On the Maximum Obtainable Purity and Resultant Maximum Useful Membrane Selectivity of a Membrane Separator
Sean-Thomas B. Lundin, Ayumi Ikeda, Yasuhisa Hasegawa

TL;DR
This paper explores how purity and selectivity limits in membrane gas separation depend on operating conditions and feed concentration.
Contribution
The paper introduces a new analytical framework to determine maximum useful membrane selectivity based on purity limitations.
Findings
Maximum purity over-predicts at higher recovery rates.
Purity becomes independent of selectivity under certain conditions.
Low-concentration separations benefit more from higher permeance than selectivity.
Abstract
Design considerations concerning the maximum purity of a membrane separator, and the resultant maximum effective selectivity of the membranes were explored by modeling a binary gas membrane separator (pressure-driven permeance) using a dimensionless form. Although the maximum purity has an analytical solution at the limit of zero recovery or stage cut, this solution over-predicts the obtained purity as the recovery is increased. Furthermore, at combinations of high recovery, low feed mole fraction, and low pressure ratio, the maximum purity becomes independent of selectivity above some critical selectivity. As a consequence of this purity limitation, a maximum selectivity is defined at which further increases in selectivity will result in less than a 1% change in the final purity. An equation is obtained that specifies the region in which a limiting purity is less than unity (indicating…
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Taxonomy
TopicsMembrane Separation and Gas Transport · Membrane Separation Technologies · Membrane-based Ion Separation Techniques
1. Introduction
Gas separations represent a growing market segment, with several potential applications including carbon capture [1,2], hydrogen purification [3], and chemical upgrading [4]. Compared to pressure-swing adsorption or cryogenic distillation, membrane separators do not require the energy-intensive processes of pressure or thermal cycling. However, historically, membranes have suffered from low selectivity or low permeance that has prevented them from being economically viable for the large number of potential applications available [5]. Yet, as membrane technologies improve, so do the economics [6]. This has resulted in an increased interest in membrane separations in the research community, with a wide range of target separations and numerous techno-economic assessments being published.
Potential gas separations span a wide range, including the most common applications of hydrogen generation, air purification, and CO_2_ capture. With these applications, a range of potential feed gas compositions is possible, with concentrations as high as 75% for hydrogen production from ammonia [7], to as low as ca. 400 ppm for direct air capture of CO_2_ [8]. Additionally, a large number of potential separations sit within a moderate concentration range, including O_2_ purification from air (20%) [9], and CO_2_ separation from industrial flue gases (typically 5–30%) [10,11]. Thus, any modeling study analyzing the separation of membranes from a general perspective must span a wide range of inlet concentrations. Although most studies focus on a small number of applications and thus limit the feed conditions to within a limited range.
The primary challenges in modeling membrane separators include the presence of concentration polarization and non-ideal gas behavior. Concentration polarization is the phenomenon of reduced concentration near the membrane surface that results in reduced effective permeance due to non-idealities arising from the convective and diffusive transport. Several modeling studies have explored these effects, with the requirement of a 2D or 3D geometry to model the diffusion effects perpendicular to the convective flow [12,13,14]. Concentration polarization is increasingly significant at higher permeances, but some techniques can reduce the effects. Feed spacers or baffles aid in gas mixing within the membrane module [15,16,17,18], showing that some of the non-ideal geometry issues can be solved by optimizing the design of the separator itself. In the case of propylene/propane separation, it has been shown that modified equations of state were necessary to correctly calculate gas properties and accurately model the membrane separator [19]. Nevertheless, a large number of studies have shown that simplified 1D models with ideal gas assumptions can accurately model some gas separations [1,9,10], making them efficient for techno-economic studies and surveys of large variable spaces due to the low computational power required. Two recent reviews by Kancherla et al. [20] and Foo et al. [21] on the topic of membrane separator modeling provide thorough overviews of the aforementioned topics.
