] [PubMed] [Google Scholar]
  12. Böhme U.; Barth B.; Paula C.; Kuhnt A.; Schwieger W.; Mundstock A.; Caro J.; Hartmann M. Ethene/Ethane and Propene/Propane Separation via the Olefin and Paraffin Selective Metal–Organic Framework Adsorbents CPO-27 and ZIF-8. Langmuir 2013, 29, 8592–8600. 10.1021/la401471g. [DOI] [PubMed] [Google Scholar]
  13. Mason J. A.; Oktawiec J.; Taylor M. K.; Hudson M. R.; Rodriguez J.; Bachman J. E.; Gonzalez M. I.; Cervellino A.; Guagliardi A.; Brown C. M.; et al. Methane Storage in Flexible Metal–Organic Frameworks With Intrinsic Thermal Management. Nature 2015, 527, 357–361. 10.1038/nature15732. [DOI] [PubMed] [Google Scholar]
  14. Cui X.; Chen K.; Xing H.; Yang Q.; Krishna R.; Bao Z.; Wu H.; Zhou W.; Dong X.; Han Y.; et al. Pore Chemistry and Size Control in Hybrid Porous Materials for Acetylene Capture From Ethylene. Science 2016, 353, 141–144. 10.1126/science.aaf2458. [DOI] [PubMed] [Google Scholar]
  15. Caskey S. R.; Wong-Foy A. G.; Matzger A. J. Dramatic Tuning of Carbon Dioxide Uptake via Metal Substitution in a Coordination Polymer With Cylindrical Pores. J. Am. Chem. Soc. 2008, 130, 10870–10871. 10.1021/ja8036096. [DOI] [PubMed] [Google Scholar]
  16. Mason J. A.; Sumida K.; Herm Z. R.; Krishna R.; Long J. R. Evaluating Metal–Organic Frameworks for Post-Combustion Carbon Dioxide Capture via Temperature Swing Adsorption. Energy Environ. Sci. 2011, 4, 3030–3040. 10.1039/c1ee01720a. [DOI] [Google Scholar]
  17. Wong-Foy A. G.; Matzger A. J.; Yaghi O. M. Exceptional H2 Saturation Uptake in Microporous Metal-Organic Frameworks. J. Am. Chem. Soc. 2006, 128, 3494–3495. 10.1021/ja058213h. [DOI] [PubMed] [Google Scholar]
  18. Cook T. R.; Zheng Y. R.; Stang P. J. Metal-Organic Frameworks and Self-Assembled Supramolecular Coordination Complexes: Comparing and Contrasting the Design, Synthesis, and Functionality of Metal-Organic Materials. Chem. Rev. 2013, 113, 734–777. 10.1021/cr3002824. [DOI] [PMC free article] [PubMed] [Google Scholar]
  19. Xue M.; Liu Y.; Schaffino R. M.; Xiang S.; Zhao X.; Zhu G. S.; Qiu S. L.; Chen B. New Prototype Isoreticular Metal–Organic Framework Zn4O(FMA)3 for Gas Storage. Inorg. Chem. 2009, 48, 4649–4651. 10.1021/ic900486r. [DOI] [PubMed] [Google Scholar]
