. avfiflmpfi w. 3:. L» a a... 5.1.! trial? u . £an . ”Anglia,“ } 9...... .umnw‘;..ll.avl‘|‘v\c “I! :. 0?..l‘t1lvil', cl, ‘0‘. I:|\| .3 A Iquol. tilt I! I. II... .9. but: , x. in. Fania; .. .3. imfluIqlglflmwlfllrg/ilfll(Ill £000 LIBRARY Michigan State University PLACE IN RETURN BOX to remove this checkout from your record. TO AVOID FINE return on or before date due. MAY BE RECALLED with earlier due date if requested. A 1‘ uxlx A RNEDUE DATE DUE DATE DUE W! 4 Ltd?“ J Cal OCT 2 6 2006 ‘ 11/00 chlRODfiDmpSS—p.“ SORPTION AND DIFFUSION OF ETHYL ACETATE VAPOR IN POLYIMIDE-CLAY NANOCOMPOSITE FILMS By Wenzhen Cheng A THESIS Submitted to Michigan State University In partial fulfillment of the requirements for the degree of MASTER OF SCIENCE School of Packaging 1 999 ABSTRACT SORPTION AND DIFFUSION OF ETHYL ACETATE VAPOR IN POLYIMIDE-CLAY NANOCOMPOSITE FILMS By Wenzhen Cheng Sorption and diffusion of an organic vapor are key processes to gain an understanding of the mass transfer properties of polyimide-clay nanocomposite films. The sorption characteristics of ethyl acetate vapor in polyimide-clay films were determined by micro-gravimetry and the diffusion characteristics were calculated from the sorption kinetics at different vapor activities, by curve fitting. The vapor activity dependence of the solubility and diffusion coefficients, S and D, respectively, is represented by a modified dual-mode sorption model and a tortuosity model. The montmorillonite clay mineral, which is hybridized with a polyimide, consists of stacked silicate sheets about 10 A in thickness, and 800 ~ 2000 A in length. In this nanocomposite film, montmorillonite is dispersed homogeneously into the polyimide matrix and oriented parallel to the film surface. Due to this structure, the nanocomposite showed excellent organic vapor barrier properties. Only a small volume fraction of clay (i.e. 2.5v/v%) resulted in a significant decrease in the diffusion coefficient. Furthermore, solubility and solubility coefficient values for the polyimide-clay composites were similar to those obtained for the non-clay loading polyimide films, over the range of ethyl acetate vapor activity levels studied. The permeant studies indicated that the organic vapor diffusion coefficients increased exponentially with an increase in local penetrant concentration within the polymer membrane. The studied also showed that the diffusion coefficients decreased dramatically with an increase in clay loading level of the polymer membranes. To My beautiful wife, Xiaole Lovely baby boy, Christopher iii Acknowledgements Thank god for giving me a precious opportunity to study and to have a good time in School of Packaging of Michigan State University. I would like to thank Dr. Jack Giacin from my heart. During the years of study, Dr. Giacin has given me a generous financial support and valuable academic advice. Without this, I can't complete my study and this project. Also, I would like to thank my co-advisor Dr. Ruben Hernandez and Dr. Thomas Pinnavaia, for their sourceful guidance through the entire project. I appreciate Christopher Barr, former graduated student, for helping me get started with this research project. In addition, I am very grateful to the Center for Fundamental Materials Research whose funding made this project possible. Finally, my wife and my son deserve my deepest love for their love, support and good will during the years studying in this far—away-from- home country. iv Table of Contents List of Tables .............................................................................. vi List of Figures ............................................................................. ix List of Symbols and Abbreviations .................................................... xii Introduction ............................................................................... 1 Literature Review ....................................................................... 4 Polymer-clay nanocomposites .......................................................... 4 1. General concepts of nanocomposite .......................................... 4 2. Recent study and advance in polymer-clay nanocomposites .............. 6 3. The barrier improvement of polyimide-clay nanocomposites ............. 15 Ideal diffusion and sorption of organic vapor in glassy polymers ................. 19 Non-ideal sorption and diffusion of organic vapor in the glassy polymers ....... 21 Model for the path of a diffusing gas through the polyimide-clay nanocomposite 25 Materials, Instrument and Methods ............................................... 27 A. Materials for synthesis of clay/polyimide nanocomposites ............... 27 B. Materials for sorption tests .................................................... 28 C. Synthesis of clay/polyimide nanocomposite films ......................... 29 D. Cahn 2000 Electrobalance ..................................................... 31 E. Gravimetric sorption method .................................................. 33 F. Gas Chromatographic Analysis ............................................... 37 G. Calculation of diffusion coefficient .......................................... 44 1) "Half sorption time" method ......................................... 46 2) Gauss-Newton curve fitting method ................................. 47 3) Least square method ................................................... 49 4) "Consistency for continuous flow" method ........................ 50 H. Calculation of solubility coefficient .......................................... 52 1. Calculation of parameters of dual-mode sorption method ................. 54 Results and Discussion .................................................................. 56 Sorption properties ......................................................................... 56 1. Equilibrium Solubility for Ethyl Acetate Organic Vapor ................... 56 2. Solubility coefficient .............................................................. 62 3. Dual mode sorption parameters .................................................. 65 Diffusion properties ........................................................................ 69 1. Effect of Ethyl Acetate Vapor Activity .......................................... 71 2. Effect of Clay-Loading on Polyimide-clay Nanocomposites ................. 77 3. Aspect Ratio and Tortuosity ....................................................... 80 Error Analysis .............................................................................. 83 1. Uniform of the nanocomposite films ........................................... 83 II. Thickness variance of the films ................................................. 84 III. Concentration variance of the permeant ..................................... 85 VI. Temperature variance of testing system ...................................... 87 V. Non-Fickian sorption behavior ................................................. 88 Summary and Conclusion .............................................................. 89 Recommendation and Future Research .............................................. 92 Appendices .................................................................................. 94 Bibliography ................................................................................ 99 vi Table 1 Table 2 Table 3 Table 4 Table 5 Table 6 Table 7 Table 8 Table 9 Table 10 Table 1 1 List of Tables Gas chromatograph condition used for ethyl acetate quantification 39 Comparison of the ethyl acetate vapor activity in the hangdown tube obtained by the experimental and literature ............................... 43 Vapor activity dependence of solubility values in polyimide-clay nanocomposites ........................................................ 58 Variation in normalized sorption time (tss) to equilibrium in polyimide- clay nanocomposites (1mil film thickness) ............................... 59 Equilibrium solubility values of clay powder and original unfilled polyimide film ........................................................... 59 Comparison of experimental and calculated absorption properties of a polyimide clay hybrid as a function of ethyl acetate vapor activity 60 The calculated solubility coefficients (cc [STP]/cc . pa") for the non-clay and 1.25 % v/v polyimide clay nanocomposites ............................ 62 Dual-Mode Sorption Parameters for Polyimide film ..................... 66 Diffusion coefficients (mz/s) for non-clay polyimide films, determined by the different methods as a function of vapor activity. ................... 69 Diffusion coefficients (mz/s) of clay-loading polyimide films, determined as a function of clay loading and vapor activity. ......................... 70 Vapor activity dependence of diffusion coefficient values in polyimide- clay nanocomposites. ........................................................ 73 vii Table 12 Table 13 Table 14 Table 15 Table 16 Effect of ethyl acetate vapor pressure on the permeability of Clay/polyimide Composite films at 23 °C in the Literature (Gu, 1997) ...................................................................................... '76 Comparison of the diffusion coefficient values of non-clay polyimide composite films/ethyl acetate at 23 °C between the Literature (Gu, 1997) and this study ................................................................... 76 Comparison of the estimated aspect ratio with the literature data .. 82 Thickness distribution of the test film ..................................... 84 Residual errors by the Gauss-Newton method as a function ethyl acetate vapor activity ................................................................... 88 viii Figure 1 Figure 2 Figure 3 Figure 4 Figure 5 Figure 6 Figure 7 Figure 8 Figure 9 Figure 10 Figure 11 Figure 12 Figure 13 List of Figures Structure differences in intercalated and exfoliated polymer-clay nanocomposites .......................................................... 4 A model for the path of a diffusing gas through the polyimide clay nanocomposite films ......................................................... 25 Synthesis of polyimide clay hybrid ....................................... 3O Schematic of gravimetric sorption experimental .......................... 36 Ethyl acetate calibration curve ........................................ 40 Half sorption time determined by the sorption profile ............... 46 [[(Mcm - Mcxp) 2 /(Mca.c_) 2/n] as a function of the best estimated diffusion coefficient value for the polyimide film ................................. 48 Z[(Mcalc_ - Mexp.) 2] as a function of the best estimated diffusion coefficient value for the polyimide film ................................................. 49 The " l/X versus time" plot of a polyimide film ......................... 5] Determining the Henry's law constant by dual-mode sorption mod :1 .. 55 Determining parameters by Langmuir Plot ............................... 55 A representation plot of Mt/ M55 as a function of time, for the sorption of ethyl acetate by the non-clay polyimide film ........................... 57 A representation plot of Mt/ Ms, as a function of time, for the sorption of ethyl acetate by the clay-loading polyimide film ........................ 57 ix Figure 14 Figure 15 Figure 16 Figure 17 Figure 18 Figure 19 Figure 20 Figure 21 Figure 22 Figure 23 Figure 24 Figure 25 Solubility values comparison for the 1.25 v/v% clay loading composite, between the experimental and calculated values. ........................ 61 Solubility coefficients of non-clay polyimide films ..................... 64 Solubility coefficients of 1.25 v/v% clay/polyimide films ............. 64 Typical sorption isotherm of ethyl acetate in non-clay polyimide films at Concentration (CD = KD . p) by Henry's Law is a function of the vapor pressure Langmuir solubility (CH = C - CD) is not a function of the vapor pressure at a relatively high vapor partial pressure Diffusion coefficients of non—clay polyimide film versus organic vapor activity Diffusion coefficients of 1.25 v% polyimide-clay nanocomposite films versus organic vapor activity ................................................. ‘72 Variation in normalized sorption of ethyl acetate in non-clay polyimide film with time after introduction of vapor at 23 °C ....................... 73 Clay-loading dependence of diffusion coefficients in Polyimide-clay Nanocomposites Variation in clay—loading dependency of normalized sorption of ethyl acetate (av = 0.68) in polyimide/clay films with time after introduction of vapor at 23 °C Figure 26 Figure 27 Figure 28 Relative diffusion coefficient value of polyimide-clay nanocomposite at ethyl acetate vapor activity av = 0.68 @23 °C 0%RI-l .................. 81 Equilibrium vapor pressure in the lower portion of the electrobalance hangdown tube as a function of time. .................................... 86 Polyimide-clay composite sorption profile under alternating system temperature. ................................................................... 