Optimization of a membrane separator can involve either direct operational parameters, typically purity and recovery, or cost targets, such as total membrane area and compression costs. Due to limitations with purity and recovery in single-stage separators, techno-economic assessments rely on multi-stage separators with recycle loop configurations to obtain the cheapest potential membrane separations [1,22,23,24,25,26]. Amongst these studies, several techno-economic designs suggest operating at pressure ratios of less than 50 [25,26,27,28,29]. However, low pressure ratios combined with high recovery targets can lead to limitations in the obtainable purity. Previously, Kaldis et al. [30] observed a notable lack of purity or recovery increase with increasing membrane selectivity when a membrane separator was modeled at a pressure ratio of 20. Similarly, a fractionally decreasing cost reduction was reported for increasing selectivity above ca. 30 by Ahmad et al. [23]. However, neither study explored the limited purity in detail. Huang et al. [31] introduced the concept of a pressure-ratio-limited regime, in which operating below a limiting feed concentration results in the purity being limited by the pressure ratio. Yet, while this study offered insight into the maximum purity trends, it did not provide any equations for predicting the pressure-ratio-limited regime without modeling each condition explicitly. In the current work, a membrane separator model is used to explore the parameter space of operation across a much wider range than previously reported, with an emphasis on the purity limitations of membrane separators and the resultant useful membrane selectivity targets.
2. Materials and Methods
2.1. Model Assumptions
A simplified membrane-based gas separator model has been employed with the following assumptions: (1) steady-state operation; (2) isothermal operation; (3) isobaric operation; (4) negligible dispersion (diffusion) effects; and (5) constant permeance and selectivity.
For continuous membrane separation processes, a system can be assumed to be running at a steady state such that no time dependencies remain. Because the permeation process involves negligible energy changes (e.g., adsorption/desorption), an isothermal assumption is valid. The isobaric assumption is valid for larger geometry membranes such as supported silica or zeolite membranes on porous supports with radii greater than ca. 5 mm but is less valid for spiral-wound or densely-packed hollow fiber polymer membrane modules. Conversely, the negligible dispersion assumption is more valid for spiral-wound or hollow fiber modules and less valid for larger supported membrane modules due to the increased radial distance of supported membrane tubes. In both cases, the assumptions imply an idealized system, with decreases in performance expected in real systems. However, techno-economic assessments commonly employ a simple 1D approach with isobaric conditions to obtain approximate notions of the economic feasibility of a membrane process [22,26]. Lastly, the use of constant permeance and selectivity means that adsorption-induced permeance inhibitions or time-dependent degradations in the membrane structure are ignored. The effects of permeance-inhibitions can be ignored because the modeled permeance can be considered an effective permeance rather than the theoretical permeance of a specific material. The use of theoretical permeance would be applicable when optimizing a specific membrane system, but the goal is to obtain a generalized result that is independent of membrane selection so that the general trends of the membrane separator can be understood. Note, however, that this effective permeance does not include concentration polarization effects, which would require a 2D model to accurately interpret.
2.2. Membrane Geometry and Solving Environment
The geometry of the membrane separator is assumed to be a concentric shell-and-tube design with a membrane placed in the inner volume of an outer shell, the feed introduced on the shell side, and the permeate collected on the lumen side. For a single tube separator, this is shown schematically in Figure 1 with the required variables to define the system labeled and tabulated (Table 1). The geometry is defined by the membrane length, L_m_ [m], membrane radius, r_m_ [m], and shell radius, r_s_ [m]. The membrane properties include the permeance of species i, φ_i_ [mol m^−2^ s^−1^ Pa^−1^], and the ideal selectivity of species i vs. j, S_ij_. Lastly, the operational conditions include the feed temperature, T [K], the feed composition of each species i, x_r_,i,0, the total volumetric feed flow rate, f [m^3^ s^−1^], the retentate pressure, P_r_ [Pa], the sweep composition of each species i, x_p_,i,0, the total volumetric sweep flow rate, s [m^3^ s^−1^], and the permeate total pressure, P_p_ [Pa]. Although this system is for a single tube, the final model derivation allows for the comparison of differing geometries via normalization of the active permeable membrane area and total volume on the retentate side. As will be shown in the derivation, the dimensional analysis results in a grouping of terms for the geometry such that only the membrane area A_m_ [m^2^] remains. Furthermore, although the model shows a co-current flow, the presence of the sweep is for model convergence only and the final results can be assumed to occur for systems with zero sweep flow.
This model has been developed in the finite element analysis software COMSOL Multiphysics^®^ 6.1 (Burlington, MA, USA). The retentate and permeate transport equations were solved simultaneously using a parallel sparse direct solver (PARDISO) algorithm. A mesh consisting of 100 domain elements was used for the iterative solver and the solution was determined based on residual or error criteria below 10^−6^.