  20. Mueller U.; Luinstra G.; Yaghi O. M.. US Pat.6 617 467. 2004; BASF Aktiengesellschaft.
  21. Rood J. A.; Noll B. C.; Henderson K. W.; Dame N. Synthesis, Structural Characterization, Gas Sorption and Guest–Exchange Studies of the Lightweight, Porous Metal–Organic Framework α-[Mg3(O2CH)6]. Inorg. Chem. 2006, 45, 5521–5528. 10.1021/ic060543v. [DOI] [PubMed] [Google Scholar]
  22. Alvarez E.; Guillou N.; Martineau C.; Bueken B.; Vandevoorde B.; Leguillouzer C.; Fabry P.; Nouar F.; Taulelle F.; Devos D.; et al. The Structure of the Aluminum Fumarate Metal-Organic Framework A520. Angew. Chem., Int. Ed. 2015, 54, 3664–3668. 10.1002/anie.201410459. [DOI] [PubMed] [Google Scholar]
  23. Deng H.; Grunder S.; Cordova K. E.; Valente C.; Furukawa H.; Hmadeh M.; Gandara F.; Whalley A. C.; Liu Z.; Asahina S.; et al. Large-Pore Apertures in a Series of Metal-Organic Frameworks. Science 2012, 336, 1018–1023. 10.1126/science.1220131. [DOI] [PubMed] [Google Scholar]
  24. Witman M.; Ling S.; Anderson S.; Tong L.; Stylianou K.; Slater B.; Smit B.; Haranczyk M. In Silico Design and Screening of Hypothetical MOF-74 Analogs and Their Experimental Synthesis. Chem. Sci. 2016, 7, 6263–6272. 10.1039/C6SC01477A. [DOI] [PMC free article] [PubMed] [Google Scholar]
  25. Wilmer C. E.; Leaf M.; Lee C. Y.; Farha O. K.; Hauser B. G.; Hupp J. T.; Snurr R. Q. Large-Scale Screening of Hypothetical Metal–Organic Frameworks. Nat. Chem. 2011, 4, 83–89. 10.1038/nchem.1192. [DOI] [PubMed] [Google Scholar]
  26. Martin R. L.; Lin L. C.; Jariwala K.; Smit B.; Haranczyk M. Mail-Order Metal-Organic Frameworks (MOFs): Designing Isoreticular MOF-5 Analogues Comprising Commercially Available Organic Molecules. J. Phys. Chem. C 2013, 117, 12159–12167. 10.1021/jp401920y. [DOI] [Google Scholar]
  27. Martin R. L.; Haranczyk M. Construction and Characterization of Structure Models of Crystalline Porous Polymers. Cryst. Growth Des. 2014, 14, 2431–2440. 10.1021/cg500158c. [DOI] [Google Scholar]
  28. Addicoat M. A.; Coupry D. E.; Heine T. AuToGraFS: Automatic Topological Generator for Framework Structures. J. Phys. Chem. A 2014, 118, 9607–9614. 10.1021/jp507643v. [DOI] [PubMed] [Google Scholar]
  29. Boyd P. G.; Woo T. K. A Generalized Method for Constructing Hypothetical Nanoporous Materials of Any Net Topology From Graph Theory. CrystEngComm 2016, 18, 3777–3792. 10.1039/C6CE00407E. [DOI] [Google Scholar]
  30. Rosi N. L.; Kim J.; Eddaoudi M.; Chen B.; Keeffe M. O.; Yaghi O. M. Rod Packings and Metal–Organic Frameworks Constructed From Rod-Shaped Secondary Building Units Rod Packings and Metal–Organic Frameworks Constructed From Rod–Shaped Secondary Building Units. J. Am. Chem. Soc. 2005, 127, 1504–1518. 10.1021/ja045123o. [DOI] [PubMed] [Google Scholar]
  31. Lee K.; Isley W. C.; Dzubak A. L.; Verma P.; Stoneburner S. J.; Lin L.-C.; Howe J. D.; Bloch E. D.; Reed D. A.; Hudson M. R.; et al. Design of a Metal–Organic Framework With Enhanced Back Bonding for Separation of N2 and CH4. J. Am. Chem. Soc. 2014, 136, 698–704. 10.1021/ja4102979. [DOI] [PubMed] [Google Scholar]
  32. Wang L. J.; Deng H.; Furukawa H.; Gándara F.; Cordova K. E.; Peri D.; Yaghi O. M. Synthesis and Characterization of Metal-Organic Framework-74 Containing 2, 4, 6, 8, and 10 Different Metals. Inorg. Chem. 2014, 53, 5881–5883. 10.1021/ic500434a. [DOI] [PubMed] [Google Scholar]
