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Journal <strong>of</strong> Membrane Science 173 (2000) 61–71<strong>Simulation</strong> <strong>of</strong> <strong>multicomponent</strong> <strong>gas</strong> <strong>separation</strong> <strong>in</strong> a <strong>hollow</strong> <strong>fiber</strong> membraneby orthogonal collocation — hydrogen recovery from ref<strong>in</strong>ery <strong>gas</strong>esS.P. Kaldis, G.C. Kapantaidakis, G.P. Sakellaropoulos ∗Aristotle University <strong>of</strong> Thessaloniki and Chemical Process Eng<strong>in</strong>eer<strong>in</strong>g Research Institute, P.O. Box 1520, Thessaloniki 54006, GreeceReceived 26 August 1998; received <strong>in</strong> revised form 7 February 2000; accepted 8 February 2000AbstractModel<strong>in</strong>g <strong>of</strong> <strong>hollow</strong> <strong>fiber</strong> asymmetric membranes can provide useful guidel<strong>in</strong>es to achieve desirable <strong>separation</strong>s <strong>of</strong> <strong>multicomponent</strong><strong>gas</strong> mixtures. Especially <strong>in</strong> cases <strong>of</strong> high commercial <strong>in</strong>terest, such as hydrogen recovery from ref<strong>in</strong>ery streams,the accurate prediction <strong>of</strong> membrane <strong>separation</strong> performance is important. In this work, the appropriate model equationsare solved by orthogonal collocation to approximate differential equations, and to solve the result<strong>in</strong>g system <strong>of</strong> non-l<strong>in</strong>earalgebraic equations by the Brown method. This technique is applied for the first time <strong>in</strong> a <strong>multicomponent</strong> <strong>gas</strong> <strong>separation</strong> by<strong>hollow</strong> <strong>fiber</strong> membranes and <strong>of</strong>fers m<strong>in</strong>imum computational time and effort, and improved solution stability. The predictions<strong>of</strong> the mathematical model are compared with experimental results for the <strong>separation</strong> and recovery <strong>of</strong> hydrogen from a typical<strong>gas</strong> oil desulfurization unit for various feed pressures, temperatures and stage cuts. In general, there is a very good agreementbetween simulation and experimental results. Further application <strong>of</strong> the developed mathematical model to various ref<strong>in</strong>ery<strong>gas</strong> streams <strong>of</strong> <strong>in</strong>terest reveals that high permeate purity (99.95+), and high recovery (0.6–0.9), can be achieved even <strong>in</strong> aone-stage membrane unit. The reported experimental results and the theoretical analysis demonstrate the potential whichpolymer membrane technology has for the <strong>separation</strong> <strong>of</strong> hydrogen from ref<strong>in</strong>ery <strong>gas</strong> streams. © 2000 Elsevier Science B.V.All rights reserved.Keywords: Gas <strong>separation</strong>; Orthogonal collocation; <strong>Simulation</strong>; Hydrogen recovery; Ref<strong>in</strong>ery1. IntroductionPolymer membrane technology appears as an attractivealternative for the <strong>separation</strong> <strong>of</strong> <strong>gas</strong>es <strong>in</strong><strong>in</strong>dustrial processes. Compared with conventional<strong>separation</strong> technologies, membranes exhibit simplicity<strong>of</strong> operation and ma<strong>in</strong>tenance, small size, andeffective and reliable performance. These appeal<strong>in</strong>gfeatures enabled membrane technology to penetrate awide variety <strong>of</strong> markets and applications. After almost∗ Correspond<strong>in</strong>g author. Tel.: +30-31-996271;fax: +30-31-996168.E-mail address: sakel@verg<strong>in</strong>a.eng.auth.gr (G.P. Sakellaropoulos)two decades <strong>of</strong> cont<strong>in</strong>uous research development andefforts, polymer membranes have found applications<strong>in</strong>to a variety <strong>of</strong> <strong>in</strong>dustrial processes, such as air dehumidification,nitrogen production, ref<strong>in</strong>ery hydrogenrecovery, ammonia purge <strong>gas</strong> <strong>separation</strong>, landfill <strong>gas</strong>upgrad<strong>in</strong>g, acid and sour <strong>gas</strong> treatment, helium <strong>separation</strong>,and volatile organic compound recovery [1].Most <strong>of</strong> these applications refer to the <strong>separation</strong> <strong>of</strong><strong>multicomponent</strong> <strong>gas</strong> streams. As <strong>in</strong> the case <strong>of</strong> b<strong>in</strong>ary<strong>gas</strong>eous mixtures, the prediction <strong>of</strong> the <strong>separation</strong>performance and the evaluation <strong>of</strong> the membrane processare important. Successful membrane model<strong>in</strong>gand simulation can provide valuable <strong>in</strong>formation forthe design, optimization and economics <strong>of</strong> the overall0376-7388/00/$ – see front matter © 2000 Elsevier Science B.V. All rights reserved.PII: S0376-7388(00)00353-7