87 xi av Cexp C68! List of Symbols and Abbreviations penetrant activity Fihn thickness, m represents Ft/Foo hole affinity constant, pa'l experimental solubility values, g/g sorbant calculated solubility values, g/g sorbant solubility values of polyirrride matrix, g/g sorbant solubility values of clay powder, g/ g sorbant concentration of the standard solution for gas chromatography analysis, cc/cc vapor concentration of point A, cc gas(STP)/cc polymer vapor concentration of point B, cc gas(STP)/cc polymer hole saturation constant, cc[STP]/cc polymer concentration independence diffusion coefficient, mz/sec limiting diffusion coefficient, mz/sec thickness of a film, m total path of a diffusing gas, m diffusion coefficient of nanocomposite, m2 / sec diffusion coefficient of polymer matrix, m2 / sec permeation rate of permeation flux afier infinite time gas flow rate at point A, cc/sec gas flow rate at point B, cc/sec xii Ft k0 M00 (or M5,) Mcalc. Mcxp. permeation rate of permeation flux at time t rate of diffusion Henry's law constant, cc[STP]/cc ' pa'l length of the clay platelet, m total amount of the sorbate uptake in the polymer afier infinite time, g theoretical amount of the sorbate uptake in the polymer at time t, g experimental data of the sorbate uptake in the polymer at time t, g total amount of the sorbate uptake in the polymer at time t, g steady state permeability coefficient, cc[STP] - m/m2 - pa - sec vapor partial pressure, pa vapor partial pressure at point A, pa vapor partial pressure at point B, pa permeability coefficient of nanocomposite, cc[STP] - m/m2 ~ pa - sec test vapor partial pressure of ethyl acetate, pa tortuosity factor a coefficient of Equation 43 permeability coefficient of polymer matrix, cc[STP] - m/m2 - pa - sec saturation vapor pressure of ethyl acetate, pa quantity injected for gas chromatography analysis, g solubility coefficient, cc[STP]/cc - pa'l solubility coefficient of nanocomposite, m2 / sec solubility coefficient of polymer matrix, m2 / see time of sorption experimental, sec xiii DOV AV a“). {‘3 é Temperature of point A, 0C Temperature of point B, °C volume of the system at point A, cc volume of the system at point B, cc volume fraction of a clay width of the clay platelet, m represents 02/4D t xiv Introduction The sorption and diffusion of low molecular weight compounds, such as water vapor and organic vapors, are of major concern in the use and application of polymeric packaging materials, since such product/package systems are typically stored in an environment which may contain organic and/or water vapors. New packaging materials with high strength, light weight, high barrier, more fimctionality and low cost are expected to be developed for future industry use. For the purpose of these applications, polyimides have been evaluated as a promising class of material, with potential applications in packaging. Polyimides are widely used for microelectronics because they exhibit high heat resistance, chemical stability and superior electric properties (Ghosh, 1996). In recent years, composite films made of polyimide have been used as membranes for the industrial dehydration of organic vapor by the per-vaporization membrane process (Okamoto et al., 1992). Polyimide membranes may also have packaging applications, such as in electronic packaging, where the barrier property of the package system is one of the major concerns. It would be desirable to reduce the cost and amount of vapor absorption by polyimides, as well as to enhance their barrier properties, since those properties of polyimides are not sufficient for advanced electronics use. Polymer-clay nanocomposites are a new class of material designed to meet these demands. In this case, the nano-size clay layers (10 A - thick) are homogeneously dispersed in the polymer matrix. Due to their specific molecular composition, nanocomposites usually exhibit significant enhancement in mechanical, optical, conductive, nonlinear optical and barrier properties, as compared to the single components and conventional composites (Lan, 1994). As montmorillonite is composed of stacked silicate sheets, it has a low thermal expansion coefficient and high gas barrier properties (Yano et al., 1993). Polymer-clay nanocomposites are usually stable after the hybrid complexes are formed, and do not undergo phase separation. The synthesis and properties of a polyimide-clay nanocomposite had been reported in the early 90's by Yano (1991). It was found that when a specific ammonium ion is chosen as the intercalating reagent, montmorillonite disperses homogeneously in dimethyl-acetamide, which is a solvent for the preparation of polyimides. The montmorillonite dispersion can be mixed with the precursor solution of the polyimide, and after removing the solvent, the polyimide-clay nanocomposite membranes were obtained. The resultant polyimide-clay nanocomposite showed excellent gas barrier properties to C02, 02 and water vapor. Organic vapor permeability of the nanocomposite membranes has also been reported for 2.5 % (v/v) polyimide-clay nanocomposite film and showed an 85% reduction in organic vapor transmission rate, when compared to the polyimide film without clay inclusion (Gu, 1997). The solubility and diffusivity of a penetrant in a polymer membrane depends on the temperature and the vapor activity in contact with the polymer. Knowledge of the correlation between the solubility and diffusion coefficients of the penetrant in the polymer membrane and penetrant vapor activity in the atmosphere surrounding the membrane, would make possible the calculation of either the variation of penetrant sorption extent with time on the specific conditions, or its permeability rate through the membrane. Yano (1993) reported that the difiusion coefficient of Oz and water vapor in polyimide/clay hybrid could be well explained by the tortuosity model. In the present study, the sorption and diffusion characteristics of ethyl acetate vapor in polyimide were described by microgravimetry and the tortuosity model. The objective of the study is to gain an understanding of the mass transfer properties of nanocomposites derived from organic polymers and plate-like inorganic inclusions (i.e. clays) and organic penetrants, and the principles governing the barrier properties of nanocomposites derived from organic polymers and plate-like inorganic inclusions. The present study therefore includes measurements of the sorption and dirfusion of ethyl acetate into polyimide membranes with and without clay inclusion, over a range of sorbate activities. Isotherms were determined gravimetrically at 23 i 1 °C, 0% RH at O, 1.25, 2.5 and 5 % (v/v) clay loading. To provide insight into the activity dependence of the mass transfer process, seven vapor activity levels were evaluated: 0.15, 0.21 , 0.27, 0.34, 0.44, 0.55 and 0.68, respectively. Literature Review Polymer-Clay Nanocomposite 1. General Concepts of Nanocomposites lnlcrcalation Exfoliarion Figure 1. Structure differences between intercalated and exfoliated polymer-clay nanocomposites. In general, there are two categories of polymer-clay nanocomposites, as presented above in Figure 1. As shown, the intercalated and exfoliated nanocomposites exhibit structural differences. Compared to the nanocomposite, the clay tactoids in conventional composites exist in their original aggregated state with no intercalation of the polymer matrix into the clay gallery regions. The intercalated polymer-clay nanocomposites are of interest because organic polymer layers and inorganic silicate layers are alternatively interstratified at the molecular level --- at least one dimension in the size range of a nanometer (l x 10'9 meter, or 1/25 x 106 inch) (N anocor, Inc. web page, 1997). Polymer/clay nanocomposites are differentiated from conventional composites by the fact that the size of the fillers is so small that the nanocomposite is macroscopically homogenous. Exfoliated polymer—clay nanocomposites possess unique structural and mechanical properties. For example, the exfoliated clay layers (10 A - thick), which are dispersed into the polymer matrix, simulate the fibers in fiber-reinforced-plastics (Lan, 1994) The physical and mechanical properties of a nanocomposite are determined not only by the bulk properties of each component, but also by complex interactions between the building blocks and their interface. Nanocomposites usually exhibit a significant enhancement in mechanical, optical, conductive, nonlinear optical and barrier properties, over the individual components and conventional composites containing simple fillers (Pinnavaia, 1997). 2. Recent Studies and Advances in Polymer-clay Nanocomposites Polymer-clay composites have been studied since 1965 (Blumstein, 1965) (Lagaly and Beneke, 1975). It was not until Toyota researchers developed several nanoscale polymer-clay hybrid composites, however, that polymer-clay nanocomposites have become the subject of significant research efforts (Fukushima and Inagaki, 1987). These studies were based on the dispersion of an (yo-amino acid and alkylammonium exchanged forms of montomorilonite clay into: i) semicrystalline nylon-6 (Fukushima and Inagaki, 1987), (Usuki et al., 1995) ii) amorphous epoxy (Usuki et al., 1989), iii) acrylic resin (U suki et al., 1995(a)), iv) polyimide (Yano et al., 1993), (Lan and Pinnavaia, 1994(a)). At present, there are three major research groups working on polymer-clay nanocomposites. These include Giannelis's group at Cornell University, the Toyota group at Toyota Centgal R&Dl;b_, Inc. Japan, and Pinnavaia's group at Michigan State University. Two different synthetic methods are commonly used to prepare intercalated clay polymer nanocomposites. One procedure involves preformed-polymer-intercalation, where the preformed polymer and clays, respectively, are dissolved and dispersed in a compatible solvent, and then mixed. Water-soluble polymers can be intercalated into clay galleries by this method. Such systems include (i) polyethylene oxide (Ruiz-Hitzky, 1993); (ii) ethylene-vinyl alcohol copolymer (Tohoh, 1992); and (iii) polyvinyl alcohol (Greenland, 1963). Molten polymers can also be intercalated in this way. For example, polystyrene was intercalated into organo-montrnorillonite clays (V aia et al., 1993). The second method is the “in situ” intercalative polymerization procedure. In this procedure, the desired monomers are adsorbed or intercalated into the clay galleries. The intercalated monomers are then polymerized within the clay galleries to form the polymer-clay nanocomposite. This method has been used extensively to modify a number of engineering polymers to include: polyamide (Kato et al., 1979), polymethyl metharcylate (Blumstein, 1965), polyimide (Yano et al., 1993), polyaniline (Mehrotra and Giannelis, 1990), poly(e-caprolactone) (Messersmith and Giannelis, 1993), polyacrylonitrile (Blumstein, 1974), and polyfurfuryl alcohol (Bandosz, 1992). Lan and Pinnavaia (1994) studied the intercalation of a polyarnic acid into the galleries of a series of montrnorillonites and the subsequent conversion of the polyamic acid to polyimide. The results indicated that the polyimide intercalates in large part as a monolayer and the composite exhibits enhanced barrier fihn properties, as judged from C02 permeation measurements. Although face-face clay layer aggregation is extensive, the clay-polyimide hybrid composite films exhibited greatly improved C02 barrier properties at low clay content. Less than 8.0 volume % clay results in nearly a ten-fold decrease in permeability rate. A self-similar or fractal dispersion of the clay platelets in the polyimide matrix may explain the barrier property enhancement. In addition, the incorporation of low loading levels of clay into the polyimide hybrid results in a significant reduction in the permeability of water vapor, oxygen, and ethyl acetate vapor, as compared to the pure polyimide film. The results demonstrated a non-linear dependence of permeability on clay loading. The temperature dependency of the transport process, over the temperature ranges studies, followed well the Arrhenius relationship. Under humidified conditions, the polyimide film showed a loss in barrier property, while the polyimide-clay film showed an enhancement in the barrier properties to ethyl acetate vapor. (Gu, 1997) The morphology or crystallization behavior of nylon 6/montmorillonite nanocomposites has been studied by means of wide-angle x-ray diffractive (WAXD), small-angle laser scattering (SALS), and differential scanning calorimeter (DSC). The nanoplastics of montmorillonite dispersed in the nylon-6 matrix were found to act as a nucleating agent. Surface modification of montmorillonite particles was found to increase adhesion between nylon-6 and montmorillonite, which prohibits the crystallization of nylon, thus leading to an increase in crystallization activation energy. (Li et al., 1997). In order to improve the thermal stability and mechanical properties of polyimides, a series of polyimide/silica composite films, which ranged in silica content up to 45 wt%, were successfully prepared by sol-gel reaction of tetraethoxysilane in the presence of polyarnic acid, a precursor of polyimide. The density, decomposition temperature and modulus increased with increasing silica content. In addition, the linear thermal expansion coefficient of the silica in the composite films decreased, whereas tensile strength and elongation at break displayed a maximum with the change of silicate content. (Chen, et al., 1997). Based on the results of these studies, polymer-clay nanocomposites processing has been developed for the plastics industry. Nanocor Inc., a branch of AMCOL International Corporation, has claimed that their unique, chemically modified clays, when added to polymers, form nanocomposites. Compared to the base polymer, the nanocomposites demonstrate improved heat resistance, as well as enhanced structural and barrier properties. Nanocor