  33. Kapelewski M. T.; Geier S. J.; Hudson M. R.; Stück D.; Mason J. A.; Nelson J. N.; Xiao D. J.; Hulvey Z.; Gilmour E.; FitzGerald S. A.; et al. M2(m-Dobdc) (M = Mg, Mn, Fe, Co, Ni) Metal-Organic Frameworks Exhibiting Increased Charge Density and Enhanced H2 Binding at the Open Metal Sites. J. Am. Chem. Soc. 2014, 136, 12119–12129. 10.1021/ja506230r. [DOI] [PubMed] [Google Scholar]
  34. McDonald T. M.; Mason J. A.; Kong X.; Bloch E. D.; Gygi D.; Dani A.; Crocellà V.; Giordanino F.; Odoh S. O.; Drisdell W. S.; et al. Cooperative Insertion of CO2 in Diamine-Appended Metal-Organic Frameworks. Nature 2015, 519, 303–308. 10.1038/nature14327. [DOI] [PubMed] [Google Scholar]
  35. Runčevski T.; Kapelewski M. T.; Torres-Gavosto R. M.; Tarver J. D.; Brown C. M.; Long J. R. Adsorption of Two Gas Molecules at a Single Metal Site in a Metal–Organic Framework. Chem. Commun. 2016, 52, 8251–8254. 10.1039/C6CC02494G. [DOI] [PubMed] [Google Scholar]
  36. Lee K.; Howe J. D.; Lin L. C.; Smit B.; Neaton J. B. Small-Molecule Adsorption in Open-Site Metal-Organic Frameworks: A Systematic Density Functional Theory Study for Rational Design. Chem. Mater. 2015, 27, 668–678. 10.1021/cm502760q. [DOI] [Google Scholar]
  37. Lin L. C.; Lee K.; Gagliardi L.; Neaton J. B.; Smit B. Force-Field Development From Electronic Structure Calculations With Periodic Boundary Conditions: Applications to Gaseous Adsorption and Transport in Metal-Organic Frameworks. J. Chem. Theory Comput. 2014, 10, 1477–1488. 10.1021/ct500094w. [DOI] [PubMed] [Google Scholar]
  38. Dzubak A. L.; Lin L.-C.; Kim J.; Swisher J. A.; Poloni R.; Maximoff S. N.; Smit B.; Gagliardi L. Ab Initio Carbon Capture in Open-Site Metal–Organic Frameworks. Nat. Chem. 2012, 4, 810–816. 10.1038/nchem.1432. [DOI] [PubMed] [Google Scholar]
  39. Mercado R.; Vlaisavljevich B.; Lin L.-C.; Lee K.; Lee Y.; Mason J. A.; Xiao D. J.; Gonzalez M. I.; Kapelewski M. T.; Neaton J. B.; et al. Force Field Development From Periodic Density Functional Theory Calculations for Gas Separation Applications Using Metal-Organic Frameworks. J. Phys. Chem. C 2016, 120, 12590–12604. 10.1021/acs.jpcc.6b03393. [DOI] [Google Scholar]
  40. Pham T.; Forrest K. A.; Mclaughlin K.; Eckert J.; Space B. Capturing the H2-Metal Interaction in Mg-Mof-74 Using Classical Polarization. J. Phys. Chem. C 2014, 118, 22683–22690. 10.1021/jp508249c. [DOI] [Google Scholar]
  41. VandeVondele J.; Krack M.; Mohamed F.; Parrinello M.; Chassaing T.; Hutter J. Quickstep: Fast and Accurate Density Functional Calculations Using a Mixed Gaussian and Plane Waves Approach. Comput. Phys. Commun. 2005, 167, 103–128. 10.1016/j.cpc.2004.12.014. [DOI] [Google Scholar]
  42. Hutter J.; Iannuzzi M.; Schiffmann F.; VandeVondele J. CP2K: Atomistic Simulations of Condensed Matter Systems. WIREs Comput. Mol. Sci. 2014, 4, 15–25. 10.1002/wcms.1159. [DOI] [Google Scholar]
  43. Perdew J. P.; Burke K.; Ernzerhof M. Generalized Gradient Approximation Made Simple. Phys. Rev. Lett. 1996, 77, 3865–3868. 10.1103/PhysRevLett.77.3865. [DOI] [PubMed] [Google Scholar]
  44. Adamo C.; Barone V. Toward Reliable Density Functional Methods Without Adjustable Parameters: The PBE0Model. J. Chem. Phys. 1999, 110, 6158. 10.1063/1.478522. [DOI] [Google Scholar]
  45. Ernzerhof M.; Scuseria G. E. Assessment of the Perdew-Burke-Ernzerhof Exchange-Correlation Functional. J. Chem. Phys. 1999, 110, 5029–5036. 10.1063/1.478401. [DOI] [PubMed] [Google Scholar]
  46. Poloni R.; Smit B.; Neaton J. B. CO2 Capture by Metal-Organic Frameworks With Van Der Waals Density Functionals. J. Phys. Chem. A 2012, 116, 4957–64. 10.1021/jp302190v. [DOI] [PubMed] [Google Scholar]