62 S.P. Kaldis et al. / Journal <strong>of</strong> Membrane Science 173 (2000) 61–71<strong>separation</strong> process with m<strong>in</strong>imum cost and effort. Forthese reasons, the <strong>multicomponent</strong> <strong>gas</strong> permeation hasattracted considerable attention. Sh<strong>in</strong>do et al. [2,3]developed approximate calculation methods for <strong>multicomponent</strong><strong>separation</strong>s <strong>in</strong> five flow patterns:one-sidemix<strong>in</strong>g, complete mix<strong>in</strong>g, cross flow, countercurrentand cocurrent flow. The ma<strong>in</strong> assumptions <strong>in</strong> thesestudies is that concentration gradients and pressuredrop on both sides <strong>of</strong> the permeator are negligible. Inorder to deal with concentration and pressure gradientsalong the permeator, Chen et al. [4] supplementedthe previous model by <strong>in</strong>troduc<strong>in</strong>g an average driv<strong>in</strong>gforce approximation. Sengupta and Sirkar [5,6] studiedexperimentally and theoretically the <strong>separation</strong> <strong>of</strong>a ternary <strong>gas</strong> mixture <strong>in</strong> a cocurrent and countercurrentpermeator. Their model <strong>of</strong>fers a good representation<strong>of</strong> the operation <strong>of</strong> a <strong>hollow</strong> <strong>fiber</strong> permeatoroperation by tak<strong>in</strong>g <strong>in</strong>to account the concentrationand pressure gradients. However, the model is limitedto only three-component mixtures and is based on af<strong>in</strong>ite difference algorithm; its extension to a highernumber <strong>of</strong> components would require considerablecalculation effort. The most detailed representation <strong>of</strong><strong>multicomponent</strong> <strong>separation</strong> <strong>in</strong> <strong>hollow</strong> <strong>fiber</strong> asymmetricmembranes has been presented thus far by Pan [7].However, the solution method <strong>of</strong> the nonl<strong>in</strong>ear differentialequations is very complicated and requires<strong>in</strong>itial estimates <strong>of</strong> pressure and concentration pr<strong>of</strong>ilesalong the <strong>fiber</strong>. Try<strong>in</strong>g to deal with this mathematicalcomplexity, Kovvali et al. [8] presented a computationalmethod which is based on a l<strong>in</strong>ear approximation<strong>of</strong> permeate and feed compositions at certa<strong>in</strong><strong>in</strong>tervals along the <strong>fiber</strong> length. With this technique,solution accuracy depends strongly on the number <strong>of</strong><strong>in</strong>tervals across the <strong>fiber</strong>. The error, compared with theexact solution <strong>of</strong> Pan, is between 5 and 30% for high(30) and low (10) number <strong>of</strong> <strong>in</strong>tervals, respectively.To overcome solution difficulties with <strong>multicomponent</strong>mixtures, Coker et al. [9] used a staged approach(100–1000 stages) to convert the pert<strong>in</strong>ent differentialequations to a set <strong>of</strong> coupled, non-l<strong>in</strong>ear differenceequations. This corresponds to a first order f<strong>in</strong>ite differencemethodology, with an iterative solution <strong>of</strong> thederived tridiagonal matrices. This method was usedto simulate the <strong>separation</strong> <strong>of</strong> a ref<strong>in</strong>ery stream and <strong>of</strong>impurity conta<strong>in</strong><strong>in</strong>g air streams, without further experimentalvalidation. The sensitivity <strong>of</strong> the techniqueto <strong>in</strong>itial estimates has not been discussed.In the present work, the orthogonal collocationtechnique was adopted to solve the mathematicalmodel which describes the <strong>multicomponent</strong> <strong>gas</strong> <strong>separation</strong><strong>in</strong> <strong>hollow</strong> <strong>fiber</strong> asymmetric membrane permeators.This technique has been already used effectively<strong>in</strong> b<strong>in</strong>ary systems [10], while its application <strong>in</strong> <strong>multicomponent</strong>systems has been announced [11,12].Orthogonal collocation is a widely applied method<strong>in</strong> numerous chemical eng<strong>in</strong>eer<strong>in</strong>g problems similarto or more complicated than the one exam<strong>in</strong>ed here.In all applications to boundary value, nonl<strong>in</strong>ear differentialequations, this method <strong>of</strong>fers more accurate,and stable solutions, with less computation time, ascompared to other conventional techniques, such asRunge-Kutta or f<strong>in</strong>ite differences [13,14].Among the numerous <strong>in</strong>dustrial areas where multicompoment<strong>gas</strong> <strong>separation</strong> occurs, the recovery <strong>of</strong>hydrogen from ref<strong>in</strong>ery <strong>gas</strong>es has been chosen hereas a case study for the application <strong>of</strong> the developedmathematical model. Hydrogen is a valuable <strong>gas</strong>which is produced and consumed <strong>in</strong> large quantitiesand <strong>in</strong> a wide variety <strong>of</strong> oil ref<strong>in</strong><strong>in</strong>g processes.Over the next decade, the demand for hydrogen <strong>in</strong>ref<strong>in</strong>eries is expected to <strong>in</strong>crease rapidly due to thegrow<strong>in</strong>g demand for environmentally friendly fuels,and the deterioration <strong>of</strong> crude oil quality. Excess hydrogencan be either produced on site or recoveredfrom a number <strong>of</strong> available processes which generatehydrogen as a by-product. The developed mathematicaltechnique for <strong>multicomponent</strong> <strong>gas</strong> <strong>separation</strong>s bymembranes has been applied here to evaluate hydrogen<strong>separation</strong> from various ref<strong>in</strong>ery streams <strong>in</strong> terms<strong>of</strong> permeate purity, hydrogen recovery, residue compositionand stage cut. In order to validate the results<strong>of</strong> the mathematical model, experimentation with a<strong>multicomponent</strong> <strong>gas</strong>eous mixture has been carriedout on a bench scale <strong>separation</strong> unit equipped with apolyimide <strong>hollow</strong> <strong>fiber</strong> membrane module.2. Mathematical model<strong>in</strong>gThe developed model is based on Pan’s <strong>in</strong>itialtheoretical formulation [7], modified and augmentedto account for the dependence <strong>of</strong> <strong>gas</strong> viscosity andpermeability on temperature and pressure. The modelconsists <strong>of</strong> a system <strong>of</strong> differential and algebraicequations with the appropriate boundary conditionsat the <strong>fiber</strong>s entrance and exit.