has partnered with plastic resin producers and users to develop the special technologies and products suitable for several different polymer types. Targeted applications being considered range from flexible and rigid barrier packaging to structural components for trucks and automobiles. Pilot plant facilities have been established to advance process operations and produce trial quantities of NAN OMER® ’ nano-sized platelets. The initial commercial production of some products was launched in the second half of 1997. Nanocor received its first patent pertaining to the preparation of chemically modified clays and nanocomposites in September 1996. (N anocor web page, 1997) ' NANOMER® is the trademark of Nanocor Inc. Because of their unique properties, polymer-clay hybrids have been considered for a number of applications in both manufacturing and research areas, as reviewed below: 0 Food Packaging In 1997, Triton Systems (Triton Systems, Inc., 1997) proposed an irmovative nanotechnology that would develop an inexpensive, recyclable, and mechanically durable material for a food tray with sufficient barrier properties to provide food with a three-year shelf life. A new generation of polymeric sheet stock material with a high barrier embedded glass structure, capable of being thermoforrned into a retortable food- container, was to be produced. This unique and innovative technology involves embedding a highly elastic barrier glass structure within a polymer sheet stock during extrusion. This single-layered, recyclable food tray can replace the current non-recyclable co-extruded 3-layered tray. A reduction in energy and die costs may also be realized because of the use of a single extruder for processing of the single-layered tray. This technology has tremendous potential as a high gas and moisture barrier material in food packaging applications in the form of rigid and semi-rigid food containers, as well as flexible pouches. Other applications include airplane interiors, brakes, tires, fuel yanks, components in electrical and electronic parts, and under-the-hood structural components. Replacement of current filled-polymer systems in automobiles, and airplanes offers tremendous potential. 10 o Multi-chip Packaging Material Polyimides are widely used for microelectronics because of their heat resistance, chemical stability, and superior electric properties. However, it would be desirable to reduce the cost and dielectric constant of the polyimide employed. Kim (1997) reported that a silica-polyimide hybrid could improve the electric properties and reduce the cost of the pure polyimide fihn. The structure of silica-polyimide composites, prepared as thin films, was studied by small-angle x-ray scattering and microscopy. Nanometer—scale composites were successfully obtained from S 30% tetraethoxysilane-loaded mixtures with poly (amic diethyl ester) and poly (amic acid). The microstructure of the composite films, based on poly (amic diethyl ester) was not significantly affected by the inorganic particles, i.e., the structure of the homo-polyimide was maintained, while those based on poly (amic acid) showed changes in structure due to the growth of nanoparticles in situ during the sol-gel process. 11 0 Electronic Industries M (1997) reported that nanocomposites of vanadium pentoxide (V205) aerogel and conducting polymers have applications in the preparation of high performance intercalation materials for rechargeable lithium batteries. Vanadium pentoxide (V 205) has been proposed as a cathode material in electric energy storage batteries, due to its high electrode potential and capacity. Aerogels of V205 (ARG) are materials characterized by high porosity with a solid phase thickness in the nanometer scale (10 ~ 50 nm). They were shown to be almost free of lithium diffusion limitation during the electrochemical insertion and release processes, because of the very short diffusion length of the intercalate cation in the V205 solid phase. Using a conducting polymer with a nanometer size structure was found to help enhance the electronic conductivity of the ARG. The addition of a nanometer thick conducting polymer layer covering to the vanadium penetrates covered structure, provides electronic conductivity throughout the ARG particle without loosing the merits of ARG. In this case, the polypyrrole coating exhibits electronic conductivity with ionic transparency. The resultant ARG-Polypyrrole nanocomposite material showed improved electrochemical performances compared to the bare ARG. 12 0 Automobile industries The Toyota researchers reported that the nylon-6-clay nanocomposites exhibited mechanical and thermal properties which were remarkably superior to those of the individual components. At a loading of 5.0wt% exfoliated clay, the tensile strength of the composite increased by 50% and the heat distortion temperature increased from 65 °C to 152 °C (Fukushima and Inagaki, 1987). Transmission Election Microscopy studies revealed that the improved performance observed was due to the formation of a nanoscopic composite. The nanocomposite immediately found application in the automobile industry, as the structural material of bumpers (Okada et al., 1990). According to a recent report (U suki et al., 1995), it was found that a nylon 6-clay hybrid using montmorillonite was superior to the other types of clay minerals in mechanical properties. This was attributed to the montmorillonite interacting strongly with nylon 6 by ionic interaction. 13 0 Material Industries To evaluate the feasibility of controlling polymer flammability via a nanocomposite approach, Gilman et. al. (1997) have examined the flammability properties of nylon-6 clay-nanocomposites. The fire retardant (FR) properties of this new class of materials, organic-inorganic nanocomposites, were reported by the authors. The cone calorimeter data showed that the peak heatrelease rate (HRR), the most important parameter for predicting fire hazard, is reduced by 63 percent in a nylon-6 clay-nanocomposite containing a clay mass fraction of only five percent, as compared to the simple polyanride. Not only is this a very efficient FR system, but, it does not have the usual drawbacks associated with other FR additives. That is, the physical properties are not degraded by the additive (clay), instead they are greatly improved. Furthermore, this system does not increase the carbon monoxide or soot produced during the combustion, as many commercial fire retardants do. The nanocomposite structure appears to enhance the performance of the char through reinforcement of the char layer. Indeed, transmission. electron microscopy (TEM) of a section of the combustion char from the nylon-6 clay- nanocomposite (five percent) shows a multilayered silicate structure. This layer may act as an insulator and a mass transport barrier slowing the escape of the volatile products generated as the nylon-6 decomposes. 14 3. The Banier Improvement of Polyimide-clay Nanocomposites Polyimides which exhibit excellent thermal, chemical and mechanical durability have attracted much attention for their potential use in gas separation processes. When montmorillonite was intercalated with the ammonium salt of 12-aminododecanoic acid, it dispersed at the molecular level into the polyimide matrix. Due to this unique structure, this polyimide hybrid exhibited high strength, high modulus, low thermal expansion coefficient and a low permeability coefficient. Only 2 wt % addition of montmorillonite reduced gas (water, 02) permeability values to less than half of that of the non-clay loaded polyimide. (Okamoto et al. 1992) Polyimides also have electronic, composite and adhesive applications. In these applications, it would be desirable to increase their moisture and organic vapor barrier properties and dielectric constant, since these properties of polyimides are not sufficient for advanced electronics use. As montmorillonite is composed of stacked silicate sheets, it has high gas barrier properties. Therefore, this polyimide-clay nanocomposite would be expected to exhibit enhanced barrier properties. Montrnorillonite is one of the clay minerals whose size is about 2000 A in length and 10 A in thickness. Recent studies evaluated the effect of the size of clay minerals on the barrier properties of the resultant polyimide-clay nanocomposites (Yano, 1997). Four different sizes of clay minerals were synthesized and compared. These clays consisted of stacked silicate sheets of about 460 A (hectrite), 1650 A (saponite), 2180 A 15 (montmorillonite), and 12300 A (synthetic mica), respectively in length and 10 A in thickness. Yano (1997) found that the longer the length of the clay platelet, the more effectively the barrier properties of the polyimide were improved. In the case of the polyimide-mica hybrid, only 2 wt % addition of synthetic mica reduced the permeability coefficient of water vapor to a value less than one-tenth of that of ordinary unfilled polyimide. The earliest studies on the barrier properties of polyimide-clay nanocomposites were carried out by the Toyota group (F ukushimaand and Inaganki, 1987, 1988). They found that the addition of only 2 wt% montmorillonite, reduced the permeability coefficients of various gases to values less than half of those of the ordinary unfilled polyimide (Yano, 1993). Furthermore, it has been suggested that nearly complete dispersion of the IO-A-thick clay layer is needed to optimize the aspect ratio of the filler (the aspect ratio is defined as the ratio of the length of a face of a filler plate to the thickness of the filler plate), which in the case of montmorillonite can reach a value of 200 (Yano, 1993). Lan and Pinnavaia (1994) showed that similar composites, with an aspect ratio of 192, had enhanced C02 barrier properties. To describe the mechanism of the barrier property enhancement of polyimide-clay nanocomposites, Lan and Pinnavaia (1994) compared the structural difference between exfoliated and intercalated polyimide- clay hybrids. In the exfoliated structure, the single clay layers act as filler elements. The aspect ratio of the individual clay plates and the filler loading were found to determine the barrier property improvement. And for the intercalated structure, the clay fractal aggregates, and not single layers, function as filler elements. The formation of the fractal I6 clay structure for natural clay minerals is due to a water swelling effect. When water molecules have been pre-intercalated into the clay galleries and then evaporated from the system, they tend to form a water domain region. This causes the clay layers to slip and change their stacking pattern from turbostratic to a staircase fashion. During the synthesis of the polyimide-clay nanocomposites, a rearrangement of the clay stacking occurs to form the fractal structure of the clay within the polyamic acid matrix during the pre-intercalation process. After firrther heating, the clay fractal structure will simply remain because of the low mobility of the preformed polymer chains. While various researchers have proposed different mechanisms to account for the barrier property enhancement of polyimide-clay nanocomposites, the observed non-linear dependence of the diffusion coefficients as a function of clay loading and the very low content of the inorganic phase, is crucial in developing light-weight composites of enhanced barrier properties. In an earlier study, Gu (1997) determined the permeability of water vapor, oxygen, carbon dioxide, and ethyl acetate vapor through the same polyimide-clay nanocomposite films. These permeability values were determined with the MOCON Permatran-W, 0x-Tran 200, Permatran C-IV, and the Aromatran 1A permeability test systems, respectively. Gu (1997) found that the mass transfer process for the respective penetrants, i.e. water, C02 and 02, is highly dependent on the clay loading level and exhibited a non-linear dependency with the respect to the decrease in permeability. With a clay loading level of 2.5 % (v/v), the permeability coefficients to H20, 02 and C02 17 were reduced to 39 %, 47 % and 54 % of the permeability value of the pure polyimide film, while the permeability coefficients of the 5% (v/v) clay loading film were deceased by nearly 70 %, when compared to the single polyimide. Gu (1997) also found that the temperature dependency of the oxygen transport process followed well the Arrhenius relationship, over the testing range evaluated (0 °C - 30 °C). The obtained activation energies for the pure polyimide and the 2.5 % v/v polyimide-clay film were 16.9 KJol/mol and 19.6 KJol/mol, respectively. Furthermore, when ethyl acetate vapor was evaluated as a penetrant, the following results were obtained. a) The 2.5 % v/v polyimide-clay nanocomposite film under dry conditions showed an 85 % reduction in the permeability coefficient, as compared to the polyimide fihn without clay loading. b) Within the test temperature range from 15 °C to 30 °C, the effect of temperature on the permeability coefficient is minimal. Less than 3200 Pa ethyl acetate vapor pressure, the activation energies for the pure polyimide and the 2.5 % v/vpolyimide-clay film are 7.1 KJol/mol and 4.1 KJol/mol, respectively. c) Over an ethyl acetate vapor pressure range from 1700 Pa to 3200 Pa, the permeability coefficient appeared to be independent of vapor concentration. There was no indicated effect of penetrant vapor pressure on the activation energies for the polyimide-clay composite film, while the activation energy of the pure polyimide showed a minimal dependency on penetrant concentration. d) When water vapor (50% RH) was introduced to the test system, the permeability coefficient value of the pure polyimide film doubled as compared to that obtained under dry conditions. However, the permeability coefficient for the polyimide clay nanocomposite (2.5 % v/v) film under humidified conditions showed a decrease of approximately 50 % when compared to permeability coefficient obtained under dry conditions. 