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8/7/2019 ECH4301-Wk5 Application of Thermodynamics in process engineering
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Slide 1 of 93HMY\ ECH4301\ Semester 2 2009/2010
Application of Thermodynamics
in Solving Process EngineeringProblem
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Slide 2 of 93HMY\ ECH4301\ Semester 2 2009/2010
Sommerfeld on thermodynamics
Thermodynamics is a funny subject. The first
time you go through the subject, you don't
understand it at all. The second time you go
through it, you think you understand it, except for
one or two small points. The third time you go
through it, you know you don't understand it, but
by that time you are so used to the subject that itdoesnt bother you any more.
- Arnold Sommerfeld (1868-1951)
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THERMODYNAMIC PROPERTY
MODELING FOR CHEMICAL PROCESS
AND PRODUCT ENGINEERING : SOME
PERSPECTIVE
John P. OConnell; Rafiqul Gani; Paul M. Mathias; Gerd Maurer; James D. Olson;
Peter A. Crafts; Ind. Eng. Chem. Res. 2009, 48, 4619-4637.DOI: 10.1021/ie801535a
Copyright 2009 American Chemical Society
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Introduction - 1
Chemical tech has broadened & deepened-
uses of thermodynamic properties much more
sophisticated
Process designs developed via computation,
based on accurate data & complex model
To reveal the condition need for desired product
quality
To optimize efficiency for sustainability
To suggest alternative molecular structures for novel
application (health, comfort & defence)
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As March 2009
45 000 000 organic & inorganic substances
61 000 000 chemical sequences in the CAS registry
Principles model for pure component & mixture PYTxequation of state
Excess Gibbs free energy
Introduction - 2
Stateproperties
of formation
Reactionequilibria
Volume Enthalpies
Entropies
Bulkproperties
Component properties
Chemical potential
FugacityEquipment sizing
Energy analysis
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Property model and process model
Process model set of mass and energy
balance equations, as well as imposed physical,
chemical and economic constrains, of process
situation 2 kind of properties i)measurable, ii) conceptual
Quantitative equilibrium or dynamic behaviour
Property model requires spec of desired
behaviour (properties & molecular structure) and
then establish the process steps
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Process and property model
relationships.
Published in: John P. OConnell; Rafiqul Gani; Paul M. Mathias; Gerd Maurer; James D. Olson; Peter A. Crafts; Ind. Eng. Chem. Res. 2009, 48,
4619-4637.DOI: 10.1021/ie801535aCopyright 2009 American Chemical Society
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Roles of property models in Process
and Product Engineering1. Common service role
1. A specified set of property values is provided when
requested
2. Process simulation
2. Service plus advice role1. Models provide information about feasibility
2. Process and product design
3. Integration role
1. Contribute to the technique of problem solution2. Developing efficient and flexible integrated simulation
design strategies
*Forward design approach vs Reverse approach
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Singlephase, fixed
T & P
T and cchange?
Multiplephase ?
Q in/out?Any
reaction?
Model SelectionOnly V (density) needed V(T,c) J for equilibrium phase
Enthalpy H (T, P, c, T)
Simultaneous chemical &
physical equilibriumProperties of formation
* For more complicated situations, model selection may not be straightforward
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Model Information Sources
Molecular simulation
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Estimation Level of empiricism
Fundamental behavior - unknown
or excessively complex.
Continuous variables - by curve-
fitting sparse experimental data
using, for e.g. polynomials,
loglog plots, analysis of variable
statistical methods (ANOVA), and
time-series analysis.Restricted to data interpolation.
Resulting equations with fitted
parameters should not be
extrapolated outside the space of
measured variables.
Computational
chemistry -
calculations from
first principles
where it may be
claimed that no
data are needed.
Include quantummechanics and
applied statistical
mechanics.
Uses rigorous equations or
models from chemical theory.
Collections of quantities include
parameters adjusted to fit data.
E.g. ~ activity coefficients,
compressibility factors, residual
enthalpies, and entropies and
fugacity coefficients.Relations include equations-of-
state, group-contribution
methods, and corresponding-
states formulations
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Model Development
Essential element appropriate specification of the
problem type and expected outcome
E.g. ~ Develop a model for the estimation of the
average density of polymers for the pressures andtemperatures encountered in extruding the product
A clear delineation of model type, application range and
expected users.
Develop a model to predict the activity coefficients ofliquid solutions
Must put constrain or the model must treat all types of system
under all conditions
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Development strategy Iterative steps.
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Schematic phase equilibrium diagram of thebinary system formaldehyde + water. V =vapor; L = liquid; S = solid. (insert) Lower
temperatures where an azeotrope exists atdilute formaldehyde.
Example 1 VLE for Formaldehyde
with Water
The liquidvapor phase region is restricted
to low formaldehyde concentrations since
solids characterized as oligomers of
poly(oxymethylene) glycols, formed from
varying numbers of formaldehyde and watermolecules, precipitate at higher
concentrations.
However, even at the low formaldehyde
concentrations, complicated phase behavior
arises, as shown in the insert of Figure 4.
This is attributed to the formation ofoligomers that remain in solution,
preventing formaldehyde from volatilizing
as well as complexing to form methylene
gycol which can appear in the vapor phase.
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Thermodynamic properties are usually insufficient to
determine speciation, because there are too many
different options, with too many parameters, that may
correlate the data satisfactorily.
Many of the models based on property data would be
unreliable for extrapolation.
The model was established some years ago when
computational chemistry would not have been adequate
to explore the most stable species. However, even now,
it is essential to validate calculations with appropriate
measurements.
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Figure 5 shows a schematic of the vaporand liquid species equilibria with
formaldehyde (FA), water (W), methylene
glycol (MG = HO(CH2O)H), and its
oligomers (MGi= HO(CH2O)iH, i> 1)
The liquid phase, instead of
being a binary, contains at
least four species.
The vapor phase is
considered as a ternary
mixture of the volatile species
FA, W, and MG, since theoligomers should have vapor
pressures that are extremely
low.