S.P. Kaldis et al. / Journal <strong>of</strong> Membrane Science 173 (2000) 61–71 63For the mathematical formulation, the follow<strong>in</strong>gma<strong>in</strong> assumptions are made [7]:1. The porous support<strong>in</strong>g layer <strong>of</strong> the membrane hasnegligible resistance to the <strong>gas</strong> flow, and diffusionalong the pore path is <strong>in</strong>significant due to high permeateflux.2. Feed <strong>gas</strong> pressure drop is negligible.3. Permeate flow is governed by the Hagen–Poiseuilleequation.4. The deformation <strong>of</strong> the <strong>fiber</strong> under pressure is negligible.5. The membrane permeabilities depend on temperatureby an Arrhenius type equation; pressure andconcentration dependence can also be <strong>in</strong>corporatedeasily, when needed (e.g. a dual sorption or equivalentmodel [10] can be used for CO 2 ).6. Gas viscosities are assumed to vary l<strong>in</strong>early withconcentration, and are calculated by Thodos’smethod [15].7. The effect <strong>of</strong> back-diffusion is negligible, thus, theconcentration <strong>of</strong> the permeate leav<strong>in</strong>g the membranesk<strong>in</strong> surface, is identical to that <strong>of</strong> the bulkpermeate stream outside the porous layer. This assumptionis valid for membranes with ultrath<strong>in</strong> sk<strong>in</strong>and a highly porous support<strong>in</strong>g layer. The use <strong>of</strong>this assumption <strong>in</strong> the present work was dictatedby the complexity which back-diffusion would <strong>in</strong>troduce<strong>in</strong> the <strong>multicomponent</strong> model. The requirementthat the sum <strong>of</strong> concentrations at every po<strong>in</strong>t<strong>of</strong> the membrane must be equal to unity results, as itwill be shown further, <strong>in</strong> the development <strong>of</strong> highlynonl<strong>in</strong>ear equations. By assum<strong>in</strong>g that the permeatebulk concentration is equal to the porous supportconcentration (i.e. no back-diffusion present)solution is simplified considerably.The permeation and transport <strong>of</strong> a <strong>multicomponent</strong> <strong>gas</strong>mixture conta<strong>in</strong><strong>in</strong>g (n) <strong>gas</strong>es through a differential element<strong>of</strong> the membrane are described by the follow<strong>in</strong>gset <strong>of</strong> differential and algebraic equations:2.1. Residue concentrationsdx idS = 1 ( )u α xii(x i − γy i ) − 1y ifor i = 1, 2,...n− 1 (1)n∑x i = 1 (2)i=12.2. Permeate concentrationsy i =α i x i y o1 − γ + γα i y <strong>of</strong>or i = 1, 2,... ,n− 1 (3)n∑y i = 1 (4)i=12.3. Feed side flowratedudS=−(1 − γ)y o(5)2.4. Permeate pressure build-updγ 2dS = A µ (u c − u) (6)µ 1whereu = U U f(7)γ = p P( )( )Q1 PS = πD o zN Fd U f(8)(9)256µ 1 RTU 2 fA =π 2 (Q 1 /d)P 3 D o Di 4N F2 (10)The three simultaneous differential Eqs. (1), (5) and(6), together with Eqs. (2)–(4), describe the permeateand residue mole fractions, the feed side flowrate, andpermeate pressure drop along the <strong>fiber</strong>. The permeateflow rate can be easily obta<strong>in</strong>ed from the materialbalances.The boundary conditions depend strongly on theoperational mode <strong>of</strong> the <strong>fiber</strong>. In countercurrent modethe area coord<strong>in</strong>ate starts at the <strong>fiber</strong>’s exit (z=0, S=0)and the follow<strong>in</strong>g conditions apply:2.5. B.C. for countercurrent operation(<strong>fiber</strong> exit) S = 0:x i = x fi u = 1 γ = γ o(<strong>fiber</strong> closed end) S= S o : dx idS = 0 u = u dγcdS =0(11)


64 S.P. Kaldis et al. / Journal <strong>of</strong> Membrane Science 173 (2000) 61–71In the case <strong>of</strong> cocurrent operation only slight modificationsare necessary, i.e.:1. u c <strong>in</strong> Eq. (6) should be replaced by 1, which is thedimensionless feed flow rate.2. The area coord<strong>in</strong>ate should start now at the <strong>fiber</strong>’sclosed end, and the boundary conditions should be:2.6. B.C. for cocurrent operation(<strong>fiber</strong> closed end) S= 0: dx idS =0 u = u dγcdS =0 .