18 Ideal Diffusion and Sorption of Organic Vapor in Glassy Polymers Diffusion is the net transport of matter in a system, by means of random molecular motion. This results in the removal of chemical potential differences in a system and eventually produces a uniform state of equilibrium, if the boundary conditions are not held constant for a permeation experiment. (Hopfenberg and Stannett, 1973) Frequently the rate of diffusion (J) is proportional to the concentration gradient, although the proportionality constant, known as the diffusion coefficient, may be a function of the diffusant concentration in the polymer: J = 43¢);— (1) This is Fick’s first law of diffusion and it has been found experimentally to represent diffusion in many systems. Based on Fick's first law, for vapors above their critical temperature, the diffusion coefficient is independent of penetrant concentration. Fick’s second law may be derived from Fick’s first law: dc 6 6c 97-3;[D(C)5;) (2) When the boundary conditions are fixed, such that a steady-state diffusion flux is maintained, equation (1) can be used to calculate the steady state permeability, defined as the flux per unit pressure gradient across a polymer membrane of unit thickness; assuming Henry's law to describe the gas-membrane equilibrium. Henry's law simply states that the concentration of penetrant in the polymer, C, is directly proportional to the gas partial pressure, p, to which the polymer is exposed: C=Sp (3) The relationship between the permeability, diffusion, and solubility coefficients can be described by: P D S ( 4 ) where P is the steady state permeability coefficient, cc[STP] - m/m2 . pa 2 sec D is the concentration independence diffusion coefficient, mz/sec C is the solubility of vapor absorbed in the polymer or concentration of vapor in the polymer, cc[STP]/cc polymer S is the solubility coefficient, cc[STP]/cc - pa'l p is the vapor partial pressure, pa Strictly idealized behavior results not only from Fickian diffusion but also additionally from a Henry's law description of solution. 20 Non-ideal Sorption and Diffusion of Organic Vapor in the Glassy Polymers The magnitude of the negative enthalpies of sorption of organic vapors by polymers reported by Barrer (1957) were inconsistent with the sorption theories of Henry's law and led Barrer to suggest a dual-mode, concurrent sorption mechanism for glassy polymers, namely ordinary dissolution and 'hole' filling. Michaels et a1. (1963) also reported and proposed that a two-mode sorption model of ordinary dissolution and adsorption in microvoids ("holes") for gas sorption in glassy amorphous polymers. The authors (Michaels et al., 1963) assumed that the total concentration of the sorbate in the polymer, C, consisted of two thermodynamically distinct molecular populations; molecules 'adsorbed' in the 'holes' or microvoids, CH, and molecules dissolved in the amorphous polymer matrix, CD, as shown in equation (5): C = CH + CD (5 ) The concentration Cy was described by a Langmuir isotherm: C H bp C =——— 6 H 1+bp () and the concentration C D by Henry's law: 21 where C 'H = hole saturation constant cc[STP]/cc polymer b = hole affinity constant (pa '1) p = vapor partial pressure (pa) k0 = Henry's law constant for dissolution in the amorphous matrix, cc[STP]/cc - pa" The equilibrium concentration for the "dual mode sorption model" can be described by: C=C..+C..=C”"p +k..p (8) 1+bp This model was applied by Okamoto et al.(l992) to the sorption isotherm of water vapor by a polyimide film and gave an excellent fit of water vapor sorption by the glassy, amorphous polymer. The isotherm for this sorbate/polymer sorption was described by the following expression: __ 0.01356 p 1+2.26 x10‘3p +6.32 x10-3p (9) It is instructive to show the two limiting cases from the dual mode sorption model. At low partial pressure (b p<>1 which reduces the equation (8) to: C=Cp+gp am At sufficiently high pressure the term C 'H/ p becomes negligible as compared to kD, therefore indicting that the available 'holes' have become saturated and that ordinary dissolution dominates. Later investigations by Vieth et a1. (1966) on glassy polymers indicted that the gas molecules are sorbed in the "hole" site, only as monolayers. The dual-mode sorption model therefore predicts that an isothermal plot of C versus p will consist of a low-pressure linear region and a high-pressure linear region connected by a nonlinear region. So, kD can be obtained from the slope of the sorption isotherm at high pressures. By subtracting the solubility of the normally dissolved gas, CD, from the total solubility C, the solubility of the sorbate in the microvoids, Cy, can be calculated at each partial pressure: CH=C-CD=C—kpp (13) 23 Once CH as a fimction of p has been detemrined, it can be tested in terms of the assumed Langmuir model: CH=C,pr/(I+bp) (14) Equation (14) can be rearranged to: p 1 p. (15) Therefore, to test whether a single Langmuir expression fits the data for the hole-fitting process a least-mean-squares plot of p/CH versus p is made and is checked for linearity. The constants C ’H , and b can be determined from the slope and y-intercept of such a Langmuir plot. 24 Model for the path of a diffusing gas through the polyimide/clay nanocomposite The significant reduction of the permeability coefficients of the polyimide-clay nanocomposite films, as compared to the non-clay loading control, was explained by the increase of the total path of the diffusing gas through the structure. As clay is composed of stacked silicate sheets, it exhibits high gas barrier properties. The diffusing gas has to go along the length of the clay instead of the width, which is a hundred time less than lengthwise. Therefore, the total path of the diffusing gas will increase. If a plate of length L and thickness W is dispersed parallel in a polymer matrix, the tortuosity model for the path of a diffusing gas through the polyimide clay nanocomposite is shown by Figure 2 (Nielsen, 1967): For montmorillonite, length of a clay L = ~ 2000 A, width of a clay W = 10 A. The value of L was determined from transmission electron micrograph (TEM) (Yano et a1,1993) ‘ i. ................. 1:3; dd’ 'w HL>I E:::I Figure 2 A model for the path of a diffusing gas through the polyimide clay nanocomposite. 25 Total path of a diffusing gas d'=d+dLVf/2W (16) where d is the thickness of a test film and VfiS the volume fraction of a clay. Tortuositv factor t=d'/d =1 +(L/2W) vf (17) where Vf represents a volume fraction of a clay plate. The permeability coefficient ratio is given by: P, 1_ 1 P r 1+(L/2W)vj P (18) where PC and Pp are a permeability coefficient of composite and polymer matrix, respectively. According to the equation above, the permeability coefficient ratio should be smaller as aspect ratio (ratio of length versus width) of plate becomes bigger. 26 Materials and Methods Materials for synthesis of clay/polyimide Nanocomposite Natural montmorillonite Source clay mineral Depository University of Missouri, Columbia, Missouri Unit 06112 Naose [Mg086 A1514 (Si 8.00) 020 (OH)4] 4, 4' - diaminodiphenylether (4, 4' - ODA) Aldrich Chemical Co. (Milwaukee, WI) Molecular Weight: 200.24 Melting point: 190-192 °C Purity: 99% Pyromellitic Dianhydride (PMDA) Chriskev Company, Inc. (Leawood, KS) Molecular Weight: 218.12 Melting Point: 286.7 °C Purity: 99 % Dimethylacetarnide (DMAC) Aldrich Chemical Co. (Milwaukee, WI) Molecular Weight: 87.12 Melting Point: - 20 °C Boiling Point: 164 ~ 166 OC Purity: 95 % Octadecylarnine (18 A) Aldrich Chemical Co. (Milwaukee, WI) Molecular Weight: 269.52 Melting Point: 55 ~ 57 °C Purity: 99 % 27 Materials for Sorption tests Ethyl acetate (CH3-C00-C2H5) J. T. Baker Chemical Co. (Phillipsburg, NJ) Analytical Reagent grade Molecular Weight: 88.11 Boiling Point: 77.2 i 0.5 °C Purity: 99.9 % Ethylene Glycol (H0-CH2-CH2-0H) J. T. Baker Chemical Co. (Phillipsburg, NJ) Laboratory grade Molecular Weight: 67.07 Boiling Point: 197 i 0.5 °C Purity: 100 % Acetonitrile (used as a solvent when preparing standard solutions for construction of an ethyl acetate calibration curve) EM Science, Gibbstown, NJ Laboratory grade Molecular weight: 41.05 Boiling point: 81.2 i 0.5 °C Purity: 99.8 % Nitrogen gas (carrier gas of the sorbate vapor) AGA Gas, Inc., Cleveland OH Dry grade nitrogen: 99.98% 28 C. Synthesis of Clay-Polyimide Nanocomposite Film In the present study, montmorillonite/polyimide nanocomposites were prepared in a two step process involving condensation polymerization, followed by a cyclodehydration reaction, as described by Lan (1994). A flow chart of the synthesis of the polyimide-clay nanocomposites is depicted in Figure 3. Polyamic acid was synthesized by the condensation reaction between 4,4'- diaminodiphenylether and pyromellitic dianhydride in dimethyl acetamide (DMAC). An amount of pyromellitic dianhydride was slowly added to the 4,4'-diarninodiphenylether/ DMAC solution with vigorous stirring at 15 - 20 °C and kept stirring for 1 hr at room temperature. The final polyamic acid solution has a concentration of 7 wt%. Polyamic acid-clay intercalates were prepared by reaction of the desired organoclay (2 -10 wt%) with the polyamic acid solution at 25°C. The clay suspension, in polyamic acid/ DMAC solution, was then vigorous stirred for 24 hrs, followed by a 2hr settle down period. Allowing the polyamic-organoclay suspensions to dry on a clean glass plate yielded self-supporting films. The air-dried polyamic acid-clay films were heated at 1°C/min to 300 °C and kept at 300 °C for 3 hrs to form the cured polyimide-clay hybrid composites. 29 4,4'-Diaminodiphenylether DMAC < Pyromellitic dianhydride L Polymerization I l Poly (amic acid) solution 1 Mixing Organoclay (2 ~ 10 wt %) Poly(amic, acid) film 1 Heating 300 °c 3hr | l Polyimide clay nanocomposite/Hm I Figure 3 Synthesis of polyimide clay hybrid. 30 D. Cahn 2000 Electrobalance Sorption experiments conducted using the gravimetric technique are usually carried out at equilibrium vapor pressure and employ an apparatus that continuously records the weight gain or loss of a polymer sample as a function time. A recording electrobalance, such as the Cahn 2000, is commonly used for such studies. The Cahn 2000 is a very sensitive weighting instrument and is designed to measure weights up to 3.5g. It has a 0.01mg resolution and a 0.02mg precision, for a measuring scale of 100.00mg. The electrobalance can be described as a torque-to-current converter. The apparatus consists of a balance beam mounted to, supported by and pivoting about the center of a taut ribbon; a torque motor coil, located in a permanent magnetic field and also mounted to the taut ribbon; sample suspension fixtures; a beam position sensor system; and controls, circuitry and indicators. When conducting a sorption measurement by the continuous flow method, the polymer sample is suspended from the arm of the electrobalance, and a sorbate of constant concentration is continuously flowed through the sample hangdown tube. The sorbate vapor is produced by bubbling pure nitrogen gas through the liquid sorbate. This can be achieved by constructing a vapor generator system, consisting of an Impinger Bubbler, containing the organic liquid. As the weight of the polymer test sample changes, a torque is produced about the axis of rotation. The electrobalance effectively measures the amount of electric current needed by the torque converter to maintain the 31 balance beam in a level position. By calibrating the electrobalance using calibration weights, the change in electric current can be related to weight change of the polymer sample. By interfacing the electrobalance control unit to a computer, the polymer sample's change in weight can be continuously recorded, as a function of time. 32 E. Gravimetric Sorption Method Sorption studies were conducted on a Cahn 2000 electrobalance (Cahn Instruments, Inc., Cerritos, CA) by the continuous flow method. A schematic of the test system is shown in Figure 4. A polymer sample weighing approximately 25 ~ 60 mg was suspended from the arm of the electrobalance. A sorbate vapor stream of constant concentration was produced by bubbling pure nitrogen gas through the liquid sorbate. This was achieved by constructing a vapor generator system, consisting of an Impringer Bubbler, 824/40, 25ml (Ace Glass Inc. 1430 N West BLVD, Vineland, NJ 08360), which contained the organic liquid. The Impringer Bubbler, or sparger unit, was maintained in a constant temperature control bath (N ESLAB, Endocal RTE-100, Refrigerated Bath/Circulator, Neslab Instruments, Inc. Nevvington, NH) as a means of controlling the vapor pressure of sorbate delivered to the hangdown tube of the electrobalance unit. To provide insight into the concentration dependency of the mass transfer process, seven vapor activity levels were evaluated: 0.15, 0.21, 0.27, 0.34, 0.44, 0.55,0.68. Flow meters (Cole Parmer, Chicago, IL) and needle valves (Nupro 'M' series, Nupro Co., Willoughby, OH) were used to regulate the gas flow and indicated a constant flow rate. The sorbate uptake was continuously recorded with a computer, until steady state was reached. 