2.3. Model Equations
2.3.1. Dimensional Mass Balances and Variable Transformations
The governing steady-state transport equations with the aforementioned assumptions for the retentate and permeate streams of a 1D membrane separator model are as follows:
where u_z_ [m s^−1^] is the velocity in the axial direction, c_i_ [mol m^−3^] is the bulk concentration of species i, J_i_ [mol m^−2^ s^−1^] is the flux of species i through the membrane, P_m_ [m] is the circumference of the membrane, A_r_ [m^2^] is the cross-sectional area of the retentate, A_p_ [m^2^] is the cross-sectional area of the permeate, and the subscripts r and p denote the retentate and permeate sides, respectively. A negative flux is assigned to the retentate, and a positive flux is assigned to the permeate to balance the species leaving and entering each system, respectively. Within the COMSOL solving environment, the 1D model requires definitions for a physical system including all of the parameters listed except for r_s_.
The concentrations are related to mole fractions using the ideal gas relationship, as follows:
where R [J mol^−1^ K^−1^] is the universal gas constant and T [K] is the temperature. To simplify the model and reduce variable dependence, dimensionless variables were introduced. The axial length was reduced using the following:
where L_m_ [m] is the length of the membrane. The flow velocity was reduced with the following:
where u_r_,z,0 [m s^−1^] is the inlet velocity of the feed, and u_p,z,_0 [m s^−1^] is the inlet velocity of the sweep. The feed and sweep velocities are converted to volumetric feed flow rates using the following:
where f [m^3^ s^−1^] is the feed flow rate and s [m^3^ s^−1^] is the sweep flow rate. The volumetric flow rates are converted to standard flow rates f,STP, and s,STP assuming ideal gas relationships, as follows:
where P0 is the standard pressure [100 kPa] and T0 is the standard temperature [273.15 K]. Lastly, permeance through the membrane, φ_i_ [mol m^−2^ s^−1^ Pa^−1^], is modeled as a pressure-driven flux gradient with the following:
where x_r_,i is the local retentate mole fraction of species i, and x_p_,i is the local permeate mole fraction of species i. Relative permeances of differing species are related by the ideal selectivity of species i vs. j, S_ij_, using the following:
Combining the previous equations, substituting into the mass balances, and rearranging terms results in the following:
where A_m_ [m^2^] is the membrane permeable area. Note that in this form the geometric terms for the tubular geometry have disappeared and only A_m_ remains. From this, it is clear that any geometry (e.g., planar or tubular) can be used, as well as any multilayer or multitube system. As long as the separator acts as a single stage (i.e., a single feed, single retentate, and single permeate stream), only the effective total membrane surface area is required to model the system.
2.3.2. Dimensionless Transport Parameter and Reduced Pressure
From the dimensionless forms of the mass balances, two dimensionless parameters are observed. The first will be called a transport variable, θ_i_, as follows:
which balances the feed flow rate on the numerator with the membrane permeance, membrane area, and retentate pressure on the denominator. The transport parameter is defined for each species i, but note that each θ_i_ is related to other species using S_ij_ because the only difference in the definition is φ_i_. Variants of this parameter have been used in other dimensionless approaches to membrane reactors [32], sometimes being referred to as a modified Pe number by [33]. The second relationship is the reduced pressure, ψ, as follows:
where P_r_ is placed in the numerator such that, intuitively, as ψ increases, so does the permeation driving force in the membrane system. This definition, or its inverse, is used often in modeling studies to relate the retentate and permeate pressures of a membrane system.
2.3.3. Dimensionless Mass Balances
Upon replacement of terms in the mass balances with the dimensionless groups defined here, the final mass balances can be written as follows:
where the sweep side includes the ratio of feed to sweep flow rates at the inlet. Based on this definition, a zero sweep condition results in an unstable system so s was set to be 0.001% of f. For all conditions modeled, the sweep flow remained negligibly low at less than 0.1% of the permeated flow when the recovery was greater than 1%. The use of negligible permeate sweep flow means that the steady-state permeate concentrations will be constant along the length of the module. This causes the results to be identical whether the system is modeled as a co-current or counter-current configuration. Results discussed herein apply to systems with zero sweep flow such that the maximum potential permeate purity can be achieved. Due to the introduction of the reduced flow velocity parameter, the flow rate boundary conditions at the inlets are as follows:
The inlet concentrations of both retentate and permeate sides must be specified for n − 1 species, where n is the total number of species, as follows:
Because a negligible sweep flow is introduced the inlet permeate compositions do not affect the results, so the values were set arbitrarily to an equimolar concentration to prevent poor convergence of the model. In total, the model requires 2 dimensionless inputs (θ_i_, ψ), n − 1 selectivities (S_ij_), and n − 1 inlet feed compositions (x_r_,i,0) to be defined, resulting in a total requirement of 2n input parameters to specify a 1D membrane separator (Table 2). To keep the number of variables reasonable, a binary gas mixture is assumed on the basis that tertiary-order gases can be classified as either low permeance (i.e., high S_ij_) or low feed concentration compared to the primary two gases. Thus, a system consisting only of gases i and j, and requiring 4 input criteria was used for further analysis.