(<strong>fiber</strong> exit) S = S o : x i = x fi u = 1 γ = γ o(12)Solution <strong>of</strong> the <strong>multicomponent</strong> model is more complicatedthan for the b<strong>in</strong>ary mixture case [9] because<strong>of</strong> the requirement that the local sum <strong>of</strong> all molefractions <strong>of</strong> the components must be equal to unityat every po<strong>in</strong>t along the membrane. This results <strong>in</strong>the <strong>in</strong>troduction <strong>of</strong> the additional nonl<strong>in</strong>ear equations(Eqs. (3) and (4)), with a nonl<strong>in</strong>earity order (n) equalto the number <strong>of</strong> the mixture components. In eachiteration, the value <strong>of</strong> y o is obta<strong>in</strong>ed from the solution<strong>of</strong> Eqs. (3) and (4) and <strong>in</strong>troduced <strong>in</strong>to Eq. (5).Therefore, the solution algorithm should <strong>in</strong>clude aniterative Newton–Raphson (or equivalent) method <strong>in</strong>order to deal with these additional equations.To solve this set <strong>of</strong> differential and non-l<strong>in</strong>ear algebraicequations, orthogonal collocation [13] wasemployed along with the Brown method [16], as <strong>in</strong> thecase <strong>of</strong> a b<strong>in</strong>ary mixture model reported previously[10]. With this technique, the boundary value nature<strong>of</strong> this problem is reta<strong>in</strong>ed and the basic non-l<strong>in</strong>eardifferential equations for <strong>hollow</strong> <strong>fiber</strong> permeators areexpressed along the <strong>fiber</strong>. The accuracy <strong>of</strong> the techniquedepends on the number <strong>of</strong> collocation po<strong>in</strong>ts.As discussed previously for a b<strong>in</strong>ary mixture <strong>separation</strong>[9], a small number <strong>of</strong> collocation po<strong>in</strong>ts givespoor solution accuracy, while a high number <strong>of</strong> po<strong>in</strong>tsprolongs the solution convergence time with an <strong>in</strong>significanteffect on accuracy. Hence, six po<strong>in</strong>ts wereused here, because they <strong>of</strong>fer satisfactory accuracywith modest computational time. Results obta<strong>in</strong>edwith six collocation po<strong>in</strong>ts for <strong>multicomponent</strong> <strong>separation</strong>,us<strong>in</strong>g Pan’s data [7], show a difference <strong>of</strong> lessthan 5% compared to the solution obta<strong>in</strong>ed by Pan.The proposed technique does not require <strong>in</strong>itialguess<strong>in</strong>g <strong>of</strong> the concentration pr<strong>of</strong>ile <strong>in</strong>side the <strong>fiber</strong>,as <strong>in</strong> Pan’s f<strong>in</strong>ite difference solution [7]. It is also notsensitive to start<strong>in</strong>g values <strong>of</strong> residue concentrationand permeate pressure. In this work, a start<strong>in</strong>g value<strong>of</strong> unity was used for the residue concentration andfor the outlet value <strong>of</strong> the permeate pressure. Theorthogonal collocation technique permits easy evaluation<strong>of</strong> the performance <strong>of</strong> <strong>hollow</strong> <strong>fiber</strong> asymmetricmembrane permeators, for a variety <strong>of</strong> <strong>gas</strong>es, membranematerials and operat<strong>in</strong>g conditions, with highaccuracy, m<strong>in</strong>imum computational time and effort,thus hav<strong>in</strong>g improved stability compared to othermethods used.3. ExperimentalIn order to validate the predictions <strong>of</strong> the developedmathematical model, experimental data with a<strong>multicomponent</strong> mixture were used, obta<strong>in</strong>ed on amembrane bench scale unit, equipped with a modulesupplied by UBE Industries Ltd., Japan. The moduleconta<strong>in</strong>s polyimide <strong>hollow</strong> <strong>fiber</strong>s with 400 m outerand 200 m <strong>in</strong>ner diameter, and its effective surfacearea is 10 cm 2 . The membrane module can withstandpressures and temperatures <strong>of</strong> 35 bars and 100 ◦ C,respectively, while it can handle <strong>gas</strong> stream flows <strong>of</strong>up to 30 Nl/h. Fig. 1, shows a flow diagram <strong>of</strong> theexperimental set up. The membrane unit conta<strong>in</strong>s allnecessary ancillary <strong>in</strong>strumentation for pressure, temperature,flow rate measurement and control. The feedpressure is ma<strong>in</strong>ta<strong>in</strong>ed by a back-pressure regulator<strong>in</strong>stalled <strong>in</strong> the residue <strong>gas</strong> stream. Both permeateand residue flowrates are measured after expansionto atmospheric pressure. The <strong>hollow</strong> <strong>fiber</strong> module isplaced <strong>in</strong>to a water bath for controlled temperatureexperiments. The