33 The test gas delivered can be a certified gas or sparging gas. In this study, a sparging gas was used. The organic liquid is added to the sparger, and a carrier gas is passed through the liquid in such a manner so as to obtain a known and stable concentration of the permeant in the test gas stream. The test gas stream is connected directly to the test gas inlet of the hangdown tube. Test gas flows were normally set at 15 cc/min. When the temperature controller bath is set at a specified temperature, the organic liquid inside the sparger generates a fixed and constant saturation vapor pressure at that specific temperature. It is suggested that the sparging system should be maintained at a temperature below ambient so as to insure that there is no condensation in the delivery lines. In this study, the bath was set at temperatures ranging between -10 °C to 16 °C, depending upon the desired vapor activity. The resultant organic vapor partial pressure in the hangdown tube is equal to the saturation vapor pressure generated in the sparger. The conclusion is based on the following reasoning (Hernandez, 1994): The vapor pressure is generated at TA (point A), while the fihn is evaluated within the test system maintained at a higher temperature TB (point B). The parameters of partial pressure, concentration and volume for the organic vapor generator and test conditions are denoted as pA , pB , C A , CB , V A and VB , respectrvely. Assumption: i) At point A and B, the mass flows are equal. 34 Therefore, MA = MB = M, where M is the mass flow (mass/time). ii) The organic vapor pressure is usually low, therefore the mass flow consists primary of nitrogen (N2). For this case, it can therefore be assumed that the organic vapor behaviors as an ideal gas. In follows then, that FB = FA * TB/ TA, and by definition: C = M /F, where F is the gas flow rate (volume / time). So, the concentration ratio is CB /CA = TA / TB When expressing C or p by the ideal gas law, at point A: p=nRT/v=R/MW*m/v*T=R/MW*C*T pB/pA = CB TB/CA TA 1’13 =pA * I/CA TA * CA TA/TB * TB :pA So, at point A and B: o Temperatures are different 0 Mass flows are equal 0 Flow rates are different 0 Partial pressures are equal The composition of the vapor stream was determined by using a high performance, gas tight syringe (Hamilton 1750, Supelco Inc., Bellefonte, PA) to take samples from the sampling port located on the hangdown tube and performing gas chromatography (GC) analysis. All of the gravimetric sorption studies were conducted at a temperature of 23 i 1 °C. 35 SP: Sampling port SP 1 (To GC) Figure 4 oooooooooooooooooooooooo ----------------------- ----------------------- IExhaust meter Schematic of Gravimetric Sorption Experimental 36 F. Gas Chromatographic Analysis Gas chromatographic analyses were performed using a Hewlett-Packard 5890A gas chromatograph, equipped with a dual flame ionization detector and interfaced with a Hewlett-Packard 3395 integrator for quantification (Avondale, PA). The column used in this study was a Supelcowax 10 fused silica capillary column (60m, 0.25mm ID, 0.25 pm fihn thickness) (Supelco Inc., Bellefonte, PA). A detailed summary of the procedure for calibration curve construction is presented below: Materials: 0 25mL and IOOmL volumetric flasks with stoppers - 500uL high performance gas tight syringe o 1 and SmL sterile pipettes with automatic pipette fixtures 0 Lab grade ethyl acetate and acetonitrile Procedure: To determine the relationship between area response and the ethyl acetate quantity injected, a calibration curve was constructed using the following procedure: 37 1. Prepare a 1000ppm (v/v) standard stock solution 3. Using a high performance gas tight syringe, add 0.1mL of ethyl acetate to a 100ml volumetric flask. Fill to 100mL with acetonitrile. Stopper the flask and swirl to ensure proper mixing. From the 1000ppm stock solution, prepare 25mL standard solutions of the following concentrations: 10, 20, 40, and 80ppm (v/v). To the four 25mL volumetric flasks, add 0.25, 0.5, 1.0 and 2.0mL of the 1000ppm stock solution, respectively. Fill to 25mL with acetonitrile. Stopper the flasks and swirl to ensure proper mixing. Using the GC settings presented in Table I, analyze each standard solution by injecting a luL aliquot directly into the gas chromatograph for quantification. Repeat until a consistent response value is obtained for each concentration. 38 Table 1. Gas chromatography conditions used for ethyl acetate quantification Column Supelcowax 10 Injection temperature 220 °C Detector temperature 250 °C Initial temperature 100 00 Initial time 9 min Rate 7.5 °C/min Final temperature 220 °C Final time 15 min He (carrier gas) 7.0 mL/min H2 40 mL/min Air 400 mL/min Nitrogen (make-up gas) 30 mL/min l 4. Plot the average area response value obtained for each concentration as a function of the ethyl acetate quantity injected. The injected quantity of ethyl acetate can be calculated from the following expression: ‘1: = v,xcx0.902 %L (19) Where qi represents the quantity injected, v,- is the injection volume, c is the concentration of the standard solution (v/v), and 0.902 g/mL is the density of ethyl acetate. The ethyl acetate calibration curve is presented in Figure 5: 39 4. OOE +05 3 3.00505 . S 8‘ 2.00505 . 2 G 2 1.00505 . y= 5E+10x < R2 = 0.9951 0.00500 , . 5 0.00500 2.00506 4. 00506 6.00506 8.00506 Quantity Injection (9) Figure 5. Ethyl acetate calibration curve 5. Using linear regression, determine the slope of the standard curve. Take the inverse of this value to obtain the ethyl acetate calibration factor. A calibration curve was constructed to determine the relationship between area response and ethyl acetate quantity injected. Retention times for ethyl acetate and acetonitrile were found to be 7.2 and 8.4 minutes, respectively. In addition, the saturation vapor pressure of ethyl acetate at 23 °C was experimentally determined using gas chromatographic analysis. The following is the method used to calculate the ethyl acetate vapor activity levels employed in this study. 40 Materials - SOOuL gas tight syringe o 50mL crimp seal vials 0 Aluminum crimp cap 0 Teflon coated septa seals 0 5mL sterile pipettes with automatic pipette fixtures 0 Lab grade ethyl acetate Procedure The saturation vapor pressure and the vapor activity of ethyl acetate were experimentally determined using the following procedure: 1. Add IOmL of ethyl acetate to each vial and seal using a Teflon coated septa seal and an aluminum crimp cap. 2. Store the sample at 23 °C for one week, to allow the vial headspace to equilibrate, 3. Using the same GC conditions as the calibration curve in Table 1, determine the ethyl acetate saturation vapor pressure within the headspace by withdrawing a SOuL aliquot and injecting the sample directly into the gas chromatograph for quantification. 41 Determine the ethyl acetate saturation vapor pressure from the ideal gas law: pV=nRT (20) Determine the vapor activity of the ethyl acetate test vapor. Using GC conditions identical to those described above, determine the vapor pressure of the test ethyl acetate vapor by withdrawing a SOuL aliquot from the vapor stream sampling port and injecting the sample directly into the gas chromatograph for quantification. Vapor activity is determined from the following expression: a. = pi/ps (21) where a, represents the vapor activity, p,- is the test vapor partial pressure of ethyl acetate, and p, is the saturation vapor pressure of ethyl acetate. 42 The saturation vapor pressure value obtained from the literature (see appendix A) was 85.7 mmHg at 23 °C. The ethyl acetate vapor activity for the ethyl acetate permeant determined experimentally was compared with the values obtained from the literature (Appendix A) and are summarized in Table 2. The average percent deviation from the experimental was 3.3 % below the values obtained from the literature. The variation between the two procedures can be attributed to a number of factors, such as deviation of the permeant from the ideal gas law at or near the saturation point of the vapor, as well as errors introduced by the gas chromatography procedure and errors involved in the possible condensation in the test system. Table 2. Comparison of the ethyl acetate vapor activity in the hangdown tube obtained by the experimental and literature. Bath System vapor activity System vapor activity Deviation Temperature obtained from literature determined from experimental based on the ( °C) literature data -10 0. 150 ~ 0. l 5 0 % -4 0.21 8 0.21 3.7 % 0 0.284 0.27 4.9 % 4 0.361 0.34 5.8 % 8 0.453 0.44 3.0 % 12 0.566 0.55 2.8 % 16 0.700 0.68 2.9 % 43 G. Calculation of diffusion coefficient When a polymer sample of known shape and size, which is at an initially equilibrium state (uniform penetrant concentration), is suddenly exposed to an atmosphere of constant penetrant vapor pressure, the sample weight changes with time towards the sorption equilibrium value, according to kinetics governed by the penetrants diffusion coefficient. For dense polymeric materials such as polyamides, polyimides and polyethylene terephthalate, surface sorption is generally considered to be negligible, when compared with the sorption levels in the bulk polymer. As polyimide films are quite dense and uniform, a vapor absorption in the bulk materials is assumed. (Perrin et al., 1996) If M, denotes the total amount of the diffusing substance which has entered a flat sheet at time t, and M.o (or M5,), the corresponding quantity after infinite time, the change in the mass of the sample, as a function of time, is given by: (Crank 1975) M — ,,, (2n+1)27r2 w (22) M, °° 8 [-Dn2(2n+1)2t] — 6X 12 where D is the diffusion coefficient (mz/s), 0 the film thickness (m) and t is time (s). This equation is valid when the vapor penetrates bi-directionally in the material with a constant diffusion coefficient from both planer surfaces. If the fihn was bonded to an impermeable substrate (aluminum sheet) or vapor penetrates unidirectionally in the film from one surface, the thickness value in equation (22) is double that of the true sample. 44 As the sample films were thin sheets (thickness less than a hundredth of the width or length), penetrant sorption by the edges was assumed to be negligible, when compared with that by the plane surfaces. In the case of sorption of vapors or condensable gases, the diffirsion may progress locally at different rates due to the dependence of the diffirsion coefficient on the local concentration. The dependence, known as the 'plasticization' effect on the polymer by the penetrant, is caused by an increase in the mobility of polymer segments with the local penetrant concentration. (Perrin et al., 1996) To solve numerically Fick's second law equation, a trial-and-error method is typically employed to fit the experimental kinetics by varying the values of the parameters of the concentration dependence law. The simplest law, the one in which diffusion is Fickian with a constant value for the diffusion coefficient, is tested first. This is based on the assumption that the value of the diffusion coefficient can be calculated by different approximation methods, such as the method of half-sorption time t1/2, or by a method using a transform of equation (22), with only the first term of the series. Nevertheless, with such methods, it is not possible to check the validity of the assumption of a constant difiusion coefficient. In this study, equation (22) was used for the fitting of the entire curve by the "Least square curve fitting method". A statistical treatment of the data [[(Mcalc, - Mcxp. )2] showed that the total departure of the calculated from the experimental values should be minimized in order to obtain a good fit of the experimental data. 45 1) luv/A'mmmu)0"99¢nflfl "half sorption time" method Diffusion coefficient values, D, can be estimated using the following expression derived by Ziegel (1969): D = 0.049 — (23) tl/Z 0n the assumption that the diffusion process followed Fickian sorption behavior, this equation can only be used when there is a good agreement between the experimental and theoretical sorption profiles. Estimation of t1/2 is illustrated in Figure 6 for the penetrant/polymer system of ethyl acetate (3 = 0.68) and the non- clay loading polyimide film. 1.25 4 120 150 180 Time (houn Figure 6 Half sorption time determined by sorption profile of 0.675mil non- clay polyimide film at ethyl acetate vapor activity a = 0.68 and T = 23 °C. (t1/2 = 15.3 hours, D = 2.58 x 10 '16 mz/sec) 46 2) Gauss-Newton curve fitting method Equation (22) can be used for fitting the entire sorption curve, based on the "Gauss-Newton curve fitting" method. In this procedure, diffusion coefficient values are selected and for each selected D value, a value of M, is calculated from Equation (22) for each data point (11) on the sorption curve. Statistical treatment of the data [[(Mcmc. - Mcxp, )2 /((Mc,,.c,)2 . n)] showed the average relative departure of the calculated values from the experimental values. The best estimated D values can be determined by the least sum of the {[(Mcm, - Map, )2 /((M,,,,k,_)2 . n)]. A value less than 1% is considered to be a likely good fit of the data to the theoretical equation (Penin, 1996). A typical plot of the statistical treatment of the data ZKMcarc. - Mexp, )2 /((Mc,uc)2 . n)] is presented in Figure 7, where the sum of X[(Mca.c, - Mexp, )2 /((Mc,.c,)2 . n)] is plotted as a function of selected diffusion coefficient values. Here the diffusion coefficient giving the lowest value of [[(Mcarc. - Mexp, )2 /((Mc,,.c.)2 . n)] is assumed to give the best fit of the experimental data to Equation (22). 