  47. Nazarian D.; Ganesh P.; Sholl D. S. Benchmarking Density Functional Theory Predictions of Framework Structures and Properties in a Chemically Diverse Test Set of Metal-Organic Frameworks. J. Mater. Chem. A 2015, 3, 22432–22440. 10.1039/C5TA03864B. [DOI] [Google Scholar]
  48. Grimme S.; Antony J.; Ehrlich S.; Krieg H. A Consistent and Accurate Ab Initio Parametrization of Density Functional Dispersion Correction (DFT-D) for the 94 Elements H-Pu. J. Chem. Phys. 2010, 132, 154104. 10.1063/1.3382344. [DOI] [PubMed] [Google Scholar]
  49. Ling S.; Slater B. Unusually Large Band Gap Changes in Breathing Metal–Organic Framework Materials. J. Phys. Chem. C 2015, 119, 16667–16677. 10.1021/acs.jpcc.5b04050. [DOI] [Google Scholar]
  50. Nanthamathee C.; Ling S.; Slater B.; Attfield M. P. Contradistinct Thermoresponsive Behavior of Isostructural MIL-53 Type Metal-Organic Frameworks by Modifying the Framework Inorganic Anion. Chem. Mater. 2014, 27, 85–95. 10.1021/cm503311x. [DOI] [Google Scholar]
  51. Ling S.; Slater B. Dynamic Acidity in Defective UiO-66. Chem. Sci. 2016, 7, 4706–4712. 10.1039/C5SC04953A. [DOI] [PMC free article] [PubMed] [Google Scholar]
  52. Guidon M.; Hutter J.; Vandevondele J. Auxiliary Density Matrix Methods for Hartree-Fock Exchange Calculations. J. Chem. Theory Comput. 2010, 6, 2348–2364. 10.1021/ct1002225. [DOI] [PubMed] [Google Scholar]
  53. Campañá C.; Mussard B.; Woo T. K. Electrostatic Potential Derived Atomic Charges for Periodic Systems Using a Modified Error Functional. J. Chem. Theory Comput. 2009, 5, 2866–2878. 10.1021/ct9003405. [DOI] [PubMed] [Google Scholar]
  54. Golze D.; Hutter J.; Iannuzzi M. Wetting of Water on Hexagonal Boron Nitride@Rh(111): A QM/MM Model Based on Atomic Charges Derived for Nano-Structured Substrates. Phys. Chem. Chem. Phys. 2015, 17, 14307–14316. 10.1039/C4CP04638B. [DOI] [PubMed] [Google Scholar]
  55. Dovesi R.; Orlando R.; Erba A.; Zicovich-Wilson C. M.; Civalleri B.; Casassa S.; Maschio L.; Ferrabone M.; De La Pierre M.; D’Arco P.; et al. CRYSTAL14: A Program for the Ab Initio Investigation of Crystalline Solids. Int. J. Quantum Chem. 2014, 114, 1287–1317. 10.1002/qua.24658. [DOI] [Google Scholar]
  56. Dovesi R.; Saunders V. R.; Roetti C.; Orlando R.; Zicovich-Wilson C. M.; Pascale F.; Civalleri B.; Doll K.; Harrison N. M.; Bush I. J.. et al. CRYSTAL14 User’s Manual; University of Torino: Torino, 2014; Available at http://www.crystal.unito.it. [Google Scholar]
  57. Stephens P. J.; Devlin F. J.; Chabalowski C. F.; Frisch M. J. Ab Initio Calculation of Vibrational Absorption and Circular Dichroism Spectra Using Density Functional Force Fields. J. Phys. Chem. 1994, 98, 11623–11627. 10.1021/j100096a001. [DOI] [Google Scholar]
  58. Rappe A. K.; Casewit C. J.; Colwell K. S.; Goddard W. A. III; Skiff W. M. UFF, a Full Periodic Table Force Field for Molecular Mechanics and Molecular Dynamics Simulations. J. Am. Chem. Soc. 1992, 114, 10024–10035. 10.1021/ja00051a040. [DOI] [Google Scholar]
  59. Mayo S. L.; Olafson B. D.; Goddard W. A. DREIDING: A Generic Force Field for Molecular Simulations. J. Phys. Chem. 1990, 94, 8897–8909. 10.1021/j100389a010. [DOI] [Google Scholar]
  60. Chen L.; Morrison C. A.; Düren T. Improving Predictions of Gas Adsorption in Metal-Organic Frameworks With Coordinatively Unsaturated Metal Sites: Model Potentials, Ab Initio Parameterization, and GCMC Simulations. J. Phys. Chem. C 2012, 116, 18899–18909. 10.1021/jp3062527. [DOI] [Google Scholar]