2.3.4. Performance Criteria
The goal of this study is to elucidate the maximum separation capability of a membrane separator in terms of total flow productivity, recovery, and purity. Recovery of species i is defined as follows:
where ṅ_r_,i,0 is the inlet molar flow rate of species i and ṅ_r_,i,1 is the outlet molar species of i in the retentate. Purity is defined as follows:
where ṅ_p_,i is the outlet molar flow rate of species i, and ṅ_p_ is the total outlet molar flow rate. A maximum volumetric productivity can be acquired, for example, by setting targets for R_i_ or x_p_,i and obtaining the highest value of θ_i_ possible.
3. Results
3.1. Modified Pressure Ratio
In the derivations, the total pressure ratio (P_r_/P_p_) was used to define ψ, which is reasonable given its appearance in the mass balances. However, a simple ratio of pressures fails to account for the change in partial pressures of the system, particularly when the species of interest is at a low concentration in the inlet. Instead, a reduced pressure ratio, ψ_i_, based on the permeance equation to balance the partial pressure gradient across the membrane is required, as follows:
This ratio is a measure of the effective driving force for permeation at the separator inlet, as it uses the feed and sweep inlet concentrations (x_r_,i,0 and x_p_,i,0). At a value of unity the driving force for permeation of species i is zero so no separation occurs, and as ψ_i_ increases the driving force increases resulting in higher recovery. Because the sweep gas in this system is negligibly small to avoid issues with further purification, the value of x_p_,i,0 is not a known input. However, for conditions at which φ_i_ΔP_i_,0 ≫ φ_j_ΔP_j_,0 the value of x_s_,i,0 converges on unity, which will be increasingly valid as S_ij_ increases. Thus, a value of x_p_,i,0 = 1 is used for all conditions. Importantly, this decision does not affect the accuracy of the results as it only changes the input parameter calculations, not the model equations themselves. Previously, Huang et al. [31] discussed a similar modified pressure ratio.
The ability of the modified ψ_i_ term to normalize pressure driving force is illustrated in Figure 2 using a θ_i_,offset value defined as follows:
In this equation, the value of θ_i_,offset is determined as a fractional difference between the θ_i_ obtained for 98% recovery at a ψ_i_ of 10^2^ and 10^4^. Equivalently, a θ_i_,offset is also calculated using the unmodified ψ of 10^2^ and 10^4^ for comparison. The θ_i_,offset was calculated at x_r_,i,0 of 0.10 and 0.70, and S_ij_ of 10 and 500, and shown for both ψ and ψ_i_ in Figure 2. At higher x_r_,i,0 the θ_i_,offset is low and similar for both ψ and ψ_i_, which is reasonable as the value of ψ and ψ_i_ converge at a feed mole fraction of one. However, at x_r_,i,0 = 0.10 the θ_i_,offset is significantly more negative when calculated using ψ, meaning that increasing the pressure ratio from 10^2^ to 10^4^ would result in a significant increase in the obtained θ_i_ (i.e., higher productivity with higher pressure gradient). The use of ψ_i_ compresses the change in θ_i_ with respect to x_r_,i,0 and S_ij_, and Figure S1 indicates that negligible change in R_i_ is expected above ψ_i_ of 10^3^ for any condition tested (x_r_,i,0 > 0.10 and S_ij_ < 500).