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The thermodynamic problem is simultaneous vaporliquid
equilibrium for FA, W, and MG and chemical-reaction
equilibrium for the formation of MG in both phases and the
formation of MGi in the liquid phase.
For the expected low-pressure distillation, the phase
equilibrium relation chosen here assumes ideal gas vapor andnon-ideal liquid solution:
where pis
is the saturation pressure of the three volatilizingspecies I (i = FA, W, and MG), with xi and yi being the molefractions of volatilizing species i in the liquid phase and in thevapor phase, respectively, and i being the activity coefficient of
species iin the liquid phase. The total pressure is indicated by p.
s
i i i ip x pyK !
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The chemical reaction in the vapor phase is the formation of methylene
glycol from formaldehyde and water:
The species concentrations in the ideal vapor phase are related to the equilibrium
constant, a function only of temperature, through
where p(0) = 0.1 MPa is the standard state pressure.For reaction 1, the equilibrium constant in the liquid phase KI can be expressed with K1gas
and the saturation pressures of the pure components and is related to the liquid phasespecies activities:
CH2O + H2O HOCH2OH (1)
(0 )
1 ( ) (2)gas MG
FA W
y pK T
y y p!
1 1 (0)( ) ( ) = (3)
s sgas FA W MG MG
s
MG FA W FA W
p p xK T K T
p p x x
K
K K!
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The formation of poly(oxymethylene) glycols involves other equilibria:
The equilibrium constant for the oligomer of degree n is
The variation with Tofpis(T) was the Antoine form, while that of variousequilibrium constants was the usual parametrized form of
These were selected because the range ofTwas limited and no more
complicated relations, i.e., added parameters, could be justified. The form
for i(T,x)was chosen to be the UNIFAC group contribution approach
because it is predictive and the number of groups in this system is limited.
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The vapor pressures of formaldehyde and water are available in the
literature, but none are found for MG, as it does not exist as a pure
substance.
Thus, pMGs(T) for MG was estimated or treated as an adjustable parameter
when regressing VLE data.
The parameters for the vapor reaction equilibrium constant, K1gas(T), were
determined by the correlation of experimental gas phase density data.
The parameters for the otherKj(T) were found by fitting experimental NMRdata.Some of the UNIFAC parameters for the species were adjusted from
those in the literature by regression of new VLE data.
Model Calculation and Development
The calculations for the simultaneous phase and reaction equilibria were
straightforward, and no new models needed to be developed.
Information Sources
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Figure 6 Equilibrium concentrations of methylene glycol (MG) and poly(oxymethylene)
glycols MG2 and MG3 in aqueous solutions of formaldehyde at 338 and 368 K:
(experiment) Hahnenstein et al.,(41) Balashov et al.;(42) (calculated) Albert et al.(43)
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Figure 6 shows the MG species concentrations in
aqueous formaldehyde mixtures as calculated from the
model in comparison with the experimental NMR data
used to obtain the equilibrium constants.
Since in the liquid phase more than 99% of the
formaldehyde is converted to methylene glycol and
poly(oxymethylene) glycols under the conditions shown
in Figure 6, the mole fraction of (monomeric)formaldehyde is too small to show.
Results
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Figure 7 Vaporliquid partitioning of formaldehyde in the system formaldehydewater at 363 and 413 K:
(experiment) Credali et al.,(45) Kogan,(46) Maurer,(47) Albert et al.,(43) Albert et al.;(44)
(calculated) Albert et al.(44)
Figure 7 shows a typical
comparison betweenexperimental data and
correlation results for the
vaporliquid equilibrium of
the binary system(formaldehyde + water) at
363 and 413 K.
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Formaldehyde also reacts with alcohols. - forms hemiformal and
poly(oxymethylene) hemiformals with methanol.
The above model was extended in a straightforward manner to the binary
formaldehyde + methanol, the ternary formaldehyde + water + methanol, and
to multicomponent systems containing trioxane and some reaction side
products.
The model correctly predicts that at low temperatures the presence of
methanol results (at very low methanol concentrations) in a higher volatility of
formaldehyde, whereas at higher methanol concentrations the volatility of
formaldehyde is lowered.
The thermodynamic model was also extended to describe caloric properties
of these mixtures.
This whole framework has been successfully applied by many companies to
do basic engineering of processes involving aqueous solutions of
formaldehyde. The important feature is that the species are established by,
and their predicted amounts under some conditions are compared with,
molecular measurements such as NMR and/or UV-VIS spectroscopy.
Extensions
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Example 2 - VLE for CO2 and H2S in
Aqueous Amine Solutions over Wide
Ranges of ConditionsSour gases, e.g., CO2 and H2S, are commonly removed from natural or
synthesis gas by chemical absorption in aqueous solutions of amines
(such as, 2,2-methyliminodiethanol = N-methyldiethanolamine =
MDEA) or amine mixtures (e.g., MDEA + piperazine).
While the competitive chemical absorption of CO2 and H2S is kinetically
controlled, departures from equilibrium are the driving forces of such
processes.
The reliable design and optimization of the separation equipmentrequires knowing the chemical reaction thermodynamics and the
vaporliquid equilibria, along with information about the energy to
vaporize/condense the mixtures.
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Gas absorption plants - run at ambient T & P up to 4 Mpa,
whereas solvent regeneration is in a stripper (i.e., gas desorption) at
elevated temperatures (over 390 K) and low pressures.
Composition measurements show that the liquids leaving the
absorption tower contain nearly no neutral amine and very small
amounts of neutral sour gases, though there are large amounts of
electrolyte reaction products such as protonated amines, bicarbonate,
carbonate, and carbamate.
In contrast, the liquids leaving the regeneration unit contain nearly no
electrolytes, the sour gases have been stripped off, and the amines
are mostly neutral.
The latest references addressing this approach and earlier works are
by Maurer and co-workers. A recent similar analysis related to
postcombustion carbon dioxide capture in aqueous ammonia is given
by Mathias et al.