47 0.12 0.11 .L 0.1 .. 0.09 .. V 0.08 -. 0.07 a 0.06 1. sum 0f (M exp ' "only, (Meal2 ' n) 0.05 , , , , 0.00500 1.00516 2.00E—16 3.00516 4.00516 5.00516 Diffusion Coefficient (m’Isec) Figure 7. £[(Mcalc. — Mex, )2 /((Mc,,)c_)2 . n)] as a function of the best estimated diffusion coefficient value for the system of 0.675mi1 non-clay polyimide film at ethyl acetate vapor activity a = 0.68 and T = 23 °C. (D best = 2.8 x 10 '16 m2/sec) 48 3) Least square method Equation (22) can also be used for fitting the entire sorption curve, based on the least square method. For the least square curve fitting method, diffusion coefficient values are selected and for each diffusion coefficient value selected, values of M, are calculated by solution of Equation (22). Statistical treatment of the data [[(Mcalc, - Map, )2] shows the total departure of the calculated values from the experimental values. The best estimated D value is determined from the minimum sum of the squares value, which is considered to be the likely best fit. A typical graphical treatment is presented in Figure 8, where the sum of squares is plotted as a function of the selected diffusion coefficient values. 1.8 E 1.6 a 3 "6 :5, 1.2 (D 1 . 0.8 0.00E+00 1.00516 2.00516 3.00516 4.00516 5.00516 6.00516 Diffusion coefficient (mzlsec) Figure 8. [[(ch, - Map) 2] as a function of the best estimated diffusion coefficient value for the system of 0.67 5mil non-clay polyimide film at ethyl acetate vapor activity a = 0.68 and T = 23 °C. (D best = 3.2 x 10 '16 mz/sec) 49 4) "Consistency for continuous flow" method The consistency test for continuous flow permeability experimental data has been described in detail by Gavara and Hernandez (1993) and is summarized briefly below. The permeation rate or permeant flux at any time F. during the transient state portion of the permeability experiment, varies from zero at time zero, up to the value F.o reached at steady state. This is described by the following expression 2 w _ 22 5’_= 4 J 1 exp n 1 (24) Fan J7? 4D! n=1.3.5... 4D! , where F(/F.o is the permeant flux ratio. F t is the permeant flux at time t, and F... is (24): the permeant flux at steady state. In this equation, D is assumed to be time and concentration independent. For short times, the first term of the convergent series in Equation (24) gives a good description of the permeation process from t = 0 up to the time when 95% of the steady-state flow has been reached. Equation (24) is then simplified to read: (J?) 6... (25) 50 1 where (0 represents Ft/Fm in Equation (25) and X = 122/4Dt . By using a Newton- Raphson method, the value of X can be calculated for each value of t and the diffusion coefficient D can be obtained from the slope of 1/X versus t. The plot of I/X versus time is expected to be a straight line and to intercept the ordinate axis at zero. This is illustrated in Figure 9 for the ethyl acetate (a = 0.68) / non- clay loading polyimide film system. 1.600 1.400 .. 1.200 _ 1.000 . 0.600 . 0.400 _ 0.200 - 0.000 , , . . - 0 5 10 15 20 25 30 35 40 45 Time (hour) Figure 9 The " I/X versus time" plot of 0.675mil non-clay polyimide film at ethyl acetate vapor activity a = 0.68 and T = 23 0C. (Slope = 0.0329, R2 = 0.965, D = 6.6 x 10 "6 mZ/sec) 51 H. Calculation of solubility coefficient The solubility coefficient (S) is usually determined by observing the change in weight of a polymer sample during a sorption process. Such a process can involve the absorption or desorption of low molecular weight moieties by the polymer sample. To relate the concentration of the penetrant (C) in the polymer to the penetrant concentration in the gas or vapor phase in equilibrium with the polymer, Henry's law is assumed: C = S p (3) where p is the partial pressure of the penetrant in the gas phase. The partial pressure of the penetrant is further related to the penetrant concentration in the gas phase through the ideal gas law. As discussed in the Results and Discussion section (see page 65), the ethyl acetate sorption isotherm, assumes a dual-mode sorption model of ordinary dissolution and adsorption into the microvoids ("hole") for vapor sorption in the glassy amorphous polyimides. The sorption isotherm for this polymer was accurately described by the dual-mode sorption model (Equation 8). C'b C=CH+CD=i—+%+kbp (8) 52 ll From the isotherm, the changes in the vapor partial pressure are not consistent with the changes in the solubility values. If the Henry's law component contributes only a portion of the ethyl acetate uptake described by the sorption model, the solubility coefficient (S) will be given by: EC = CHb 2 +ko 6p (1+bp) S = (26) Solving Equation (26) thus gives the tangent value of the sorption isotherm at each vapor partial pressure. The S values determined by this procedure, show how the vapor partial pressure affects the solubility values. 53 I. Calculation of parameters of dual-mode sorption methods Calculation of the sorption parameters C 'H, [(0, b from the sorption isotherm data was carried out as following: C=CH+kDp (27) This form of equation (27) indicates that a quantitative separation of the sorption contributions is possible at high partial pressures, assuming the dual mode sorption model adequately describes the data. Since the expression is in a linear form, a plot of C as a function of p give a slope equal to kg and the y-intercept equal to C 'H . After kn has been determined from the slope of the best straight lines through the high partial pressure data, the 'hole' contribution, C”, for each vapor pressure can be determined by subtracting kD p fromC. CH=C—kDp (28) Also the expression for C” can be rearranged to the form; 1’: 1+le (29) 54 Then the Langmuir plot, p/CH versus p, should yield a straight line of slope 1/C'H and intercept at (p = 0) of l/C'Hb. This procedure, as in most procedures involving curve fitting of the data, is of a trial and error nature and it is continued until the best (least mean-squares) fit of the data on the Langmuir plot is achieved. This procedure is illustrated in Figure 10 & 11. Sorption lsotherm SIOPC=KD C (cc[STP]/cc polymer) 0 a 8 8 8 8 8 —I 0 2000 4000 6000 I 8000 10000 Vapor partial pressure, p (pa) , Figure 10. Determining the Henry's law constant by dual-mode sorption model Langmuir Plot 0.35 0.3 . 0.25 _ 0.2 _ 0.15 - 0.1 - 0.05 _ P/CH slope = l/C 'H y-intercept = l/b C'” 0 2000 4000 6000 8000 10000 Vapor partial pressure, p (pa) Figure 11. Determining parameters by Langmuir Plot 55 Results and Discussion Sorption Properties 1. Equilibrium Solubility for Ethyl Acetate Organic Vapor The solubility at equilibrium of ethyl acetate in a polyimide film was obtained from the weight gain of the sample at long sorption times, where weight gain is determined at steady state. A representative plot of Mt/ M55, as a function of time, for the sorption of ethyl acetate by the non-clay polyimide film, is presented in Figure 12. The theoretical sorption curve obtained by solution of Equation 22 is superimposed for comparison. -D7r2(2n+1)2t] (22) M °° 8 ' =1- ex M, giannfnz p[ 12 The sorption behavior of clay-loading polyimide film (2.5 v/v%) is illustrated in Figure 13 and is representative of the sorption profile curves obtained for the respective clay/polyimide composites studied. The theoretical sorption curve for the clay/polyimide film is also presented in Figure 13 for comparison. 56 1.2 0.8 - 0.6 . 0.4 . M 1’" cs (mm/(m9) Figure 12 . Experimental (mg/mg) — Theoretical (mg/mg) 50 100 150 200 250 Time (hour) A representation plot of M,/ M55 as a function of time, for the sorption of ethyl acetate by the non-clay polyimide film. (av = 0.68) 1.2 1.0 - 0.8 4 0.6 . 0.4 . M , m“ (mg/mg) 0.2 . 0.0 Figure 13 O. 0 Experimental (mg/mg) —— Theoretical (mg/mg) 50 100 150 200 250 300 350 400 Tlme (hour) A representation plot of Mt/ Ms, as a function of time, for the sorption of ethyl acetate by the 2.5 v% polyimide-clay film. (av = 0.68) 57 It can be seen that the theoretical curve lacks a good fit to the experimental data, and as shown, the initial portion of the experimental data is approximated by a straight line. The lack of good agreement between the experimental and calculated sorption data can be explained by the fact that a calculated D value can not accurately account for the whole sorption kinetics in the limited range of diffusion coefficient variations. The equilibrium solubility values (C) and the time values to equilibrium (tss) determined for ethyl acetate in non-clay and clay loaded polyimide composites ranging from 1.25 % to 5% (v/v) are summarized in Table 3 and Table 4, respectively. As shown, while the sorption time to equilibrium varied dramatically as a function of clay loading, the equilibrium solubility of ethyl acetate in the unfilled polyimide and clay/polyimide composite membranes was relatively constant at the respective vapor activity levels studied. It can be concluded that the polymer matrix and clay filler have similar organic vapor absorption properties, and the clay has neither a synergetic or antagonistic effect on the solubility of organic vapor in the polyimide matrix. Table 3 Vapor activity dependence of solubility values in polyimide-clay nanocomposites (23 i 1 0C) Ethyl acetate 0 v% clay a 1.25 v% clay 2.50 v% clay 5.0 v% clay vapor activity Polyimide film Polyimide film Polyimide film Polyimide film (mg/mg polymer) (mg/mg polymer) (mg/mg polymer) (mg/mg polymer) 0.68 0.141 21:0.002 0.130 0.124 0.116 0.55 0.126 :t0.004 0.120 0.1 15 0.44 0. 112 i0.002 0.108 0. 104 0.34 0.101 $0.001 0.096 0.27 0.091 :t0.002 0.082 0.21 0.082 2120.002 0.15 0.067 i0.002 ‘1 Solubility values are the average of at least two sorption tests. 58 Table 4 clay nanocomposites (23 i 1 °C, 1mil film thickness) Variation in normalized sorption time (t,,) to equilibrium in polyimide- Ethyl acetate 0 v% clay 1.25 v% clay 2.50 v% clay 5.0 v% clay vapor activity Polyimide film Polyimide film Polyimide film Polyimide film (hours) (hours) (hours) (hours) 0.68 188 255 313 509 0.55 369 457 788 0.44 569 787 1089 0.34 700 1667 0.27 957 2034 0.21 1 108 0.15 1358 * The time value to equilibrium (t,,) is calculated by the time value which is equal to 6 times of t1/2 (half-sorption time value). The sorption capacity of the organo-clay inclusion was also determined and compared to the solubility of ethyl acetate in the non-clay loading polyirrride membrane. The results are summarized in Table 5. As shown, the clay filler and the polymer matrix exhibit comparable sorption properties for ethyl acetate vapor. Table 5 Equilibrium solubility values (mg/mg sorbant) of clay powder and unfilled polyimide film. Ethyl acetate vapor activity 0.68 0.44 0.27 Clay powder 0.131 0.082 0.055 Original polyimide 0. 141 0. 1 12 0.09 1 With regard to the equilibrium solubility determined for the respective clay/polyimide hybrid membrane, it can be assumed that the solubility value is the sum of the polymer equilibrium solubility value and the clay inclusion solubility value. 59 Equation 30 can therefore be used to estimate the solubility values of the clay loading polyimide nanocomposites. 6,... =(1-Mf)Cp+Mch (30) where M; is the weight fraction of the clay inclusion in the composite. In this case, the weight fraction of the clay is equal to two times the volume fraction of the clay (Vf). Cp and Cc are the solubility values of the non-clay polymer and the clay powder itself, respectively. Estimated values for the equilibrium solubility of ethyl acetate in the 1.25% (v/v) clay/polyimide hybrid are summarized in Table 6. The determined solubility values are also listed for comparison. As shown, good agreement was obtained between the experimental and calculated solubility values. This is also shown graphically in Figure 14, when calculated and experimental solubility values are compared for the 1.25 v/v% clay/polyimide composite at selected ethyl acetate activity levels. Table 6 Comparison of experimental and calculated absorption properties of a polyimide clay hybrid as a function of ethyl acetate vapor activity w a = 0.68 a = 0.44 a = 0.27 Solubility (wt/wt sorbant) Cp Polyimide 0.141 0.1 12 0.091 Cc Clay powder 0.131 0.082 0.055 chp 1.25 v% polyimide-clay hybrid 0.130 0.108 0.082 Cest 1.25 v% clay + 98.75 v% polyimide 0.141 0.110 0.090 60 3 E 1 § I B .5. o“ 2 '1' z. I Experimental 1 g DEstimated . 2 o m a = 0.44 a = 0.27 Vapor activity , pip, Figure 14 Solubility values comparison for the 1.25 v/v% clay-loading polyimide composite, between the experimental and calculated values. 