CRAFTED - An exploratory database of simulated adsorption isotherms of metal-organic frameworks Felipe Lopes Oliveira12 Conor Cleeton3 Rodrigo Neumann Barros Ferreira1 Binquan

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CRAFTED - An exploratory database of simulated
adsorption isotherms of metal-organic frameworks
Felipe Lopes Oliveira1,2, Conor Cleeton3, Rodrigo Neumann Barros Ferreira1,*, Binquan
Luan4, Amir H. Farmahini3, Lev Sarkisov3, and Mathias Steiner1
1IBM Research, Av. Rep´
ublica do Chile, 330, CEP 20031-170, Rio de Janeiro, RJ, Brazil.
2Department of Organic Chemistry, Instituto de Qu´
ımica, Universidade Federal do Rio de Janeiro, Rio de Janeiro,
RJ, Brazil.
3
Department of Chemical Engineering, Engineering A, the University of Manchester, Manchester, M13 9PL, United
Kingdom
4IBM Research, 1101 Kitchawan Road, Yorktown Heights, 10519, NY, USA.
*Corresponding author: rneumann@br.ibm.com.
ABSTRACT
Grand Canonical Monte Carlo is an important method for performing molecular-level simulations and
assisting the study and development of nanoporous materials for gas capture application. These
simulations are based on the use of force fields and partial charges to model the interaction between
the adsorbent molecules and the solid framework. The choice of the force field parameters and partial
charges can significantly impact the results obtained, however, there are very few databases available to
support a comprehensive impact evaluation. Here, we present a database of simulations of CO
2
and
N
2
adsorption isotherms on 726 metal-organic frameworks taken from the CoRE MOF 2014 database.
We performed simulations with two force fields (UFF and DREIDING), four partial charge schemes (no
charge, Qeq, EQeq, and DDEC), and three temperatures (273, 298, 323 K). The resulting isotherms
compose the
C
harge-dependent,
R
eproducible,
A
ccessible,
F
orcefield-dependent, and
T
emperature-
dependent Exploratory Database (CRAFTED) of adsorption isotherms.
Background & Summary
Carbon capture, storage, and utilization is considered as one of the key strategies required to reduce
anthropogenic carbon dioxide emissions and their impacts on climate change
1
. The most viable option for
this approach is to focus on CO
2
capturing from the point sources, such as fossil fuel power plants, fuel
processing plants and other industrial plants where carbon capture technology can be applied to streams
with the industrial scale flow rates
2
. However, despite several decades of intensive research, carbon capture
in an economically viable way remains an enormous challenge3.
Adsorption processes are considered to be a promising alternative to the conventional absorption
processes due the their low regeneration energy, high selectivity, and high capture capacity
4
. Combined,
these characteristics may lead to energy-efficient processes for industrial scale capture and utilization
of greenhouse gases (GHG). At the heart of a typical adsorption process for gas separation, such as the
Pressure Swing Adsorption process, is the active adsorbent material; and the efficiency of the process
crucially depends on the properties of this material. Within the different adsorbent materials that are
potentially available for this process, crystalline nanoporous materials such as metal-organic frameworks
(MOF)
58
, covalent organic frameworks (COF)
911
, zeolitic imidazolate frameworks (ZIF)
1214
, and
zeolites
15
feature many of the necessary characteristics for a solid sorbent for efficient gas separation
arXiv:2210.09456v1 [cond-mat.mtrl-sci] 17 Oct 2022
under the conditions of interest.
These families of materials contain hundreds of thousands synthesized structures and countless more
hypothetical ones, featuring pores of different size, shape, and chemical characteristics. This creates large
exploration space for studies that seek to identify the best candidates for a given gas capture application.
This endeavour, however, is not possible via a brute-force experimental campaign. The number of large
databases built upon experimental
1620
and hypothetical
21,22
structures, combined with the continuous
growth of diversity and scope of new materials due to the advancements in digital reticular chemistry,
23,24
make high-throughput computational screening (HTCS) approaches an an imperative strategy for efficient
exploration of the vast chemical landscape of crystalline nanoporous adsorbents25,26.
Most of the HTCS studies for carbon capture and related problems are based on using Grand Canonical
Monte Carlo (GCMC) simulations to generate adsorption data. This data is then used to form some simple
material performance metrics or is passed on to the process level modelling to explore performance of
candidate materials under the realistic process conditions.