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Figure 8 shows a speciation
scheme for the solubility of
CO2 in aqueous solutions ofMDEA and piperazine (PIP).
The vapor phase - have only
CO2 (C) and water (W),
though solvent volatilizationmight need to be treated in
full process design.
Liquid phase - extremely
complicated (more than adozen species, neutral and
ionic).Figure 8 VLE and chemical reactions in theCO2/MDEA/piperazine/H2O system.
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Broad range of species and compositions requires a model that is able to
describe phase behavior over a very wide range of T and P & high loading of
amine and CO2.
The VLE relation includes vapor-phase non-ideality and the effect of pressure
on the liquid phase. For water, the phase equilibrium relation is
while the extended Henrys law standard state on the molality scale
is used for carbon dioxide because it is supercritical at most conditions
of interest here. Consistent treatment of pressure and non-ideality withEqn 6 must be implemented
Model Relations and Selection
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The fugacity coefficients of saturated water vapor, water in
the vapor mixture, and CO2 in the vapor are
and respectively.
Predicted by the 2nd virial equation of state (since P were
not extremely high and the coefficients are generally more
reliable for aqueous systems than cubic equations of state
based on corresponding states
The Poynting factors for liquid phase pressure effects use
the pure liquid molar volume for water, vW, and the partialmolar volume at infinite dilution for CO2 in water, vCW
,
since these are good estimates and the effects on them
of composition and pressure can be ignored.
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For liquid phase properties - Chemical reactions dominate (see Fig 8).
Chemical equilibrium for reaction Rk is expressed using activities:
where the activity of a solute species i(i.e., all species except water)is the product of its stoichiometric molality and its activity coefficient
appropriate for the Henrys Law standard state, denoted with *:
For water, the activity, aw, is calculated via integration of theGibbsDuhem equation using the activities of all the solutes.
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The temperature-dependence of the chemical
equilibrium constant
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The scheme shown in Figure 8 involves extensive information.Parameters for the equilibrium constants were provided from the literature
cited above.
The Henrys law constant is that for unreacted carbon dioxide in water, which
along with pWs, vW, and the second virial coefficients, which, along with the
estimation method forvCW were taken from in the literature.
The Pitzer model for Gibbs excess energy requires binary and ternary
parameters to describe the interactions between solute species from low gas
loadings (i.e., at low partial pressures of carbon dioxide) to high gas loadings
(i.e., at high partial pressures of carbon dioxide).
The only source for obtaining reliably the most important parameter values is
experimental data of the solubility of CO2 in aqueous solutions of MDEA and of
piperazine at low, as well as at high, CO2 partial pressures.
Such investigations were performed with two different types of experimental
equipment.(50, 51, 60)
Information Sources
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Figure 9 Partial pressure of carbon dioxide (left diagram) and total pressure (right diagram) above
liquid mixtures of (CO2 + MDEA + H2O), mMDEA 2 molkg1: (experiment)(60) 313, 353, 393 K; (experiment)(61) 313, 333, 373, 393, 413 K; (calculation) correlation from all
data, - - - from only high pressure data.(60)
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Figure 10 Carbon dioxide partial pressure (left) and total pressure (right) above liquid mixtures of
(CO2 + MDEA + H2O), mMDEA 8 molkg1: (experiment)(59) 313, 353, 393 K;(experiment)(60, 61) 313.7, 354.4, 395 K; (calculations) correlation from all data, - - - from
only high pressure data.(60)
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The solid lines in Figure 9 and 10 show the excellent comparisons
between experimental(60, 61) and model results(60) for CO2 solubility
in aqueous solutions at low (Figure 9) and high (Figure 10) MDEA
molalities.
In addition, the broken lines in both figures show predictions at lowpartial pressures of carbon dioxide when all interaction parameters
were estimated by using only high-pressure gas solubility data.
These predictions agree well with low pressure experimental data at
low and moderate amine concentrations (high C/MDEA values) but are
less accurate at higher amine concentrations where parameters
characterizing important interactions between molecular MDEA and
other solute species were not included, as they cannot be determined
from high pressure gas solubility data.
Results
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This example illustrates the very great range of data thatmust be assembled in order to reliably develop a full model
for a truly complex system.
Note that every aspect was compared with data and
sensitivity to parameters was tested.
Compared to the first case, fewer molecular
measurements were available, though the speciation was
generally known.
It is possible that computational chemistry methods could
apply here, but this work was done before they were ready
for implementation.
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Example 3 LLE of carboxylic Acid from
Aqueous Solution Many carboxylic acid products are produced by fermentation. Product
recovery from the dilute aqueous solutions is achieved by reaction with
a hydrophobic component, e.g. tri-n-octylamine (TnOA), with theresulting complexes extracted into an organic phase.
Subsequently, the carboxylic acid must be separated and the auxiliary
component regenerated. The design of such extraction and recovery processes requires a
thermodynamic model for liquidliquid equilibria that accounts for
electrolytes in both aqueous and organic liquid solutions.
Our example is for citric acid partitioning between water and different
organic solvents in the presence of TnOA, including the effect of saltson the TnOA partitioning for recovery and regeneration.
The latest references summarizing this approach are by Maurer and
co-workers.
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At low aqueous-phase molalities of citric acid and fixed TnOA - the ratio of
organic to aqueous phase concentrations of citric acid increases with
increasing acid concentration.
It then passes through a maximum and decreases at the highestconcentrations.
This behavior is attributed to two competing effects.
At low acid concentrations in the aqueous phase, the dissociation equilibrium
for citric acid is shifted to its ionic species.
As only neutral acid molecules can be extracted into the organic solvent, the
partition coefficient increases when the amount of dissolved neutral citric acidincreases.
The decrease of the partition coefficient observed at high acid concentrations
results from complete complexation of the TnOA, so additional citric acid
cannot be bound, and the acid remains in the aqueous phase.
In such processes the aqueous phase may also contain strong electrolytes.
While most strong electrolytes reduce the solubility of an organic compoundin an aqueous phase, i.e., salt-out the organic compound, the presence ofsalt actually reduces the partitioning of a carboxylic acid to the organic phase
when a complexing agent, such as TnOA, is present.