3.2. Absolute Maximum Permeate Purity
The absolute maximum purity of the membrane separator is obtained as an analytical solution for the limiting case in which the recovery (stage cut) goes to zero [19], given as follows:
which requires x_r_,i,0, S_ij_, and ψ to be defined. The maximum purity, x_p_,i,max, is shown for S_ij_ vs. x_r_,i,0 at a ψ_i_ of 10^2^ in Figure 3a. Both S_ij_ and x_r_,i,0 strongly influence x_p_,i,max, with the x_p_,i,max converging on x_r_,i,0 as S_ij_ decreases to unity. S_ij_ = 1 implies the membrane is unselective and all species transport equally, so the purity is equal to the input concentration. Generally, x_p_,i,max increases as either x_r_,i,0 or S_ij_ increases. Next, x_p,i,max_ is shown for S_ij_ vs. ψ_i_ at x_r_,i,0 of 0.10 in Figure 3b, wherein the majority of change with ψ_i_ occurs for ψ_i_ < 10. Above ψ_i_ = 10, the maximum purity becomes asymptotic with little change in the range of S_ij_ explored. However, note that the change in x_p_,i,max, with respect to ψ_i_, increases as S_ij_ increases, indicating a substantially high S_ij_ would require an increased ψ_i_ to stabilize (i.e., ψ_i_ > 10^2^ at S_ij_ > 10^4^).
3.3. The Effect of Recovery on the Maximum Purity
The issue with the analytical solution, with regard to maximum purity, is that it only applies at R_i_ = 0. To understand the effects of increasing recovery on the maximum attainable purity, first consider the effects of θ_i_ and ψ_i_ on R_i_ (Figure 4a) and x_p_,i (Figure 4b). Although increasing ψ_i_ results in an asymptotic R_i_ and x_p_,i, the contour lines arise from opposite ends of the θ_i_ scale, which means the maximum x_p_,i at a specified R_i_ occurs at the highest ψ_i_ possible. As before, the majority of change occurs for ψ_i_ < 10^2^, so a value of ψ_i_ = 10^2^ will be chosen as a reasonable maximum operating condition. Note that, as previously mentioned and shown in ESI Figure S1, the selection of ψ_i_ = 10^2^ is reasonable across a wide range of x_r_,i,0, and S_ij_. Furthermore, it is important to realize that real systems will not likely operate at ψ_i_ > 10^2^, but the choice of pressure ratio is driven by the desire to obtain an estimate of the maximum potential purity. Any decrease in pressure ratio driven by economic arguments will result in a lower obtained purity, which is the reason this result may be considered the maximum obtainable purity of a single-stage separator.
Using ψ_i_ = 10^2^ as the pressure ratio, the effects of S_ij_ and R_i_ on the maximum purity are shown for x_r_,i,0 of 0.10 (Figure 5a) and 0.90 (Figure 5c). Here, the maximum purity was obtained using simulated data by optimizing θ_i_ until the target R_i_ was achieved for each combination of S_ij_, x_r_,i,0, and ψ_i_. As R_i_ increases, x_p_,i slightly decrease for a specified S_ij_. Furthermore, the contour lines show that while the absolute x_p_,i changes with x_r_,i,0, the overall trends of constant x_p_,i remain similar. To illustrate this effect in detail, the S_ij_ at a specified R_i_ was compared to the analytical solution S_ij_ as R_i_ goes to zero (S_ij_,min), and shown as surface plots in Figure 5b,d. This information can be useful in predicting the minimum selectivity of a separation given a target R_i_ and x_p_,i using the relationship
3.4. Estimating the Minimum Selectivity for a Desired Purity and Recovery
Although the analytical result of Equation (30) can be solved to obtain a selectivity target for a desired purity, the change with recovery is not considered. Using the relationship in Equation (31) and data from Figure 5, an improved estimate for the minimum selectivity can be obtained via the following:
- Using the analytical solution (Equation (30)), solve for the S_ij_ required to obtain the target x_p_,i at the specified x_r_,i,0, and use a ψ_i_ > 10^2^. Consider this S_ij_ as S_ij_,min;
- Use the relationship shown in Figure 5b to identify the multiplication factor for the target R_i_ (e.g., 2.7 at R_i_ = 90%, S_ij_ of 10^2^);
- Multiply the S_ij_/S_ij_,min factor by S_ij_,min to obtain the minimum selectivity required to achieve the target x_p,i_ at the target R_i_.