feed <strong>gas</strong> enters the shell side at highpressure and flows <strong>in</strong>side the <strong>fiber</strong>s <strong>in</strong> a counter currentmode to the permeate flow. The composition <strong>of</strong>each <strong>gas</strong> stream is analyzed by a Perk<strong>in</strong> Elmer 8500Gas Chromatograph equipped with a Porapak Q anda Molecular Sieve 5A columns.The polyimide membrane module was <strong>in</strong>itiallycharacterized by study<strong>in</strong>g the permeability <strong>of</strong> H 2 ,CH 4 ,C 2 H 6 ,CO 2 , pure <strong>gas</strong>es. Then, tests were carriedout with a <strong>multicomponent</strong> <strong>gas</strong> mixture simulat<strong>in</strong>gthe composition <strong>of</strong> a <strong>gas</strong> oil desulfurization ref<strong>in</strong>erystream. Such streams usually conta<strong>in</strong> H 2 , light hydrocarbons(C 1 ,C 2 ) and H 2 S. Tak<strong>in</strong>g <strong>in</strong>to account


S.P. Kaldis et al. / Journal <strong>of</strong> Membrane Science 173 (2000) 61–71 65Fig. 1. Flow diagram <strong>of</strong> the experimental set up.that polyimide membranes exhibit similar CO 2 andH 2 S permeability values and plasticization behavior,H 2 S was replaced <strong>in</strong> the test mixture by CO 2 ma<strong>in</strong>lyfor safety and handl<strong>in</strong>g reasons. The latter exist <strong>in</strong>concentrations between 5–10%. Thus the <strong>gas</strong>eousmixture which was fed to the <strong>hollow</strong> <strong>fiber</strong> membraneunit conta<strong>in</strong>ed 67.5% H 2 , 16.7% CH 4 , 4.3% C 2 H 6and 11.5% CO 2 .4. Results and discussionTable 1, summarises some potential sources for hydrogenrecovery <strong>in</strong> a typical oil ref<strong>in</strong>ery, as well asstream compositions, flowrates, pressures and temperatures[13]. In all cases, the concentration <strong>of</strong> hydrogenvaries from 30 to 90%, the stream temperaturesare relatively low (30–40 ◦ C) and the pressure variesfrom 12 to 40 bar. Undoubtedly, these values <strong>of</strong> majorprocess variables are all compatible with polymericmembrane <strong>separation</strong> technology.The permeation rates <strong>of</strong> pure H 2 and CH 4 <strong>gas</strong>eswere measured through the polyimide membrane, at40 ◦ C and 10 bar pressure, and <strong>of</strong> CO 2 and C 2 H 6 at40 ◦ C and 2 bar pressure. Activation energies were estimatedfrom permeation rate measurements <strong>of</strong> pure<strong>gas</strong>es <strong>in</strong> the temperature range 20–80 ◦ C, by apply<strong>in</strong>gan Arrhenius type equation. Table 2 gives the calcu-Table 1Ref<strong>in</strong>ery <strong>gas</strong> streams available for hydrogen recoveryNaptha Light Naptha Mild Mild Gas Gas OilHydrotreater (a) Isomerization (b) Hydrocrack<strong>in</strong>g (c) Hydrocrack<strong>in</strong>g (d) Oil (e) Desulfurization (f)Gas composition (%)H 2 90.0 85.0 32.4 35.7 74.0 79.9CH 4 5.2 5.2 23.1 25.4 13.3 14.4C 2 H 6 1.8 2.0 17.3 19.1 3.6 3.9C 3 ,C 4+ 3.0 7.8 18.0 19.8 1.7 1.8H 2 S – – 9.2 – 7.4 –Flowrate (Nm 3 /h) a 500 400 8000 7264 2500 2315Temperature ( ◦ C) a 35 30 40 40 40 40Pressure (bar g) a 40 19 12 12 25 25a Typical values for small-medium ref<strong>in</strong>eries.


66 S.P. Kaldis et al. / Journal <strong>of</strong> Membrane Science 173 (2000) 61–71Table 2Permeabilities and activation energies <strong>of</strong> pure <strong>gas</strong>es <strong>in</strong> polyimide membraneComponent Permeability, P a Activation Energy,(cm 3 (STP)/cm 2 /s/cm Hg)E p (kJ/mol)H 2 2.9×10 −4 13.9CO 2 0.93×10 −4 12.3CH 4 0.037×10 −4 9.3C 2 H 6 0.0064×10 −4 7.7a Measured at a pressure <strong>of</strong> 10 bar for H 2 and CH 4 , and 2 bar for CO 2 and C 2 H 6 ; temperature was 40 ◦ C for all <strong>gas</strong>es.lated permeation rates and activation energies for eachpure <strong>gas</strong> component. These values were then used <strong>in</strong>simulat<strong>in</strong>g the <strong>hollow</strong> <strong>fiber</strong> module performance withthe <strong>in</strong>vestigated <strong>gas</strong> mixtures. All <strong>in</strong>put data used <strong>in</strong>this work are experimental, and no trial and errormatch is <strong>in</strong>cluded. No extrapolation <strong>of</strong> permeabilitieshas been done us<strong>in</strong>g activation energies.The <strong>gas</strong>eous mixture was fed to the <strong>hollow</strong> <strong>fiber</strong>membrane unit at three different temperatures (22,40, 60 ◦ C) and five different pressures (5, 10, 