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Figure 11 Partition coefficient of citric acid (PCit(m) = mCit(org)/mCit(aq)) in theaqueous/organic two-phase system (citric acid + water + MIBK + TnOA + NaNO3) at
298.15 K for equal volumes of the aqueous and the organic feed solutions at constant
TnOA concentration (mTnOA(org),(0) = 1.24 molal) in the organic feed and several saltconcentrations in the aqueous feed solution:(63) (experiment) mNaNO3(aq),(0) = 0,= 0.01, = 0.05, = 0.1 molal; prediction.
Figure 11 shows
the influence of
NaNO3 on thepartition
coefficient of citric
acid in the organic
phase relative to
aqueous phase
for the system(citric acid + water
+ MIBK + TnOA +
NaNO3)
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For this complex system, the fugacities of the coexisting liquid phases are
treated with the aqueous phase as an electrolyte solution as in eqs 6 and 8,
while the organic phase has only neutral species as in eq 1.
Pitzers excess Gibbs energy model is used in both phases.
It has terms associated with electrostatics and ions in the aqueous phase,
while a power-law equation is used for the organic phase.The organic-phase complexes of citric acid and TnOA are in chemical
reaction equilibrium; most contain water, as verified by IR-spectroscopy.
The stoichiometry of the complexes depends on the organic solvent and can
be complicated.
For example, two complexes (citric acid:TnOA:water = 2:3:2 and 1:1:1,
respectively) were found for toluene, whereas four complexes (1:0:3, 1:2:3,1:1:3, and 2:1:6) were in methyl isobutyl ketone (MIBK).
The equilibrium constants for the various reactions were expressed as in
eqs 4, 5, 7, and 8. Figure 12 shows the resulting speciation for liquidliquid
equilibria with toluene.
Model Relations, Selection, and
Information Sources
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Figure 12. Speciation in liquidliquid
phase equilibria for the system (citric
acid + water + toluene + TnOA).
Figure 12 shows the resulting
speciation for liquidliquid
equilibria with toluene.
The equilibrium constants for
the various reactions were
expressed as in eqs 4, 5, 7,
and 8. Figure 12 shows the
resulting speciation for
liquidliquid equilibria withtoluene.
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Comparisons between predictions and experimental data
are also shown in Figure 11; the agreement is within
experimental uncertainty.
When NaNO3 is added to equal volumes of aqueous andorganic feed solutions (NaNO3(aq),(0) = 0.05 mol kg1;
TnOA(org),(0) = 1.24 mol kg1) giving Cit.tot(aq) = 0.02
mol kg1 in the equilibrated aqueous solution, the
partition coefficient of citric acid to the organic phase is
about 0.4 compared to about 40 in the salt-free system.
When NaCl is the salt under the same conditions, the
value is about 10.
Results
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A number of applications have been made by adding other reactive
components to the scheme of Figure 12.
The partitioning of inorganic acids (HCl, HNO3, and H2SO4) in TnOA-
containing two-phase systems with toluene and MIBK and chloride
partitioning in the system (citric acid + water + MIBK + TnOA + NaCl) have
been studied.The addition of the salt of the carboxylic acid was predicted not to affect
the partitioning of the acid, as there is no competition of different acids for
the amine; this is found to be true for monocarboxylic acids like acetic acid,
though not for acids with more than one carboxylic group.
The model predicts all of the above behavior quantitatively, verifying the
thermodynamic framework.
Again, comprehensive use of, and comparisons with, many different data,
along with careful speciation, allows quantitative description of many
variations of these complex solutions. The results can be used for testing,
for exploring options in process synthesis, and for process optimization.
Extensions
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Example 4 VLE for oleum
Oleum, also known as fuming sulfuric acid, consists of SO3 dissolved in
100% H2SO4.
Thus, for example, 20 mol % oleum consists of 20% SO3 and 80% H2SO4by moles.
The modeling objective is to provide VLE and heat of vaporization
information for the system components in a case where corrosion andtoxicity make extensive measurements extremely challenging.
There are known to be many different species complexes in the liquid
phase of oleum in addition to the H2SO4 and SO3 components.
However, the dominant complex is H2S2O7 which is formed from 1 mol each
of H2SO4 and SO3 by the complexation reaction proposed by Nilges and
Schrage(67) and by Mathias et al.:(68)
No ions are considered to exist in the solution.
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Model Relations, Selection, and
Information Source
The phase equilibrium is obtained with liquid fugacity expressions of the
form of eq 1 and vapor fugacity expressions of the form of eqs 6 and 7.
The activity coefficients were obtained from the NRTL excess Gibbs energy
model since the non-ideality is strong.
For this system where SO3 is the principal volatile component, the effect on
VLE of parameters for the H2SO4H2S2O7 pair is very small and is thereforeignored.
However, parameters for the SO3H2SO4 and SO3H2S2O7 pairs must be
valid over a range of temperature both for VLE and for calorimetric
properties.
Since the pressure is elevated, there is vapor-phase non-ideality that was
described by the RedlichKwong equation with standard parameters basedon critical properties.
This is not expected to be rigorous, but the conditions are such that the
limited composition dependence of the vapor non-ideality minimally affects
the predicted behavior.
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Figure 13 Comparisons of experimental data(71) and model calculations () for vapour
pressures of oleum mixtures.
Published in: John P. OConnell; Rafiqul Gani; Paul M. Mathias; Gerd Maurer; James D. Olson; Peter A. Crafts; Ind. Eng. Chem. Res. 2009, 48,4619-4637.
DOI: 10.1021/ie801535aCopyright 2009 American Chemical Society
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reaction equilibria of the system
Defined by the equilibrium constant for reaction III plus the non-idealities of
the three species in their liquid mixture:
where the temperature dependence ofKoleum(T) is that of eq 5 plus polynomialsin T.
Miles et al.(70) used two methods to measure the enthalpy of vaporization: (1)
evaporation of SO3 from oleum under reduced pressure and (2) heat of solution
(three sets of data) of addition of SO3 to oleum.