Using these steps, the application is explained using separation of CO_2_ for carbon capture projects; however, note that the method can be applied to higher selectivity operations or differing feed concentrations depending on the target application. CO_2_ separation membranes have a typical S_ij_ range of less than 100, with a maximum no higher than ca. 800 [34,35,36]. Sources of CO_2_ include flue gas from burners, with low CO_2_ concentrations of about 10% being common [11,37]. Thus, a 10% CO_2_ feed is considered, and the discussion will focus on identifying S_ij_ targets of 50 to 100 as reasonable. Table 3 shows the results for the example separation of 10% CO_2_ for carbon capture applications. The result of solving Equation (30) is provided as R_i_ = 0% and then targets of 90% and 95% recovery are set to show the difference. In this sample, the target purity of 90% is seemingly achievable for CO_2_ membranes using Equation (30), with a required S_ij_ of 89. However, raising the R_i_ to 95% shows that the true minimum S_ij_ is 300 for the high recovery targets of carbon capture, which is in the upper range of all reported CO_2_ membranes [34,35,38]. Instead, a more accurate maximum final purity will be closer to 70%, which shows that a recovery of 95% may be achieved with a selectivity of 72. Note that this minimum S_ij_ is still an underestimation due to the expected overprediction of both high ψ_i_ and the 1D model in general, but the outcome is simple to calculate and can provide a significantly more accurate target S_ij_ than the analytical solution at R_i_ = 0% alone.
3.5. Limiting Pressure Ratios and Asymptotic Purity Zones
Although the previous section provides insight into the minimum selectivity at high recovery, the primary limitation is that it applies only to high pressure ratios that are almost certainly not economically viable [26,29]. To explore the effects at lower pressure ratios, x_p_,i is plotted against S_ij_ vs. R_i_ for pressure ratios of ψ_i_ = 2, 5, 10, and 25 in Figure 6. At ψ_i_ = 2 (Figure 6a), x_p_,i increases slowly with R_i_ until an asymptotic rise is observed. The asymptotic R_i_ value increases with increasing S_ij_, but poses a severe limitation on the maximum achievable purity at high recovery for all S_ij_ of interest. Increasing ψ_i_ to 5 (Figure 6b), the asymptotic rise is delayed to higher R_i_, but is still a concern at R_i_ > 0.8 for the S_ij_ up to 10^4^. Further increasing ψ_i_ to 10 (Figure 6c) increases the limiting Ri to about 0.90, but it requires an increase in ψ_i_ to 25 (Figure 6d) to remove the limiting regime up to the maximum plotted condition of R_i_ = 0.95. Note that the asymptote arises due to the physical limitations imposed by permeation at near-complete recovery. As R_i_ goes to unity, θ_i_ must go to zero to allow for 100% of the inlet target species to permeate due to the increase in residence time required for permeation. This means that the asymptote will arise for all ψ_i_, but at sufficiently high ψ_i_, this situation does not occur until the R_i_ is above a reasonable target and can be ignored.
The important lesson from Figure 6 is that at high R_i_ and low ψ_i_, the asymptotic trends result in a maximum effective S_ij_. Increasing S_ij_ beyond the maximum results in no increase in purity and is unlikely to be economically viable considering higher S_ij_ is associated with lower membrane permeance (productivity) and higher development and fabrication costs. Thus, identifying the regime in which the asymptotic maximum S_ij_ arises is important in understanding the target regions of operation.
3.6. Obtention of the Limiting Selectivity
Although the information presented in Figure 6 could be construed as a maximum R_i_ for a given set of conditions, it is more practical to consider a minimum S_ij_ to avoid asymptotic regions. To approach this, first consider the residual impurity
The use of impurity is for convenience; a plot of the impurity as the value goes to zero is observed easily on a log scale compared to purity with its convergence on unity. Figure 7a shows sample data of the impurity level vs. S_ij_ at x_r_,i,0 of 0.10, ψ_i_ of 9, and R_i_ that straddle the asymptotic region. Note that ψ_i_ of 9 is an arbitrary choice, but it clearly illustrates the asymptotic effect that can occur near a target recovery of 90%; any value of ψ_i_ sufficiently low as to have an asymptotic purity regime could have been used, with appropriate change in R_i_ to illustrate the asymptotic phenomena. At R_i_ of 0.89, the impurity level decreases continuously as S_ij_ increases toward 10^6^, whereas the impurity level plateaus for R_i_ of 0.90 and 0.91. The plateau for R_i_ of 0.90 occurs at S_ij_ of ca. 10^4^, whereat further increases in S_ij_ do not decrease the impurity level below ca. 0.01 (x_p_,i = ca. 0.99). The effect is worse at R_i_ of 0.91, with a minimum impurity level of ca. 0.1 (x_p_,i = ca. 0.9) at S_ij_ of ca. 10^3^.