15, 20,25 bar), while the permeate pressure was <strong>in</strong> all cases1 bar. The feed flow rate varied from 5 to 30 Nl/h.Gaseous concentrations <strong>in</strong> the permeate and residuestreams were measured as a function <strong>of</strong> stage cut. Inall cases, flowrates and concentrations were measuredwith an accuracy <strong>of</strong> ±5 and ±3%, respectively.Initially, the <strong>gas</strong>eous mixture was fed to the membraneunit at T=40 ◦ C and P=20 bar. Figs. 2 and 3,show the effect <strong>of</strong> stage cut on the composition <strong>of</strong>the residue and permeate stream, respectively. In allcases, experimental results (symbols) compare verywell with the predictions <strong>of</strong> the mathematical model(l<strong>in</strong>es), for the same operat<strong>in</strong>g conditions. The concentration<strong>of</strong> hydrogen <strong>in</strong> the residue decreases from60 to 40%, while the concentrations <strong>of</strong> the less permeablecomponents <strong>in</strong>crease slightly with stage cut. Thepermeate conta<strong>in</strong>s ma<strong>in</strong>ly H 2 and CO 2 , and only smallamounts <strong>of</strong> hydrocarbons. Their concentration variesonly slightly with stage cut. Hydrogen is enriched <strong>in</strong>the permeate stream up to about 93%. Carbon dioxideconcentrations <strong>in</strong> the permeate vary from 6.5 to 9.5%,while the total concentration <strong>of</strong> methane and ethaneis lower than 0.5%. Hydrogen recovery <strong>of</strong> the processcan be estimated as the product <strong>of</strong> hydrogen concentration<strong>in</strong> the permeate and <strong>of</strong> stage cut; for the experimentalresults <strong>of</strong> this work it <strong>in</strong>creases l<strong>in</strong>early withstage cut from 20 to 65%.The effect <strong>of</strong> pressure on residue and permeatestream compositions, are shown <strong>in</strong> Figs. 4 and 5, respectively.Results are presented for a constant stageFig. 2. Effect <strong>of</strong> stage cut on residue composition, T=40 ◦ C,P=20 bar, po<strong>in</strong>ts: experimental, l<strong>in</strong>es: simulations.Fig. 3. Effect <strong>of</strong> stage cut on permeate composition, T=40 ◦ C,P=20 bar, po<strong>in</strong>ts: experimental, l<strong>in</strong>es: simulations.


S.P. Kaldis et al. / Journal <strong>of</strong> Membrane Science 173 (2000) 61–71 67Fig. 4. Effect <strong>of</strong> feed pressure on residue composition at T=40 ◦ C,stage cut=0.5, po<strong>in</strong>ts: experimental, l<strong>in</strong>es: simulations.Fig. 6. Effect <strong>of</strong> feed temperature on residue composition atP=16 bar, stage cut=0.5, po<strong>in</strong>ts: experimental, l<strong>in</strong>es: simulations.cut (0.5) at 40 ◦ C and pressures vary<strong>in</strong>g from 5 to25 bar. Aga<strong>in</strong> good agreement between theoretical predictionsand experimental results is obta<strong>in</strong>ed. With theexception <strong>of</strong> a slight <strong>in</strong>crease <strong>of</strong> hydrogen permeateconcentration, the other <strong>gas</strong>es <strong>in</strong> both streams rema<strong>in</strong>almost unaffected by feed pressure. This behaviourcan be attributed to the fact that the permeabilities <strong>of</strong>constant <strong>gas</strong>es, such as H 2 , do not depend on pressure.The latter is not valid for non-ideal <strong>gas</strong>es suchas CO 2 and C x H y which show pressure dependentpermeabilities [1]. Nevertheless, their low feed partialpressures (about 0.06– 0.25 bar) <strong>in</strong> the experiments <strong>of</strong>this work, result <strong>in</strong> a negligible change <strong>of</strong> permeabilitywith feed pressure and, therefore, <strong>in</strong> no pressuredependence <strong>of</strong> the exit stream concentration. Residueand permeate concentrations were also exam<strong>in</strong>ed forthree different temperatures (22, 40, 60 ◦ C), at a feedpressure <strong>of</strong> 16 bar and a stage cut <strong>of</strong> 0.5 (Figs. 6 and7). The <strong>gas</strong>es which have the highest activation energies<strong>of</strong> permeation [1], i.e. H 2 and CO 2 , show someFig. 5. Effect <strong>of</strong> feed pressure on permeate composition at T=40 ◦ C,stage cut=0.5, po<strong>in</strong>ts: experimental, l<strong>in</strong>es: simulations.Fig. 7. Effect <strong>of</strong> feed temperature on permeate composition atP=16 bar, stage cut=0.5, po<strong>in</strong>ts: experimental, l<strong>in</strong>es: simulations.