The enthalpy of mixing used for matching the calorimetry data is obtained from
the temperature dependence ofKoleum(T) and ofGE via the GibbsHelmholtz
relation
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Results
Figure 14 shows experimental data(70) and model calculations for the
enthalpy of vaporization of SO3 from oleum mixtures of various
concentrations at 30 C.
The enthalpy of vaporization here is the negative of the enthalpy change
that occurs at 30 C when 1 kg of gaseous SO3 is dissolved in a largequantity of an oleum mixture of the given concentration.
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Comparison between experimental data(70) and model calculations for
enthalpy of vaporization of SO3 from oleum mixtures of various
concentrations at 30 C.
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The sigmoidal shape of the enthalpy of vaporization curve is a clear
fingerprint that strong chemical reactions are involved.
At low SO3 concentrations, essentially all the added SO3 combines with
H2SO4 to form H2S2O7.
Hence, the total enthalpy of vaporization is approximately equal to theenthalpy of vaporization of pure SO3 ( 540 kJ kg
1) plus the heat of reaction
( 210 kJ kg1).
At about 50 mol % SO3 (45 wt % SO3), the amount of free H2SO4 has
substantially decreased, so reaction does not occur and the enthalpy of
vaporization rapidly decreases toward the enthalpy of vaporization of pure
SO3.
This is another example where success is obtained with an appropriate
conceptual model and multiproperty fitting of quality data, though no
molecular measurements were involved.
In particular, calorimetric data proved quite valuable in validating a proposed
chemistry model, given by the signature in the enthalpy of vaporization vsconcentration curve.
This case shows how a speciation can be validated by careful use of both
phase equilibrium and calorimetric data, giving a better chance of finding the
most appropriate description.
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Solvent Selection for
Pharmaceutical Production
Introduction
Challenges to develop efficient environmentally friendly process for API
only 1 in 10 new drug candidates survives through clinical trials to enter themarket
not economical to collect large quantities of thermophysical data since thesystems frequently change
predictive thermodynamic models to reduce the experimental search space
Modern drugs are functionally complex(72) and often fall beyond thecapabilities of traditional predictive models like UNIFAC
The reliable prediction of crystal structure and solid-state properties iscomputationally demanding, and still years away from mainstream application
3 examples of service and advise role
Typically, the industry deals with complex chemistry,(74) phase equilibriainvolving organic salts, and aqueous electrolytes. These factors make it clearthat pharmaceutical systems challenge the capability of modern property tools
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Example 1 - Anisole Removal during
Washing and Drying Operations
In this problem, an environmentally friendly solvent is needed to wash and dry
a crystalline pharmaceutical intermediate.
The solvent must efficiently remove anisole residues from upstream
chlorination and coupling reactions, where the product is precipitated as an
organic HCl salt and separated by pressure filtration to yield a 40% w/wanisole wet cake.
Due to anisoles low volatility, removing the residual anisole via inert gas drying
is very slow and not commercially viable.
Washing first with a more volatile solvent can increase the drying rate, and
MTBE was used in early process development.
However, at production scale, MTBE would possibly have required specificVOC abatement equipment, so a search for a better wash solvent was
initiated.
The final wash solvent was to be environmentally preferred, fully miscible with
anisole, and promote vaporization of residual anisole.
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Model Relations, Selection, and
Information SourcesTo solve the above solvent selection problem, the solvent needs are
translated into target properties.
Table 1 lists an appropriate set of pure component and mixture property
values.
The boiling point and melting point indicate the liquid range.
The key property to characterize the ease of anisole removal is the partialpressure, yip. As computed via eq 1, this quantity is increased by selecting awash solvent that gives anisole activity coefficients as large as possible.
Since the anisole will be dilute after washing, the relevant activity coefficient
for screening is its limiting value at infinite dilution, A,S.
Thus, the solvent power, Sp, is used to rank prospective wash solvents for
anisole volatilization
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The miscibility criterion is explicit. In addition to Sp, the Hansen
solubility parameters, h and p,(75, 76) were used to reduce the
solvent search space since the feasible solvent candidates are to
have low affinity for ionic solutes; i.e., small terms for hydrogen
bonding and polarity.
Finally, the functional groups were limited to those with goodenvironmental profiles.
The ProCAMD solvent search software(77) was used to find
solvent candidates matching the target properties listed in Table 1.
The pure component target properties were first estimated from
generated molecular structural information via the
ConstantinouGani or MarerroGani(78) method.
Those structures (molecules) satisfying the target values were then
examined for Sp and miscibility with the UNIFAC-LLE model.
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Results
A set of solvent candidates was identified among the 26837 molecular
structures generated by excluding 13698 substances by the hparameter; 3533 by p; 2925 by Tmelt; 6484 by Tboil; 62 by Sp; and 7 by
miscibility. That left 47 acceptable candidates as possible solvents;
Table 2 shows representative properties of four candidates.
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Of these, heptane was selected as the wash solvent for its Sp value,commercial availability, volatility, and environmental profile (fugitive
releases to the atmosphere).
Figures 15 and 16 show activity coefficients for anisole with the
original MTBE wash solvent and the heptane replacement as
predicted by the UNIFAC method.(79)
The value of ln A,S in heptane is about a factor of 3 greater than that
for MTBE.
In pilot plant trials with heptane, the drying step was considered rapidat about 7 h, and residual anisole levels were significantly reduced.
Perhaps most importantly, the VOC emissions were reduced from
0.15 mol fraction for MTBE to 0.02 mol fraction for heptane.
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Binary solution activity coefficients for MTBE
and anisole predicted by UNIFAC.(79)
Binary solution activity coefficients for
heptane and anisole predicted by
UNIFAC.(79)
This example of solvent substitution demonstrates how group contribution
methods may be applied in reverse and thus narrow the size of a search
space and minimize time-consuming laboratory experiments.