  61. Wahiduzzaman M.; Walther C. F. J.; Heine T. Hydrogen Adsorption in Metal-Organic Frameworks: The Role of Nuclear Quantum Effects. J. Chem. Phys. 2014, 141, 064708. 10.1063/1.4892670. [DOI] [PubMed] [Google Scholar]
  62. Pham T.; Forrest K. A.; Banerjee R.; Orcajo G.; Eckert J.; Space B. Understanding the H2 Sorption Trends in the M-Mof-74 Series (M = Mg, Ni, Co, Zn). J. Phys. Chem. C 2015, 119, 1078–1090. 10.1021/jp510253m. [DOI] [Google Scholar]
  63. Dubbeldam D.; Calero S.; Ellis D. E.; Snurr R. Q. RASPA: Molecular Simulation Software for Adsorption and Diffusion in Flexible Nanoporous Materials. Mol. Simul. 2016, 42, 81–101. 10.1080/08927022.2015.1010082. [DOI] [Google Scholar]
  64. Willems T. F.; Rycroft C. H.; Kazi M.; Meza J. C.; Haranczyk M. Algorithms and Tools for High-Throughput Geometry-Based Analysis of Crystalline Porous Materials. Microporous Mesoporous Mater. 2012, 149, 134–141. 10.1016/j.micromeso.2011.08.020. [DOI] [Google Scholar]
  65. Pinheiro M.; Martin R. L.; Rycroft C. H.; Haranczyk M. High Accuracy Geometric Analysis of Crystalline Porous Materials. CrystEngComm 2013, 15, 7531–7538. 10.1039/c3ce41057a. [DOI] [Google Scholar]
  66. Hedman D.; Reza Barzegar H.; Rosén A.; WÅgberg T.; Andreas Larsson J. On the Stability and Abundance of Single Walled Carbon Nanotubes. Sci. Rep. 2015, 5, 16850. 10.1038/srep16850. [DOI] [PMC free article] [PubMed] [Google Scholar]
  67. Born M. On the Stability of Crystal Lattices. I. Math. Proc. Cambridge Philos. Soc. 1940, 36, 160–172. 10.1017/S0305004100017138. [DOI] [Google Scholar]
  68. Mouhat F.; Coudert F.-X. Necessary and Sufficient Elastic Stability Conditions in Various Crystal Systems. Phys. Rev. B: Condens. Matter Mater. Phys. 2014, 90, 224104. 10.1103/PhysRevB.90.224104. [DOI] [Google Scholar]
  69. Dietzel P. D. C.; Georgiev P. A.; Eckert J.; Blom R.; Strässle T.; Unruh T. Interaction of Hydrogen With Accessible Metal Sites in the Metal-Organic Frameworks M2(dhtp) (CPO-27-M; M = Ni, Co, Mg). Chem. Commun. 2010, 46, 4962–4964. 10.1039/c0cc00091d. [DOI] [PubMed] [Google Scholar]
  70. Queen W. L.; Hudson M. R.; Bloch E. D.; Mason J. A.; Gonzalez M. I.; Lee J. S.; Gygi D.; Howe J. D.; Lee K.; Darwish T. A.; et al. Comprehensive Study of Carbon Dioxide Adsorption in the Metal–Organic Frameworks M2(dobdc) (M = Mg, Mn, Fe, Co, Ni, Cu, Zn). Chem. Sci. 2014, 5, 4569–4581. 10.1039/C4SC02064B. [DOI] [Google Scholar]
  71. Smit B.; Reimer J. R.; Oldenburg C. M.; Bourg I. C.. Introduction to Carbon Capture and Sequestration; Imperial College Press, 2014. [Google Scholar]
  72. Lin L.-C.; Berger A. H.; Martin R. L.; Kim J.; Swisher J. A.; Jariwala K.; Rycroft C. H.; Bhown A. S.; Deem M. W.; Haranczyk M.; et al. In Silico Screening of Carbon-Capture Materials. Nat. Mater. 2012, 11, 633–641. 10.1038/nmat3336. [DOI] [PubMed] [Google Scholar]
  73. Huck J. M.; Lin L.-C.; Berger A. H.; Shahrak M. N.; Martin R. L.; Bhown A. S.; Haranczyk M.; Reuter K.; Smit B. Evaluating Different Classes of Porous Materials for Carbon Capture. Energy Environ. Sci. 2014, 7, 4132–4146. 10.1039/C4EE02636E. [DOI] [Google Scholar]
  74. Joos L.; Lejaeghere K.; Huck J. M.; Van Speybroeck V.; Smit B. Carbon Capture Turned Upside Down: High-Temperature Adsorption & Low-Temperature Desorption (HALD). Energy Environ. Sci. 2015, 8, 2480–2491. 10.1039/C5EE01690H. [DOI] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Supplementary Materials

jp6b10363_si_002.pdf (17.5MB, pdf)

Articles from The Journal of Physical Chemistry. C, Nanomaterials and Interfaces are provided here courtesy of American Chemical Society

RESOURCES