To obtain an approximate S_ij_ at which the impurity level no longer declines, an error is defined as follows:
where the difference between the impurity level at some specified S_ij_ and at S_ij_ = 10^8^ is divided by the level at S_ij_ = 10^8^. A maximum selectivity of 10^8^ was defined because it is sufficiently close to infinity when considering that thin film membrane technologies do not achieve selectivity greater than 10^5^ even for the best-reported composite Pd membranes [39] (except for those in which the true impurity was below the detection limit of the equipment and the authors mistakenly claim infinity). The results of this calculation with respect to the conditions of Figure 7a are shown in Figure 7b. For the R_i_ = 0.89 condition, the error decreases continuously but never drops below 10^−2^ at S_ij_ less than 10^6^. Contrastingly, the two R_i_ with asymptotic impurity levels both experience a rapid decline to below 10^−2^ before declining further. Given this information, a change of 10^−2^ is chosen arbitrarily as a sufficient predictor of the asymptotic S_ij_ value, as it suggests that any further increase in S_ij_ will result in less than a 1% further increase in purity. Using the technique developed above, the maximum selectivity with continued decreases in impurity level was obtained across the parameter space by performing two steps. First, x_p,i_ data were obtained for a range of S_ij_ at a specified x_r_,i,0, ψ_i,_ and R_i_ (R_i_ is obtained by optimizing θ_i_). Second, ξ_p_,i and ξ_p_,i,error were calculated for each data point, and then S_ij_ that results in ξ_p_,i,error = 10^−2^ was interpolated, up to the maximum S_ij_ = 10^8^ range used; this S_ij_ value is defined as S_ij_,max.
The results of the fitting process are shown as surface plots of S_ij_,max and x_p_,i,max across ψ_i_ vs. R_i_ for x_r_,i,0 of 0.01 (Figure 8a,b), x_r,i,_0 of 0.10 (Figure 8c,d), x_r_,i,0 of 0.90 (Figure 8e,f). First, consider the case of S_ij_,max for x_r_,i,0 of 0.01 (Figure 8a). S_ij_,max increases with increasing ψ_i_ but decreasing R_i_. Due to the rapid approach toward infinite S_ij_, an arbitrary maximum S_ij_ of 10^5^ was used for clarity in the plot, with the gray-colored region effectively infinity (i.e., S_ij_ > 10^8^). Note that while the modified pressure ratio (ψ_i_) varies between 1 and 10, the absolute pressure ratio (ψ) is a factor of 10^2^ higher and a S_ij_,max exists for 90% recovery up to an absolute pressure ratio of 10^3^. In addition, the S_ij_,max is only around 10^2^ at the more reasonable ψ of 10^2^. Given this limitation, further increases in S_ij_ from currently reported levels of CO_2_ separation membranes are unlikely to significantly enhance performance for very low feed fraction CO_2_ recovery.
Although not as severe as the x_r_,i,0 = 0.01 case, increasing the feed concentration to x_r_,i,0 = 0.10 still results in S_ij_,max that may affect research targets for membrane performance. As shown in Figure 8c, S_ij_,max exists for R_i_ of 0.90 up to a ψ of 10^2^, with a S_ij_,max of 10^2^ occurring at ψ = 45 and S_ij_,max of 10^3^ at ψ = 80. An equally important result is the maximum purity, shown in Figure 8d. As recovery increases so do the gradients of the purity contour lines, showing that as R_i_ is increased to 0.90 or higher the pressure ratio required to increase purity increases substantially. Thus high R_i_ targets with low x_r,i,_0 feeds become increasingly limited in the maximum purity regardless of improvement in the selectivity of the membranes.
The dotted line denoted as x_p_,i,max = 1 in each of the Figure 8 panels is the expected condition at which no asymptotic S_ij_ occurs, meaning that the impurities can decline substantially even for S_ij_ > 10^8^. This line was plotted using a relationship obtained by fitting
where the pressure ratio that separates the purity-limited zone is defined as ψ_i_,lim, and is calculated as a function of the inlet mole fraction, x_r_,i,0, and target recovery, R_i_. Although empirically derived here, this equation fits the data accurately with the dotted lines straddling the gray region limits for x_r_,i,0 from 1% (Figure 8a) to 90% (Figure 8e). Although this equation provides no information on the specific limiting S_ij_, it clearly defines the region in which S_ij_,lim exists for all conditions of a binary membrane separator. If a separator is operated at ψ_i_, > ψ_i_,lim, then no maximum exists and an increase in S_ij_ will always lead to a valuable increase in x_p_,i; however, if a separator is operated at ψ_i_, < ψ_i_,lim, then a x_p_,i,max is expected that results in a S_ij_,max above which no further gains in purity can be expected.