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Example 2 - Solvent Selection for an
Enantiomeric PharmaceuticalThe synthesis of drugs often results in intermediates containing racemic
mixtures of left- and right-handed enantiomers of chiral molecules. For esters,
it is sometimes possible to use a catalytic lipase enzyme in an aqueous
alcohol mixture to selectively dissociate the undesirable enantiomer into its
acid via the reaction:
After dissociation, the chirally resolved ester is easily separated from the acid
and alcohol using pH-buffered liquidliquid extraction. A final crystallization
yields the desired product. Finding the optimal conditions for the dissociation
in a pH-buffered liquid extraction depends on estimating accurate values of
the acid and ester dissociation equilibrium constants or pKa, while selection ofoptimal solvent(s) is needed for both partitioning and for crystallization.
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Model Relations, Selection, and
Information SourcesSeveral properties must be estimated for the process steps: the pKa valuesfor the ester and acid as well as LLE for extraction and SLE for
crystallization of the product with the proposed solvents. A review of pKapredicting methods is presented in ref80. Note that there are two pKas forthe ester and three for the acid. Software from ACD Laboratories(81) was
used to predict the pKas for these organic molecules with the values givenin Table 3. The OH groups on the reaction product alcohol and on the t-butanol are relatively stable and do not need to be considered.
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Using straightforward calculations, the distributions of the species can be
found as functions of pH. These are shown for the ester and acid in Figures
17 and 18. Above pH 10, the ester is present in the uncharged state, while
the acid is fully deprotonated with a charge of negative one. Under theseconditions, the partitioning gives maximum separation efficiency, since
charged species prefer the aqueous phase, while the neutral ester prefers
the organic phase. The pH is adjusted by adding a bicarbonate salt, since
this acts as a sufficiently strong inorganic base for buffering during extraction
but is not strong enough to hydrolyze the ester.
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Species distributions for racemic ester
dissociation as functions of pH.
Species distributions for racemic acid formation
as functions of pH.
After a water wash to remove the bicarbonate and subsequent decanting, thepurified ester product is in a stream rich in t-butanol and saturated withapproximately 30% w/w water. However, direct crystallization of the product
by cooling this solution gave a poor yield; the product solubility in aqueous t-butanol was too high. Thus, a solvent was sought where the product could be
extracted for crystallization.
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Experimental screening of product solubility suggested toluene would be a
good crystallization solvent, but the yield from the actual process solution
turned out to be poor. The reason is clear from the ternary LLE diagram of
Figure 19, predicted with the original UNIFAC LLE parameters.(79) It
shows tie lines and a binodal curve with t-butanol favoring the toluene-richorganic phase rather than the aqueous phase. Alternatives to water, while
keeping toluene, were sought using the search criteria of Table 4, similar
to the process above. In this case, the normal melting point and boiling
point were estimated from group-contribution methods for pure
component properties; for the liquid density, the Rackett equation(22) was
used, while for the selectivity of the product for the organic phase and
miscibility calculations, the UNIFAC-LLE model(79) with the associatedparameters was used.
Result
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Liquid phase compositions for aqueous t-butanol with toluene at T= 25 C, 1 atm from UNIFAC-LLE.(79)
Published in: John P. OConnell; Rafiqul Gani; Paul M. Mathias; Gerd Maurer; James D. Olson; Peter A. Crafts; Ind. Eng. Chem. Res. 2009, 48,4619-4637.
DOI: 10.1021/ie801535aCopyright 2009 American Chemical Society
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The search led to three substances expected to be commercially available,
with the properties shown in Table 5. With the best solvent, 1,3-propylene
glycol, the LLE phase diagram appeared as in Figure 20. The tie linesbetween the toluene-rich and glycol-rich phases show the desired
selectivity fort-butanol, but the two-liquid region extended too little towardthe t-butanol apex. It was concluded that toluene would not provide acommercially viable batch extraction process. Further solubility screening
identified cyclohexane as a potential crystallization solvent, so it was
examined as an extraction solvent, by modifying the polar solvent search
criteria given in Table 4 to include selectivity with cyclohexane and an
updated density limit of 0.8 g/mL.
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Ternary LLE fort-butanol, 1,3-propylene glycol, and toluene at T= 25 C, 1 atm from UNIFAC-LLE.(79)
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Again, the propylene glycols were identified as the top-ranking candidates.
The phase diagram of Figure 21 for 1,3-propylene glycol with cyclohexane
and t-butanol shows fully desirable characteristics. The two-liquid regionextends to a 50:50 volume ratio of cyclohexane to t-butanol, and the t-
butanol partition coefficients are more appropriate for productivity. In fact, justtwo washes with propylene glycol reduces the t-butanol content to about 3%w/w with a residual level of propylene glycol in the organic phase of only
0.5% w/w. This scheme gives good productivity in generic batch
manufacturing equipment, which is common to the pharmaceuticals industry.
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Ternary LLE fort-butanol, 1,3-propylene glycol, and cyclohexane at T= 25 C, 1 atm from UNIFAC-LLE.(79)
Adequate success in this conceptual design project was obtained by flexibly
searching for alternative solvents using phase equilibrium representations of
multicomponent systems as computed from group contribution methods.
Identifying the desired partitioning in the ternary system was particularly crucial.
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Example 3 - Selection of Binary Solvent
Mixtures for a Crystallization Process
This example concerns a pharmaceutical intermediate produced by reaction
in tetrahydrofuran (THF) with the desired product obtained by crystallization.
The yield from THF alone was found to be poor, and water was introduced as
an antisolvent to increase the yield. Laboratory test results showed
inconsistencies, and it was suggested that the actual amount of water in the
crystallization solvent was varying because of carryover from an upstream
washing step. Predictions of the solubility in the aqueous THF solution were
made to determine how water content could affect the product solubility.
Details of this application can be found in ref82. This example highlights the
use of techniques other than group contribution (GC) when the necessary
parameters for a GC-based method are not available.