68 S.P. Kaldis et al. / Journal <strong>of</strong> Membrane Science 173 (2000) 61–71Fig. 8. Effect <strong>of</strong> feed pressure and temperature on feed flow rate,stage cut=0.5, po<strong>in</strong>ts: experimental, l<strong>in</strong>es: simulations.Fig. 9. Effect <strong>of</strong> stage cut on H 2 theoretical permeate mole fraction,(a–f: Ref<strong>in</strong>ery processes, cf. Table 1).concentration change with temperature, especially <strong>in</strong>the residue stream. Such change is small, because <strong>of</strong>the low activation energies (10–25 kJ/mole) associatedwith the permeation process.Although the role <strong>of</strong> pressure and concentration oncomponent concentrations seems to be m<strong>in</strong>or, theseparameters have a pronounced effect on the modulefeed flow rate. The latter is directly proportional tothe flow capacity <strong>of</strong> a <strong>hollow</strong> <strong>fiber</strong> module with certa<strong>in</strong>dimensions and characteristic properties. Fig. 8shows that both variables, and especially pressure atelevated temperatures, result <strong>in</strong> significant <strong>in</strong>crease<strong>of</strong> the throughput <strong>of</strong> the polyimide <strong>hollow</strong> <strong>fiber</strong> unit.S<strong>in</strong>ce flow rate is <strong>in</strong>versely proportional to the requiredmembrane surface area, at given operat<strong>in</strong>g conditions(T, P concentration, etc.), process economics shouldimprove appreciably at elevated pressures and temperatures.<strong>Simulation</strong> and experimental results here,show that for a five fold pressure <strong>in</strong>crease (5–25 bar)at 22 ◦ C the membrane area requirements decrease bya factor <strong>of</strong> five. A further area decrease, to about 10%<strong>of</strong> the orig<strong>in</strong>al one, should be possible by operat<strong>in</strong>g atelevated temperatures (e.g. 60 ◦ C).Follow<strong>in</strong>g validation, the mathematical model wasused to predict the performance <strong>of</strong> a membrane unitfor the <strong>separation</strong> <strong>of</strong> hydrogen from other ref<strong>in</strong>ery<strong>of</strong>f-<strong>gas</strong>es. The <strong>in</strong>put values <strong>of</strong> pressure and temperatureto the model were, <strong>in</strong> each case, those <strong>of</strong> therespective operat<strong>in</strong>g conditions at the exit <strong>of</strong> the ref<strong>in</strong>-ery process (c.f. Table 1) while the permeate pressurewas 1 bar <strong>in</strong> all cases. Fig. 9 summarizes the effect <strong>of</strong>stage cut on the concentration <strong>of</strong> hydrogen <strong>in</strong> the permeatestream for a number <strong>of</strong> feed <strong>gas</strong> streams. Whenthe ref<strong>in</strong>ery stream conta<strong>in</strong>s significant amounts <strong>of</strong> H 2(85–90%), hydrogen purity <strong>in</strong> the permeate stream isquite high (99.9%, curves a, b and f) and relatively <strong>in</strong>sensitiveto stage cut. For low hydrogen feed concentrations,as <strong>in</strong> the case <strong>of</strong> mild hydrocrack<strong>in</strong>g process(curves c, d) permeate purity decl<strong>in</strong>es rapidly withstage cut. Hydrogen recovery <strong>in</strong> the permeate streamcan reach values up to 90% at high stage cuts, even <strong>in</strong>the cases where the correspond<strong>in</strong>g H 2 purity is relativelylow (Figs. 9 and 10, respectively, curves e andc). Permeate streams rich <strong>in</strong> hydrogen can be recycled<strong>in</strong> the ref<strong>in</strong>ery, depend<strong>in</strong>g on the ref<strong>in</strong><strong>in</strong>g processused. For example, streams with 90% H 2 can be usedeffectively <strong>in</strong> hydrotreatment processes for heavy oilupgrad<strong>in</strong>g and for oil desulfurization or denitrogenation.Apart from the H 2 -rich permeate, the membraneresidue stream is also important as an additional <strong>gas</strong>fuel source. Fig. 11 demonstrates the effect <strong>of</strong> stagecut on hydrogen residue concentration. In all cases,high stage cut values lead to hydrogen depleted residuestreams. The depletion is more <strong>in</strong>tense for low hydrogenconcentration <strong>in</strong> the feed (curves c, d), wherelow to moderate (0.1–0.3) stage cuts can be achieved.Similarly, the effect <strong>of</strong> stage cut on the concentration


S.P. Kaldis et al. / Journal <strong>of</strong> Membrane Science 173 (2000) 61–71 69Fig. 10. Effect <strong>of</strong> stage cut on H 2 theoretical recovery <strong>in</strong> permeatestream, (a–f: Ref<strong>in</strong>ery processes, cf. Table 1).Fig. 12. Effect <strong>of</strong> stage cut on CH 4 theoretical residue molefraction, (a–f: Ref<strong>in</strong>ery processes, cf. Table 1).<strong>of</strong> the light hydrocarbons (methane, ethane) for variousprocesses is shown <strong>in</strong> Figs. 12 and 13. In general,the residue mole fraction <strong>of</strong> the least permeable component<strong>in</strong>creases most with stage cut. For <strong>in</strong>stance,ethane concentration <strong>in</strong> the residue becomes 2.5–3times higher than that <strong>in</strong> the feed <strong>of</strong> mild hydrocrack<strong>in</strong>gprocess (curves c, d; Fig. 13).From the above discussion it is evident that high purityhydrogen can be recovered from various ref<strong>in</strong>ery<strong>gas</strong> streams even <strong>in</strong> a one stage membrane unit and forwork<strong>in</strong>g conditions as imposed by the <strong>of</strong>f-<strong>gas</strong> com-Fig. 13. Effect <strong>of</strong> stage cut on C 2+ theoretical residue molefraction, (a–f: Ref<strong>in</strong>ery processes, cf. Table 1).position, pressure and temperature. With the reportedhere procedure <strong>of</strong> orthogonal collocation, and its goodagreement with experiment, a variety <strong>of</strong> operat<strong>in</strong>g conditionscan be simulated easily, rapidly and accurately,for further process evaluation and optimization.5. ConclusionsFig. 11. Effect <strong>of</strong> stage cut on H 2 theoretical residue mole fraction,(a–f: Ref<strong>in</strong>ery processes, cf. Table 1).The majority <strong>of</strong> <strong>gas</strong> <strong>separation</strong>s encountered <strong>in</strong><strong>in</strong>dustrial level refer to <strong>multicomponent</strong> mixtures.