To perform molecular simulations, such as GCMC, one needs a set of parameters that describe the
interactions among the adsorbate molecules, and between the adsorbate molecules and the atoms of the
adsorbent material; this set of parameters is called a force field.
Over the years of the development, many force fields have been developed for various purposes and
several options are available to describe adsorption of gases such as carbon dioxide in materials such as
MOFs. Invariably, the predicted equilibrium adsorption data and, consequently ranking of the materials
and the recommendations of the screening study will depend on the choice of the force field.
This poses several fundamental questions. How sensitive is the adsorption data to the choice of the
force field parameters? How does this sensitivity vary across different categories or classes of materials?
And ultimately, is a ranking of porous materials for a particular application a robust result or it is contingent
on using a particular force field?
To start to explore these questions one needs a representative mass of adsorption data covering typical
choices of the force field parameters, materials, gases and conditions. This defines the remit of the current
article where we tasked ourselves with building such a database (or at least, the first block of conditions).
To explain the contents of the database and our approach, let us delve first into components of the
classical force fields and the typical options available for the studies of adsorption of gases in MOFs and
related materials. In the classical force fields, the non-bonded interactions are modeled as a sum of van
der Waals and Coulomb potentials
27
. The van der Waals interactions between the adsorbed molecules and
the framework are usually modeled by the Lennard-Jones (LJ) potential, which is an effective potential
with two fitted parameters that can capture most of the intermolecular effects relevant to physisorption.
The parameters for the atoms can be taken from the generic force fields such as the Universal Force Field
(UFF)
28
, DREIDING
29
and TraPPE
30
, with the interactions between different atom species computed
using mixing rules such as Lorentz-Berthelot31 or Jorgensen32.
The Coulombic interactions are modeled by partial atomic charges assigned to the atoms which need
to be calculated for each material. There are several charge assignment methods available, and they
can be divided into two main groups: i. methods derived from quantum chemistry calculations (e.g.
RESP
33
, CHELP
34
, REPEAT
35
, and DDEC
3638
) and ii. methods based on charge equilibration (e.g.
Qeq
39
, PQeq
40
, EQeq
41
, and FC-Qeq
42
). Although there is some consensus that the approaches such as
DDEC (based on electronic structure calculations) are more accurate, methods such as EQeq can present
sufficiently good results that, combined with their low computational cost, makes them attractive choices
for HTCS studies43,44.
Lately, there have been several studies evaluating the accuracy of different methods for calculating
partial atomic charges
4448
, however, little is known about the combined impact of force field and partial
2/18
charge selection on material-level analysis and its implication on process-level performance metrics.
Furthermore, the parameters of force fields such as UFF and DREIDING were fitted employing specific
partial charge schemes (Gasteiger
49
for DREIDING and Qeq
28
for UFF), thus the combination of these
parameters with different charge assignment methodologies, even if more accurate, may not necessarily
generate better results.
These considerations guide us on the choices of the parameters of the force fields to consider in the
database.
The database contains simulated adsorption isotherms for 726 MOFs selected from the CoRE MOF
2014
16
database. The simulations were performed for the adsorption of CO
2
and N
2
with two force
fields (UFF and DREIDING), four partial charge schemes (no charge, Qeq, EQeq, and DDEC), at three
temperatures (273, 298, 323 K). The resulting isotherms compose the
C
harge-dependent,
R
eproducible,
A
ccessible,
F
orcefield-dependent, and
T
emperature-dependent
E
xploratory
D
atabase (
CRAFTED
) of
adsorption isotherms. CRAFTED provides a convenient platform to explore the sensitivity of simulation
outcomes to molecular modeling choices at the material (structure-property relationship) and process
levels (structure-property-performance relationship).
Methods
Structure selection
The 2932 structures present in the CoRE MOF 2014
16
database were analyzed and 726 structures were
retained in our analysis. This subset of 726 comprises all materials from the CoRE MOF 2014 database
for which all atom types are present in both DREIDING and UFF force fields. Throughout this work, this
subset of structures will be referred to as “CRAFTED structures”.
Partial charges calculation
The DDEC partial charges
3638
were taken without modification from the CoRE MOF 2014
16
database.
The EQeq partial charges
41
were calculated using the the extended charge equilibration method as
implemented in the EQeq software
50
v1.1.0. The Qeq partial charges
39
were calculated using the default
implementation available in RASPA51.