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Model Relations, Selection, and
Information SourcesThe structure of many heterocyclic pharmaceutical molecules cannot be
treated with GC-based models like UNIFAC, due to missing functional
groups or interaction parameters. The NRTL-SAC model(83) is an
alternative approach which uses characteristic surface segments to describe
intermolecular interactions from surface charge density. The NRTL binary
interaction parameters between the segments are fixed, and there are
adjustable characteristic segment values for each molecular species. The
NRTL-SAC database contains segment profiles for 130 solvents derived
from available literature VLE and LLE data. For a particular solvent, the 4
solute segment parameters are regressed from solubilities in at least 4, and
up to 10, pure solvents spanning the expected surface segment values. This
will allow prediction of solid solubility of a solute, in pure or binary solvents of
the components in the database, with sufficient accuracy for solvent-ranking
and trends in ternary systems. For the present system, an NRTL-SAC model
was established from existing solubility data in 25 pure solvents over the
temperature range of 1080 C.
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Results
The solubility of the pharmaceutical intermediate in mixtures of THF and
water with the regression and prediction results shown in Figure 22, along
with solute solubilities in the mixed THFwater solvent shown in detail inFigure 23. While the calculated values were sometimes far from
experiment, they were adequate for the purposes of the problem. Figure 23
shows that water was acting unexpectedly. At low concentrations, it is a
cosolvent, increasing the solubility. At higher amounts, the water depresses
solubility. The strong variation with the water fraction suggested why the
laboratory tests on the process stream were not consistent: fluctuatingcarryover combined with extreme sensitivity to composition.
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Regression results of NRTL-SAC
model(83) parameters for 25 puresolvents.
Experimental and predicted solubilities of product
in THFwater mixtures.
From these results, a different and more robust crystallization process was
developed. The key was the estimation of solubilities and careful scrutiny of the
sensitivity of properties to variations in conditions.
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5. Emerging Methods for Property
Estimation
The examples given above demonstrate current approaches and capabilities
for property modeling when data sources are available or the opportunity for
new measurements exists. We now give two examples using advanced
techniques to overcome the limitations of current approaches such as group-
contribution methods. They use contemporary computational techniques
either directly or indirectly to predict phase equilibria. The first describes how
unavailable group-contribution parameters can be obtained with a new
method based only on chemical structure, with application to VLE. The
concept is appealing, and it suggests an avenue for future developments. The
other is for a separations process and compares different modeling
techniques, including molecular methods. The results have implications forefforts to improve predictive modeling capabilities.
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Estimation of Group-Contribution
ParametersRecently, Gani et al.(84) have suggested how already availableexperimental data might be used to predict group-contribution model
parameters that are missing in a host tabulation, such as the
MarreroGani(78) group-contribution method for pure component
properties. The basis is an atom-connectivity index, developed under the
principle of additivity of contributions of different descriptors for a specific
property that gives contributions to molecular properties by atoms and theirconnectivities. With atoms, many fewer parameters are needed to
represent groups of atoms. Further, index parameter values for
connectivity indices can be found from the same available experimental
data as for regressing group-contribution parameters. Combining known
group contributions (GC) with estimated group contributions from atom-
connectivity indexes (CI) results in an approach called GCplus. The methodcan be applied to any host group contribution model. Extension to a wide
range of property models for pure component properties and to average
properties of polymer repeat units has been made
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Gonzalez et al.(86) have applied the GCplus approach to predict missing
group-interaction parameters when the host method is the UNIFAC model for
activity coefficients (GC). The available experimental data used for UNIFAC
group contributions were employed in regressing the interaction parametersfor the atom-connectivity indices (CI). Then, the CI values were used to
estimate missing group-interaction parameters.
Examples applying GCplus to pure component properties are given in refs
8486. Here, we illustrate GCplus for mixture properties. In each case, the
chemicals and the phases of interest are given along with the host model and
the group(s) with missing values. Then predicted UNIFAC group parametersare given, along with comparison of predicted and measured phase behavior
results.
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VLE for 1,2-DichloroethaneDMSO
If the original UNIFAC-VLE model(87) is the base method, the missing
group interaction parameters are for the pair CCl and DMSO. Using the CI
method, estimates of the missing group interaction parameters are listed
in Table 6. Figure 24 shows TxyVLE comparisons from using theseparameters along with the GC parameters in the UNIFAC table with
measured VLE.(88) These data were not used for the CI-model parameterestimation, but the agreement is excellent
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TxyVLE diagram at 0.953 bar for 1,2-dichloroethane with DMSO from the UNFAC-CI method with parameters not used for the
CI model regression compared to measured values: (experiment)(88).
Published in: John P. OConnell; Rafiqul Gani; Paul M. Mathias; Gerd Maurer; James D. Olson; Peter A. Crafts; Ind. Eng. Chem. Res. 2009, 48,4619-4637.
DOI: 10.1021/ie801535aCopyright 2009 American Chemical Society
SLE f A i h
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SLE for Acetaminophen
(Paracetamol) with 1-Butanol
If a later revision of the original UNIFAC-VLE model(86) is the host for this
system, only the ACNH2CH2CO interactions are missing. However, for
illustration, we also present results when all the group interactionparameters are obtained via CI. Table 7 lists GCplus group interaction
parameters for the system where those for ACNH2/CH2CO (in bold) are
estimated with CI. Table 8 lists the parameters when all are estimated from
CI. The values are different. Figure 25 shows the comparisons of the results
for both cases with data.(89) Over the limited range of paracetamol
compositions, both sets of parameters describe the data well. Thus, whileparameter values may differ, the data can be adequately predicted with both
methods.
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Figure 25. Solubility of paracetamol in 1-butanol as a function of
temperature estimated with CI-generated values: only for
ACNH2/CH2CO groups (original UNIFAC(87) parameters for other
groups), - - - all parameters estimated from CI; (experiment)(89
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VLE for Methylethylketonen-Heptane
This system involves only the CH2 and CH2CO groups, but there is a
significant temperature variation to be dealt with. The later UNIFAC model(90)
has parameter values, so a comparison can be made among data, GC
prediction, and CI prediction. The CI-computed parameter matrix with
temperature dependence is given in Table 9
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VLE for the methylethylketonen-heptane system at 318.15 K: calculated with UNIFAC(90) group-contribution parameters, - -
- calculated with CI-estimated group-contribution parameters; (experiment)(90) y, x.