70 S.P. Kaldis et al. / Journal <strong>of</strong> Membrane Science 173 (2000) 61–71Among them the <strong>separation</strong> <strong>of</strong> hydrogen from lighthydrocarbons <strong>in</strong> oil ref<strong>in</strong>eries is an issue <strong>of</strong> majorimportance. Polymer membranes can be viewed asan attractive alternative <strong>of</strong> conventional compet<strong>in</strong>gmethods. In that direction, process simulation andoptimization by model<strong>in</strong>g <strong>of</strong> membrane <strong>multicomponent</strong><strong>separation</strong>s, can be a powerful theoretical tool.In this work, membrane model<strong>in</strong>g is approached forfirst time by the orthogonal collocation method, toensure solution stability with low computational timeand effort. Model predictions have been validatedby experimental results obta<strong>in</strong>ed from the <strong>separation</strong><strong>of</strong> a <strong>multicomponent</strong> mixture <strong>in</strong> a polyimide membraneunit and the general comparison is very good.The mathematical model has been applied furtherto various other ref<strong>in</strong>ery streams. Results show thateven for a one-stage membrane unit, high hydrogenpermeate purity (up to 99+%) and significant totalrecovery (up to 90%) can be achieved for moderateto high (0.2–0.6) stage cuts. The residue stream, rich<strong>in</strong> hydrocarbons and conta<strong>in</strong><strong>in</strong>g 10% <strong>of</strong> the <strong>in</strong>itialhydrogen can be further separated <strong>in</strong> a second stage,or used as a <strong>gas</strong> fuel.u dimensionless feed side <strong>gas</strong> flow rateu c dimensionless f<strong>in</strong>al residue <strong>gas</strong> flow rate(u c =U c /U f )x fi feed concentration <strong>of</strong> component i(mole fraction)x i residue concentration <strong>of</strong> component i,mole fractiony i permeate concentration <strong>of</strong> component i,mole fractiony o sum <strong>of</strong> permeate concentrations def<strong>in</strong>edby Eqs. (3) and (4)z <strong>fiber</strong>s length variableGreek symbolsα i membrane permselectivity (permeability<strong>of</strong> component i to permeability <strong>of</strong> lesspermeable component Q 1 )γ ratio <strong>of</strong> permeate pressure to feed pressureγ o ratio <strong>of</strong> permeate pressure to feed pressureat the permeate outletµ viscosity <strong>of</strong> <strong>gas</strong> mixture (Pa s)µ 1 viscosity <strong>of</strong> the less permeablecomponent (Pa s)6. NomenclatureA dimensionless constant def<strong>in</strong>ed by Eq. (10)d effective sk<strong>in</strong> thickness <strong>of</strong> asymmetricmembrane (m)D i <strong>hollow</strong> <strong>fiber</strong> <strong>in</strong>side diameter (m)D o <strong>hollow</strong> <strong>fiber</strong> outside diameter (m)L total <strong>fiber</strong> length (m)NF total number <strong>of</strong> active <strong>fiber</strong>s <strong>in</strong> the <strong>hollow</strong><strong>fiber</strong> moduleP feed-side pressure (Pa)p permeate-side pressure (Pa)Q 1 permeability <strong>of</strong> the less permeablecomponent (mol/m s Pa)R ideal <strong>gas</strong> constantS dimensionless membrane area def<strong>in</strong>ed byEq. (9)S o dimensionless membrane area, with total<strong>fiber</strong>s lengthT temperature (K)U feed side <strong>gas</strong> flow rate (mol/s)U c f<strong>in</strong>al residue <strong>gas</strong> flow rate (mol/s)feed <strong>gas</strong> flow rate (mol/s)U fAcknowledgementsThe authors wish to thank the European Union andthe General Secretariat <strong>of</strong> Research and Technology<strong>of</strong> Greece for f<strong>in</strong>ancial support <strong>of</strong> this work throughprojects ECSC 7220-EC/703, 7220-ED/082 and HY-PER 8991. Mr Kapantaidakis thanks also the HellenicAspropyrgos Ref<strong>in</strong>ery, Greece, for a research scholarship.Part <strong>of</strong> this work was presented at the 10th NorthAmerican Membrane Society Meet<strong>in</strong>g held <strong>in</strong> Cleveland,Ohio, USA, 16–21 May 1998.References[1] R.D. Noble, S.A. Stern, Membrane Separations Technology,Elsevier, Amsterdam, 1995.[2] Y. Sh<strong>in</strong>do, T. Hakuta, H. Yoshitome, Calculation methodsfor <strong>multicomponent</strong> <strong>gas</strong> <strong>separation</strong> by permeation, SeparationSci. Tech. 20 (1985) 445.[3] Y. Sh<strong>in</strong>do, N. Itoh, K. Haraga, A theoretical analysis <strong>of</strong><strong>multicomponent</strong> <strong>gas</strong> <strong>separation</strong> by means <strong>of</strong> a membrane withperfect mix<strong>in</strong>g, Separation Sci. Tech. 24 (1989) 599.


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