61 2. Solubility coefficient The equilibrium solubility coefficient values (S) determined for the respective polyimide-clay nanocomposites membranes are summarized in Table 7. The S values reported were determined by the tangent methods, as discussed in the Materials and Methods section. Typical plots of the calculated solubility coefficient (S) as a function of ethyl acetate vapor pressure for the non-clay loading and clay-loading (1.25 % v/v) polyimide membrane are presented in Figures 15 and 16, respectively. As shown, with increasing vapor activity, the solubility coefficient (S) decreases and approaches a constant at high activity levels (i.e. av > 0.5). The Henry's law constant, k0, would be the lower limit of the solubility coefficient. Table 7 The calculated solubility coefficients S (cc [STP]/cc . pa") for the non- clay and 1.25 % v/v polyimide clay nanocompOsites. Vapor Vapor partial Solubility coefficient Solubility coefficient activity pressure (pa) (0% v/v polyimide films) (1.25 % v/v polyimide films) 0.15 1694 0.00456 0.00438 0.21 2458 0.00440 0.00424 0.27 3205 0.00434 0.00419 0.34 4065 0.00431 0.00417 0.44 511 1 0.00429 0.00415 0.55 6326 0.00427 0.00414 0.68 7894 0.00426 0.00413 As shown, with increasing vapor activity, changes in the solubility coefficient between the hybrid and polyimide matrix are almost imperceptible, over the whole range of vapor activities studied. Clay did not appear to influence the sorption of ethyl acetate vapor by the polyimide film, at the concentrations evaluated. For the respective nanocomposite films, the solubility coefficients were similar to the solubility coefficient 62 values obtained for the non-clay polyimide films, at comparable vapor activity levels. As shown in Table 7, and from Figures 15 and 16, it was found that the solubility coefficient values were independent of vapor activity, at vapor activity values great than 0.5. For the polyimide-clay nanocomposite, the clay appears to have little effect on the solubility of ethyl acetate in the polyimide fihn, while significantly changing the inherent mobility of ethyl acetate vapor within the polymer bulk phase. Okamoto et a1. (1992) observed similar behavior for water sorption by the same type of polyimide fihn, where the solubility coefficient increased at low water vapor activities and leveled off at medium and high water activities. 63 0. 0050 0.0045 . 0. 0040 0. 0035 Solubility coefficient (cc [STP] cc ' pa ') 0.0030 . . . . . . . 0.000 0.100 0.200 0.300 0.400 0.500 0.600 0. 700 0.800 Vapor Activlty, p/p , Figure 15 Solubility coefficients of non-clay polyimide films 0.0050 0.0045 3' v r 4 0.0040 . 0.0035 . Solubility coefficient (cc [STP] cc pa ') 0.0030 0.000 0.100 0.200 0.300 0.400 0.500 0.600 0.700 0.800 Vapor Activity, p/p , Figure 16 Solubility coefficients of 1.25 v/v % clay/polyimide films. 64 3. Dual mode sorption parameters The sorption isotherms obtained for the non-clay polyimide and 1.25 v/v % clay/polyimide nanocomposite are presented in Figures 17 and 18, respectively, with the calculated sorption isotherm curve obtained from Equation 8 superimposed for comparison. As shown, the sorption isotherm obtained for this polymer is concave to the activity axis at low activity and linear at higher activity levels and was accurately described by Equation 8, the dual-mode sorption model. Okamoto et a1. (1992) found that for water sorption by the same type of polyimide film, the sorption isotherms of water vapor in polyimide films were in good agreement with the dual-mode sorption model. Okamoto et a1. (1992) proposed that the large values of both kg and b and the small values of C 'H are characteristic of water vapor sorption in the polyimide films, as compared with the respective constants describing C02 sorption. The large values of both kg and b are suggestive of interaction between imide groups and water molecules. Large values of both kg and b and a small value of C '2; cause appreciable deviation from the Henry's law isotherm, in the low vapor activity region. Cszp+m (8) The dual mode sorption parameters for the ethyl acetate vapor/polyimide film system are summarized in Table 8. The constants for water vapor sorption by the same type of polyimide film, as reported by Okamoto et a1. (1992), are also given for comparison. According to the dual mode sorption model, the total quantity of penetrant 65 sorbed (C) is comprised of the Henry’s law component (CD) and the “hole” filling components (CH). The Henry’s law solubility (CD) and the Langmiur solubility (CH) values are plotted as a frmction of vapor pressure for the ethyl acetate/polyimide system in Figures 19 and 20, respectively. As shown in Figure 20, the "hole" filling component of the polymer matrix is saturated by organic vapor, when the vapor pressure exceeded 1600 pa. The small values of k0 (Henry's law solubility constant) and the large values of C 'H (Langmuir capacity constant) are characteristic of organic vapor sorption in the polyimide films, as compared to water vapor sorption. Table 8 Dual-Mode Sorption Parameters for Polyimide film [(1) b C 'H CC(STP)/Cco pa pa’l [cc(STP)/cc] Ethyl acetate vapor 0.00425 0.0218 20.5 23 °C (Non-clay) Ethyl acetate vapor 0.00412 0.0252 19.6 23 °C (1.25 v% clay) Water vapor 0.00630 0.0022 6.0 50 °C “ (Non-clay) 3'" Okamoto K., 1992. " Sorption and Diffusion of Water Vapor in Polyimide Films ". Journal of Polymer Science: Polymer Physics Edition 30: 1223. 66 60.0 50.0 . 40.0 . 30.0 . 20.0 - z’ / |.- ._ C [cc(STP)/cc] Q Experimental _ Theoretical 10.0 J 0.0 .5.. , ,5, 0100020003000400050006000700080009000 Vapor Partial Pressure, pa Figure 17. Typical sorption isotherm of ethyl acetate in non-clay polyimide films at 23°C C [cc(STP)/cc] S O l— . Experimental — Theoretical 0 1000 2000 3000 4000 5000 6000 7000 8000 9000 Vapor partial pressure, pa Figure 18. Typical sorption isotherm of ethyl acetate in 1.25 v/v % clay/polyimide fihns at 23°C 67 40.0 35.0 - ‘g 30.0 . E 25.0 . m 20.0 . ‘0 o 15.0 9 9- 100 a . . o 5.0 . 0.0 0 1000 2000 3000 4000 5000 6000 7000 8000 9000 Vapor Partial Pressure, pa Figure 19. Concentration (CD = KD . p) by Henry's Law is a function of the vapor pressure. 30. O 25.0 - 20.0 . ‘__-_.n_.l__.——r——o 15.0 . 10.0 . 5.0 . CH, (cc[STP]Icc) 0.0 O 1000 2000 3000 4000 5000 6000 7000 8000 9000 Vapor Partial Pressure , pa Figure 20. Langmuir solubility (CH = C - CD) is not a function of the vapor pressure at a relatively high vapor partial pressure. 68 Diffusion Properties For the sorption of the ethyl acetate by the non-clay polyimide films and clay- loading films, the experimental sorption curve was found to deviate from the theoretical data. These findings would indicate that the sorption process might follow non-Fickian behavior. Thus, the diffirsion coefficient values were determined by the application of the curve fitting methods described in the Materials and Methods section (see Page 44 - 51). Tables 9 & 10 summarize the diffusion coefficient values determined by the respective curve fitting methods, over a range of vapor activity levels. As shown, in Tables 9 and 10, the calculated diffusion coefficients appear to be similar, for the respective methods. In the present study, the Least Squares Method was used to calculate the diffusion coefficients. For validating the diffusion coefficient variance, the Least Squares Method provides an integration procedure which includes the entire sorption data. Also, the diffusion coefficients would be consistent with the data obtained from earlier studies, which used the same least square method (Barr, 1997). Table 9 Diffusion coefficient values (mz/s) for non-clay polyimide films, determined as a function of vapor activity. Vapor Diffusion Coefficients Diffusion Coefficients Diffusion Coefficients Activity By By By (a,) Gauss-Newton method Half sorption time method Least Squares method 0.15 0.347 x 10 '“f 0.388 x 101° 0.401 x 10 'j‘j 0.21 0.460 x 10 i": 0.476 x 10 "I 0.537 x 10::I 0.27 0.479 x 10 'I° 0.551 x 10 I° 0.608 x 10 III 0.34 0.700 x 10 ‘16 0.754 x 10 1‘: 0.875 x 10 ‘j‘j 0.44 0.884 x 10 4“ 1.036 x 10 'jj 1.290 x 10 'j‘j 0.55 1.380 x10 'I° 1.429 x10 "III 1.725 x10 "I 0.68 2.780 x 10 'I° 2.808 x 10 'I° 3.290 x 10 'I° 69 Table 10 Diffusion coefficient values (mI/s) for clay-loading polyimide films, determined as a function of clay loading and vapor activity. Clay Vapor Difi‘usion coefficients Diffusion coefficients Diffusion coefficients Loading activity By Gauss-Newton By Half sorption time By Least Squares (3,) method method method 1.25v% 0.27 0.215 x 10 "6 0.259 x 10 "6 0.292 x 10 "6 0.34 0.255 x 10 "5 0.305 x 10 "5 0.351 x 10 "6 0.44 0.515x10’I° O.669x10°I° 0.715x101° 0.55 1.025x10'I° 1.153x10'I° 1.280x10’I° 0.68 1.995 x 10 "6 2.066 x 10 “6 2.290 x 10 "5 2.5 v% 0.44 0.451 x 10 "6 0.484 x 10 '1‘ 0.555 x 10 "6 0.55 0.611 x 10 "6 0.669 x 10 "6 0.745 x 10 "6 0.68 1.555 x 10 "6 1.684 x 10 "6 1.903 x 10 "6 5.0 v% 0.68 0.885 x 10 “6 1.035 x 10 "5 1.160 x 10 "6 70 1. Effect of Ethyl Acetate Vapor Activity Diffusion coefficient values obtained from the gravimetric experiments are presented in Table 11. For better illustration, the results obtained for the non-clay loading polyimides and the 1.25 v/v % polyimide/clay nanocomposites films are presented graphically in Figures 21 and 22, respectively. As shown, in Table 11 and Figures 21 & 22, for the non-clay loading polyimide and the 1.25 v/v % clay composites, diffusion coefficient values increased with an increase in vapor activity of ethyl acetate, indicating a concentration dependency of the diffusion coefficient. Okamoto et a1. (1992) found that for water sorption by a similar polyimide film, the diffusion coefficient increases at low water vapor activities and leveled off at medium and high water activities. Integral sorption from zero pressure was investigated. Figure 23 shows typical normalized sorption curves of non-clay polyimide nanocomposites. M, and Mss refer to the mass sorbed at time t and the mass sorbed at steady state, respectively. Plots of M. ./ Mss versus time initially were linear. As shown, equilibrium sorption was achieved within 100 hours at av = 0.68 and 500 hours at av = 0.27, judging from the diffusion coefficient. At low vapor activity, the approach to equilibrium is extremely protracted, indicating the presence of a slow, minor component of sorption in addition to the normal, major mode of sorbate uptake. 71 4.00 3.50 . 3.00 . 2.50 . 2.00 . 1.50 . 1.00 . 0.50 . 0.00 0.10 0.20 0.30 0.40 0.50 0.60 0.70 0.80 0.90 1.00 Ethyl Acetate Vapor Activity, P/Ps (m’lsec) x 10 "‘ Diffusion Coefficient Figure 21 Diffusion Coefficients of non-clay polyimide film versus organic vapor activity. 2.50 2.00 1.50 . 1.00 . (m’lsec) x 10 '“ Diffusion Coetl'lclent 0.50 . 0.00 0. 10 0. 20 0.30 0.40 0.50 0.60 0.70 0.80 0. 90 1.00 Ethyl Acetate Vapor Activity, P/Ps Figure 22 Diffusion Coefficients of 1.25 v% polyimide-clay nanocomposite films versus organic vapor activity 72 1.2 3 E B .5. 3 2 gr —e—a=0.68 +a=0.44 +a=0.27 0 100 200 300 400 500 Time(hou r) Figure 23 Variation in normalized sorption of ethyl acetate in non-clay polyimide film with time after introduction of vapor at 23 °C. Diffusion coefficients are 3.2, 1.2, and 0.6 (x 10'I°m2/s), respectively. Table 11 Vapor activity dependence of diffusion coefficient values (x 10’[6 1n2/s) in polyimide-clay nanocomposites. Vapor Clay loading Clay loading Clay loading Clay loading aCfiVit)’ 0 v/v% II 1.25 v/v% 2.50 v/v% 5.00 v/v% 0.68 3.25 i 0.04 2.29 1.90 1.16 0.55 1.69 i 0.04 1.28 0.75 0.44 1.13 i 0.14 0.72 0.56 0.34 0.89 i 0.05 0.35 0.27 0.65 :i: 0.06 0.29 0.21 0.48 i 0.06 0.15 0.36 :t 0.06 a. Diffusion coefficient values are the average of at least two sorption tests. 73 The data obtained showed a significant increase in the diffusion coefficient with an increase in vapor activity for the non-clay loading polyimide and the 1.25 v/v % clay/polyimide nanocomposite. Such dependence is well known for a number of polymer-permeant systems, for which an exponential relationship was proposed (Crank, 1951). The permeation data through a film can be accounted for by a diffusion coefficient, which increases exponentially with an increase in the local solute content in the polymer film, as described by Equation (31): D = D* exp(y C) (31) Where D* is the limiting diffusion coefficient and y is a coefficient that can be interpreted as characterizing the ability of a penetrant to 'plasticize' a polymer, i.e. to increase the polymer segmental chain mobility. Schematically, the polymer structure is loosened as penetrant molecules are inserted between polymer segments, and more free volume is available for penetrant diffusion. The molecular origin of the exponential dependence of the diffusivity on both penetrant concentration and polymer free volume can be found in the free-volume theory (Neogi, 1996) (Meares, 1993). Figures 21 and 22 indicate that the diffusion coefficient for ethyl acetate increases exponentially with its local concentration in the polymer membranes. 74 0n the other hand, it should be noted that the observed increase in the diffusion coefficient, with increased solute content in the polymer, must not lead to a value larger than that of the solute self-diffusion coefficient. In fact, being limited by the extent of penetrant sorption, the diffusion coefficients increase less than tenfold, over a vapor activity range from the vacutun state to saturated state. In the case of the polyimide-clay nanocomposite of 1.25 v% clay loading, the diffusion coefficients increase about six-fold, when vapor activity increased from 0.3 to 0.7. The exponential relationship found between the diffusion coefficient and vapor activity for the polymer film is consistent with the results obtained by Perrin (1996) on the water/polyvinyl alcohol (PVA) system, but shows a lack of agreement with the results reported by Okamoto et a1. (1992) on the water/Polyimide system and Gu (1997) on the ethyl acetate/Polyimide system. Gu (1997) reported that ethyl acetate vapor concentration did not significantly affect the permeability coefficient values for the same polyimide films, over a vapor pressure range between 1700 to 3200 Pa. The results of the permeability studies reported by Gu are summarized in Table 12. The diffusion coefficient values determined by Gu (1997) and the values obtained in the present study are summarized in Table 13. The lack of agreement between the diffusion coefficient values reported by Gu and those obtained in the present sorption studies is not fully understood and a clear explanation for the discrepancy between these two cases can not be provided. The present studies suggest that the behavior of the diffusion coefficients is 75 the result of the effect of local chain organization, clay dispersion, polymer matrix morphology and the distribution of clay domains. Table 12. composite films at 23 °C in the Literature (Gu, 1997). Effect of ethyl acetate vapor pressure on the permeability of Clay/polyimide Vapor activity Ethyl acetate partial Permeability Coefficient ( Kg nV(m?sec pa) ) (a,) pressure (Pa) 0 v/v % Clay 2.5 v/v% Clay 0.27 3200 1.24 x 10 '"I 0.188 x I?