Published in: John P. OConnell; Rafiqul Gani; Paul M. Mathias; Gerd Maurer; James D. Olson; Peter A. Crafts; Ind. Eng. Chem. Res. 2009, 48,4619-4637.
DOI: 10.1021/ie801535aCopyright 2009 American Chemical Society
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Figure 26 shows the calculated Pxydiagram with the UNIFAC Dortmund parameters and the CI-computed parameters, along with data from ref91. The agreement for the CI method is not as good
as with the GC method over the whole data range, but the pressure and composition of the azeotrope
are given reasonably accurately.
VLE for the methylethylketonen-heptane system at 318.15 K: calculated with UNIFAC(90) group-contribution parameters, - -
- calculated with CI-estimated group-contribution parameters; (experiment)(90) y, x.
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These examples illustrate the possibilities of using models based on limited
information, such as connectivity indices, as well as a level of compromiseencountered when they are used in place of more elaborate methods such
as UNIFAC. In general, CI may be a reliable expedient to determine
unavailable, and perhaps less sensitive, parameters for use with incomplete
group contribution methods. It is not proposed as a replacement for
experiments, but rather to focus on a few experiments through which the
extension can be verified.
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5.2 Molecular Calculations
While methods such as CI are easily used to obtain group-contribution
parameters, their accuracy and generality may be limited. An alternative
which does not, in principle, require data for model parameter
regression is quantum chemistry calculations for inter- and
intramolecular force fields followed by molecular simulation or statistical
thermodynamic methods to obtain properties
S l t f E t ti Di till ti f
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Solvents for Extractive Distillation of
1,3-Butadiene
Mathias et al.(92) describe an investigation using quantum mechanics and
molecular simulation to improve process simulation for the classical problem
of 1,3-butadiene recovery from steam cracker C4 hydrocarbons by
determining the relative effectiveness ofn,n-dimethylformamide (DMF) and
acetonitrile (ACN) as extractive-distillation solvents. The principal propertiesobtained were the activity coefficients of the hydrocarbon components in the
presence of the extractive solvent for use in eq 1. Comparisons were made
among a quantum mechanical and statistical mechanical method, COSMO-
RS,(-36, 37) a molecular dynamics simulation approach, SPEADMD,(93)
group contributions from UNIFAC,(94) and thermodynamic intuition. Mathias
et al.(92) describe the methods and results in some detail; only a briefsummary is given here to indicate the findings.
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The COSMO-RS method reliably predicted the trends of infinite-dilution
activity coefficients with accuracy comparable to UNIFAC, but only with
systematic empirical corrections. This limited the true predictive capability
of the method. The SPEADMD molecular simulation used a force field fromthe principle of transferability,(95, 96) which assumes that forces inferred
from experimental data for one set of mixtures can be applied to other
compounds and mixtures. The computed results provided unique qualitative
structural and orientational insights at the molecular scale about the
solvation interactions between the polar solvents and the olefinic moieties
in the hydrocarbon compounds. The differences in accessibility for DMF
and ACN and the sizes and shapes that affect intermolecular contacts were
reliably characterized. However, to achieve accuracy for activity
coefficients, the molecular simulations required refinement of the interaction
potentials by regression to data, similar to finding UNIFAC parameters.
E t i f M l l
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Extensions of Molecular
CalculationsThe experience of Mathias et al.(92) suggests some of the limitations
and future prospects of molecular simulation, as do the International
Fluid Property Simulation Challenges (IFPSC).(97) The present
important question about the potential for molecular simulation as a
routine tool to provide quantitative property data for process and
product design is, Are we there yet?. In our opinion, the answer is a
qualified no. While progress is being made, the results are often like
the butadiene example: good, perhaps adequate for the advice role
without high accuracy, but not sufficient for the service role.
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A common shortcoming of molecular simulation methods is the lack of easily
available and suitable force fields(98) to solve the wide variety of problems
under consideration.(99) In particular, what should be done when noexperimental data exist for empirically fitting a force field? As an example,
consider the molecule whose chemical formula is C10H19N and structure is
the following
There are no experimental data and not even a CAS number has been
assigned. If this molecule is of interest in a product design for a particular
application or is an impurity that must be effectively removed in a processdesign, molecular simulation could not be used for property estimation unless
ab inito quantum methods alone could produce a force field. Figure 27
suggests a strategy to obtain force field parameters of molecules of industrial
interest
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Schematic for developing molecular simulation force fields for cases with different amounts of available data.
Published in: John P. OConnell; Rafiqul Gani; Paul M. Mathias; Gerd Maurer; James D. Olson; Peter A. Crafts; Ind. Eng. Chem. Res. 2009, 48,4619-4637.
DOI: 10.1021/ie801535aCopyright 2009 American Chemical Society
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Other limitations in simulations occur at lower temperatures and for larger
molecules (high density) and for transport properties. For quantum
calculations, the system size may be limiting, the fundamental basis setsmight not be accurate enough, and the way to improve results may not be
clear. Also, while only a few molecular-simulation researchers and reviewers
now list computing machinery and computing resources as a major limitation
in the extension of MC and MD to new fluid property applications,
computational capabilities beyond those currently available are needed for
computational chemistry to directly treat many practical systems.Finally, a key issue for practical application molecular simulation is the lack of
availability of tools for nonexpert users. There is no standard toolbox for
molecular simulation as pointed out by Wei.(100, 101) Our experience is that
even experts can have problems, giving one pause about very widespread
application of computation. For example, in at least two entries during IFPSC
contests, expert researchers incorrectly transcribed molecular parametersthat then produced nonrepresentative and erroneous results. In such cases,
what would nonexperts find? We mention two efforts to produce standard
molecular simulation tools which are the TOWHEE project(102) and the
LAMMPS project;(103) others should appear in the future