Grand Canonical Monte Carlo simulations
Atomistic Grand Canonical Monte Carlo (GCMC) simulations were performed using a force field-based
algorithm as implemented in RASPA
51,52
v2.0.45. Interaction energies between non-bonded atoms were
computed through a combination of Lennard-Jones (LJ) and Coulomb potentials
Ui j(ri j) = 4εi j "σi j
ri j 12
σi j
ri j 6#+1
4πε
qiqj
ri j
(1)
where
i
and
j
are interacting atom indexes and
ri j
is their interatomic distance.
εi j
and
σi j
are the well
depth and diameter, respectively. The LJ parameters between atoms of different types were calculated
using the Lorentz-Berthelot mixing rules
εi j =pεiiεj j,σi j =σii +σj j
2(2)
3/18
LJ parameters for framework atoms were taken from Universal Force Field (UFF)
28
or DREIDING
29
(see Table 1). The parameters for the adsorbed molecules were taken from the TraPPE
30
force field (see
Table 2). All simulations were performed with 10,000 Monte Carlo cycles. Swap (insertion or deletion
with with a probability of 50% for each), translations, rotations, and re-insertions moves were tried with
probabilities 0.5, 0.3, 0.1, and 0.1, respectively. To avoid the use of long initialization cycles, each isotherm
was calculated in a single simulation, with each pressure point of the simulation starting from the result
of the previous one. The uptake values for each pressure were obtained by averaging over the GCMC
equilibrium phase, determined using the Marginal Standard Error Rule. For more information, please refer
to section Automatic transient regime detection and truncation.
All atoms in the MOF were held fixed at their crystallographic positions. The number of unit cells
used was different for each MOF to ensure that the perpendicular lengths of the supercell were greater
than twice the cutoff used. The cutoff for Lennard-Jones and charge-charge short-range interactions was
12.8 Å and the Ewald sum technique was applied to compute the long-range electrostatic interactions with
a relative precision of 10
–6
. The Lennard-Jones potential was shifted to zero at the cutoff. Fugacities
needed to impose equilibrium between the system and the external ideal gas reservoir at each pressure
were calculated using the Peng-Robinson equation of state
53
with the critical parameters for each gas
taken from Table 3. All GCMC uptake data report the absolute adsorption value in mol/kg units.
The enthalpy of adsorption was computed as
H=hU·Ni−hUihNi
hN2i−hNi2RT (3)
where
N
is the number of adsorbates on the simulation box and
U
is the potential energy
54
. All the
adsorption enthalpy values are reported in kJ/mol and are the values as calculated by RASPA without
further modification.
Lennard-Jones parameters
The Lennard-Jones parameters for DREIDING and UFF force fields used in the calculations for the
framework atoms are shown in Table 1. For simplicity, only the atoms that are present in both UFF and
DREIDING are shown. The TraPPE parameters used for the gas molecules are present in Table 2. The
critical parameters used in the Peng-Robinson equation to calculate the fugacity are present in Table 3.
Automatic equilibration detection and truncation
To eliminate the use of long initialization cycles, the Marginal Standard Error Rule (MSER)
55
was applied
to automatically detect the ideal truncation point using the pyMSER package v1.0.12
56
, so that the
averages were taken only over the equilibrated phase of the simulation. The output of this method is the
equilibrated average of the observable, alongside an uncertainty metric. Here we used the uncorrelated
standard deviation, as explained in the next sub-section.
The MSER defines the start of the equilibrated region ˆ
d(n)by solving the minimization problem:
ˆ
d(n) = argmin
0kn2
gn(k)where gn(k) = 1
(nk)2
n1
j=k
(Yj¯
Yn,k)2=S2
n,k
nk(4)
The Left-most Local Mininum (LLM) version of MSER was used in a batched data with batch size of
5.
4/18
摘要:

CRAFTED-Anexploratorydatabaseofsimulatedadsorptionisothermsofmetal-organicframeworksFelipeLopesOliveira1,2,ConorCleeton3,RodrigoNeumannBarrosFerreira1,*,BinquanLuan4,AmirH.Farmahini3,LevSarkisov3,andMathiasSteiner11IBMResearch,Av.Rep´ublicadoChile,330,CEP20031-170,RiodeJaneiro,RJ,Brazil.2Departmento...

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