For high R_i_ targets coupled with low x_r_,i,0 feed sources, the S_ij_,max limit could result in the limitation being near currently obtained research levels. Again taking CO_2_ capture as the example, if a 90% R_i_ is coupled with a 10% x_r_,i,0 feed condition, then a ψ_i_,lim of 9.1 is obtained. Yet, some studies have optimized membrane separators at high recovery and suggested ψ_i_ of less than 10 [26]. More specifically, Kaldis et al. [30] reported that an increase in S_ij_ from 50 to 90 did not increase the purity for a binary separator operating at x_r_,i,0 of 0.35 and ψ_i_ of 7. Extracting information from the plot manually indicates the R_i_ was around 97% for both S_ij_, which would result in a ψ_i_,lim > 17 and a S_ij_,max of 46 using the techniques outlined above. Thus, any S_ij_ above 46 would not be expected to increase x_p_,i in a simple 1D model and the results of the current study can be considered validated against similar simulation studies. However, it is unclear how the results would change if pressure drop, and diffusion/concentration polarization effects were considered in the model. Additionally, no experimental studies were found that observed limited changes with S_ij_, so the validity of this with real systems is not well understood.
4. Conclusions
A study on the maximum purity of a single-stage gas separator has been performed across a wide parameter space, with insight into the maximum effective selectivity of the membrane imposed by the purity limitations. Due to the tendency of non-idealities to reduce membrane separator performance, the simplified model is suggested to provide the maximum theoretical purity of a single-stage membrane separator. Note, however, that the conclusions found herein are not to be interpreted as the maximum potential purity of a multi-stage separator. For a more complex separator configuration with multiple stages and recycle loops, the results of this study should be applied individually to each stage using the separator feed condition after the recycle loop has been added. Furthermore, this study has focused on collecting a purified permeate stream, but another technique could potentially involve the removal of impurities and collecting a purified retentate stream. This study did not explore such options, but it is suggested that the removal of all impurities is not likely to be the economical choice if high purity is required because it would require that all components in a multi-component mixture be more permeable than the desired component. Nevertheless, this topic is left open to future study. A summary of the main observations and conclusions are:
- An ideal membrane separator requires four input variables: the transport parameter, θ_i_, which balances the flow rate with the membrane permeance, the feed mole fraction, x_r_,i,0, the pressure ratio, ψ_i_, and the ideal selectivity, S_ij_;
- For the majority of industrial applications, x_r_,i,0 is a fixed parameter based on the upstream processes or source. Similarly, to reduce waste and meet a target recovery (e.g., carbon capture requiring RCO_2_ = 90%), θ_i_ becomes fixed. Thus, optimization of the purity is accomplished primarily with ψ_i_ and S_ij_;
- x_p,i_ increases with increasing ψ_i_ until a maximum is reached at ψ_i_ = ca. 10^2^. For ψ_i_ > 10^2^, only S_ij_ affects the purity. The required minimum S_ij_, or S_ij_,min, to achieve a target x_p_,i can be obtained by using the analytical solution for x_p_,i at R_i_ = 0 and then dividing by a factor obtained from the plot of S_ij_/S_ij_,min for S_ij_ vs. R_i_ (Figure 5b). If the S_ij_,min is greater than the attainable technology, then the information can provide either new research objective targets or show that a multi-stage separator is the only option for the target purity;
- Because ψ_i_ > 10^2^ causes ψ to become very large for low x_r_,i,0, there exist regimes in which a maximum S_ij_ is observed due to a maximum x_p_,i limitation. To determine if the desired operating condition has a S_ij_,max value, the target R_i_ and x_r_,i,0 are input into Equation (33) to obtain ψ_i_,lim. If operating at ψ_i_ < ψ_i_,lim then a S_ij_,max exists, but if operating with ψ_i_ > ψ_i_,lim then no maximum S_ij_ exists. S_ij_,max is dependent on x_r_,i,0, ψ_i_, and R_i_, so data must be gathered for the specific x_r_,i,0 of interest. Yet, as x_r_,i,0 decreases, the limitation with S_ij_ becomes more important, potentially limiting any reason for further research on increasing S_ij_.
The above information is expected to be useful in setting membrane ideal selectivity targets for specified separations and membrane technologies.
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