“ (24.36 mmHg) -- -- 0.15 1700 1.14x10'I° 0.127x10'I° (12.87 mmHg) Table 13. Comparison of the diffusion coefficient values of Non-clay polyimide composite films/Ethyl acetate at 23 °C between the Literature (Gu, 1997) and this study. Vapor activity Ethyl acetate partial Diffusion Coefficient ( m‘ /sec ) (av) pressure (Pa) Literature This Study 0.27 3200 (3.1 i 0.2) x 10 "4 (6.5 i 0.6) x 10 "7 (24.36 mmHg) 0.15 1700 (5.7:1.3)x10'” (3.6i0.6)x10'I7 (12.87 mmHg) 76 2. Effect of Clay-Loading on Polyimide-clay Nanocomposites .a=0.68 Aa=0.55 *— .a = 0.44 Diffusion Coefficient (x 10’" m‘lsec) O. 00 , . . 2 . . . . a . - . 0 0.01 0.02 0.03 0.04 0.05 0. 06 Clay loading (vlv) Figure 24 Clay-loading Dependence of diffusion coefficients in Polyimide-clay Nanocomposites a E 3 E :3 -—o—0 V/V% E- _._1.25 vlv % +2.5 vlv 96 +5.0 WV 96 0 .. . f . . . . f 0 100 200 300 400 500 600 700 800 Time(hour) Figure 25 Variation in clay-loading dependency of normalized sorption of ethyl acetate (a = 0.68) in polyimide/clay films with time after introduction of vapor at 23 °C. Diffusion coefficients are 3.3, 2.2, 1.9, and 1.1 (x 10'1° mz/s), respectively. 77 Figure 24 shows the variation of the diffusion coefficient as a fimction of the clay loading level. Also, Figure 25 presents typical normalized sorption curves, as a function of clay loading. As shown in Figure 25, at high clay loading, the approach to equilibrium sorption levels is extremely protracted, indicating the presence of a longer diffusion path through the film. This is illustrated in Figure 24, which shows that, with an increase in clay loading, the diffusion coefficient decreased dramatically. The function of the clay can be interpreted as characterizing the ability to 'modify' the polymer, i.e. to increase the diffusion path of a diffusing gas through the polymer matrix. For a gas-impermeable clay, the diffusion coefficient values may only be determined by the aspect ratio (L/W) of the clay inclusion and the clay loading v). These results also show that the effect of clay loading and organic vapor activity are independent. As a result, the degree of improvement of the barrier properties of polyimide/clay nanocomposites depends on the clay inclusion. It appears that the clay restricts the permeant mobility by decreasing the diffusion coefficient. The decrease in the diffusion coefficient can be explained by an increase in the tortuosity of the diffusion path and also by a restriction of the mobility of the polymer segments blocked in the impermeable clays. The greater the level of clay loading, the lower the effectiveness of penetrant diffusivity, at the same penetrant concentration. However, no model is available to account for the above effects. 78 Such dependence found between the diffusion coefficient and the volume fraction of clay inclusion in the polymer film is consistent with the results obtained by Gu (1997) (See Table 12), who reported that the clay-loading level dramatically affected the permeability coefficient values for the same polyinride films. The results of the sorption and permeability studies show that the mineral clay inclusion dramatically improved the barrier properties of intercalated and exfoliated polyimide-day nanocomposite films. 79 3. Aspect Ratio and Tortuosity As shown by transmission electron microscopy (TEM), for the clay/polyimide composites, montmorillonite is disposed parallel to the fihn surface. (Lan, 1994) In this case, the total path of diffusing gases is increased. If montmorillonite plates of length L and width W, are dispersed parallel within the polymer matrix, the tortuosity factor I, which can be directly calculated by the aspect ratio (L/W), is the main factor in controlling the diffusivity of the vapor through the polymer matrix (Nielsen, 1967). As previously discussed, (see page 56 - 58), the clay loading level doesn't appear to effect the solubility values and the respective solubility coefficients, where S, and Sp (Sc and Sp are the solubility coefficient values for the composite and polymer matrix, respectively) are equivalent. In Equation (18), the relative permeability data can therefore be replaced by the relative diffusion coefficient data. Therefore, the relative diffusion coefficient ratio (Dc / DP), where Dc and DI, are the diffusion coefficients for the composite and polymer matrix, respectively, is given by Equation (32): D P DS 1 . __c-§_c.___ c c = (32) DP Pp DpSp 1+ (L/2W)v, where V; represents the volume fraction of clay, and the aspect ratio (L/W) can be estimated fi'om the experimental diffusion coefficient data. 80 0.8 - a 0.6 - Q a” 0.4 - 0.2 _ 0 . . a . . . . 0 0. 025 0. 05 0. 075 0. 1 Volume Fraction Figure 26 Relative diffusion coefficient value of polyimide-clay nanocomposite at ethyl acetate vapor activity = 0.68 @23 °C 0%RH. Based on this expression, an effective aspect ratio was estimated from the diffusion coefficient data (DC/DP). Figure 26 illustrates the results obtained by application of Equation 44 to the experimental data. The solid curve represents the best fit of the calculated values from Equation 45 to the experimental data. The best-fit curve yields an effective clay aspect ratio of approximately 100 from the ethyl acetate sorption studies. Table 14 summarizes the estimated aspect ratio values obtained from the permeability data reported in the literature for similar clay/polyimide composites. The aspect ratio determined in the present study fell within the range reported in the literature. It should be noted that the films used in this study were the same films employed by Gu (1997). Also, it is further assumed that the clay texture in the nanocomposite films evaluated in the present study is similar to that obtained by Lan (1994) and Yano (1993), since the 81 methodologies employed in the respective studies in preparing the nanocomposite films were similar. Table 14 Comparison of the estimated aspect ratio with the literature data. Penetrant (23 °C) Source Estimated Aspect Ratio Ethyl Acetate This study 100 Water Gu, 1997 132 C02 Gu, 1997 83- 02 Gu, 1997 87 C02 Lan, 1994 192 Water Yano, 1993 200 It should be pointed out that the diffusion path model described is based on the assumption that the impermeable clay layers are perfectly oriented and evenly spaced within the matrix of the polymer. However, this situation is not likely to be realized in actual composite structures (Messersmith 1995). As described above, a low loading level (i.e. 5% wat) of clay improves the barrier properties of polyimide nanocomposite drastically. In general, for polymer films containing conventional clay type fillers, clay loading levels of up to 40%(wt/wt) are required to reduce the permeability of the clay filled structure. The observed increase in the barrier performance of the nanocomposite is attributed to the molecular level dispersion and specific geometry (thin plate) of the clay layers in the polymer entity. Those facts result in a large interfacial area between the clay and the polymer matrix and lead to excellent barrier properties. 82 Error Analysis I. Uniformity of the nanocomposite films The uniformity of the test films introduced the most variation in this study. Each sample of film was prepared by an individual batch procedure. Even for the pure polyimide fihns, variations may occur when using polymer solutions from a different condensation polymerization series. In addition, when preparing polyimide-clay composites, variation in stirring efficiencies in the reaction vials may result in different aspect ratios (L / W) for the clay particles. Finally, each film was cast on individual glass plates. Differences in surface properties of the respective glass plates may result in variation of film structure which may effect the orientation of the films and tortuosity of the permeant diffusing through. It is assumed that the diffusion coefficient would be most impacted by a lack of uniformity of the polyimide films. 83 II. Thickness variance of the films All of the variables described above can contribute to differences in the individual film samples in terms of the film thickness. The following is an example of thickness variation for a 2.5 v/v% Polyimide-clay film, at an ethyl acetate vapor activity of av = 0.68. (Table 15) Table 15. Thickness distribution of the test film (2.5v% polyimide-clay) for the sorption of ethyl acetate at av = 0.68 and T = 23°C. 1 2 3 4 5 6 u 0' Thickness 0.75 0.80 0.85 1.05 0.90 0.85 (mil) 7 8 9 10 ll 12 0.908 0.090 Thickness 1.00 0.90 1.00 1.00 0.90 0.90 (mil) The variation of the thickness can account for the variation observed for the diffusion coefficient values. 84 III. Concentration variance of the permeant The concentration of the ethyl acetate vapor in the hangdown tube can effect the partial pressure of the sorbate, which can directly impact the sorption value used in calculating the diffusion coefficient, especially in the very beginning of the experiment. The volume of the hangdown tube (i.e. 500cc) is significant. At the start of the sorption experiment, the volume is void of permeant vapor. While in an ideal test simulation, the volume in the electrobalance hangdown tube should instantaneously be filled with the desired vapor concentration at the time of experiment initiation, the physical design of the apparatus do not make this possible. At an operating flow rate of 15 cm3/min, the time required for the vapor concentration in the hangdown tube to approach 95% of the desired level would be approximately 2 hours. Figure 27 shows the plot of the ethyl acetate vapor concentration as a function of time. Compared to the time values to equilibrium (Table 4, Page 59), the time to reach the desired vapor concentration level would likely be minimal. Thus, the time required for displacement of the electrobalance hangdown tube volume by the penetrant vapor stream has introduced a small fraction of error into the diffusion coefficient values. 85 1.20 1.00 _ 0 0 0.80 _ 0.60 _ Pressure (96) 0.40 - 0.20 - Partial Pressure/Equilibrium vapor 0.00 . , , .4 0 1 2 3 4 5 Time (hour) Figure 27 Equilibrium vapor pressure in the lower portion of the electrobalance hangdown tube as a function of time. 86 IV. Temperature variance of testing system Temperature changes would effect the speed of the molecular movement and would effect the equilibrium solubility, as well as result in a change in the ratio of diffusivity. This is therefore an important variable in determining the diffusion coefficient. In the present study, the temperature of the test system was at ambient temperature (23 i 1 °C) and would fluctuate with building temperature fluctuation. A typical plot of temperature versus time is presented in Figure 28. The solid line in Figure 28 is the vapor uptake profiles. 30.0 29.0 - 28.0 _ 27.0 . 26.0 . 25.0 24.0 23.0 22.0 21.0 , , 1 , 20.0 0 50 100 150 200 250 300 Time (hour) Vapor uptake (mg) ‘ 7‘ ’.e :5 , 'wht: ‘4 4"“ “'1: +1.25 v% clay Poiyimide@ a=.55 _ _ .- - Roorn'i'emperature Room tempearture (° C) QANQAOIQV Figure 28 1.25v% Polyimide-clay composite sorption profile under alternating system temperature. As shown, the highest temperature was 27.2 °C, the lowest temperature was 221°C, with a mean temperature at 23.23 i 1.04 °C. 87 V. Non-Fickian sorption behavior During the sorption of ethyl acetate by the non-clay polyimide films and clay- loading films, the experimental curve was found to deviate fi'om the theoretical data. The higher the vapor activity, the greater the departure from the theoretical data and the higher the residual error. These findings can be explained by sorption induced swelling of the polymer matrix, resulting in the sorbate/polymer system exhibiting non-Fickian behavior. Table 16 summarizes the residual error, over the whole vapor activity range. The dramatic changes observed at the vapor activity values greater than 0.3 are evident. Table 16 Residual errors by the Gauss-Newton curve fitting method as a firnction ethyl acetate vapor activity. Vapor Residual Error Diffusion Coefficient Diffirsion Coefficient II Activity By By By Gauss-Newton method Gauss-Newton method Least Squares method 0.15 0.044 0.347 x 10 III 0.401 x 10 III 0.21 0.045 0.460 x 10 I° 0.537 x 10 I° 0.27 0.045 0.479 x 10 III 0.608 x 10 II 0.44 0.084 0.884 x 10 I° 1.290 x 10 'I° 0.55 0.085 1.380 x 10 I° 1.725 x 10 'II 0.68 0.090 2.780 x 10 'I° 3.290 x 10 'I° 88 Summary and Conclusion The sorption of ethyl acetate vapor by polyimide-clay nanocomposite films was determined with the Cahn 2000 electrobalance, using a gravimetric technique and recording the weight gain by the polymer sample as a function time and vapor activity. The clay loading content and the organic vapor activity are the two major factors affecting the sorption and diffusion properties of polyimide-clay nanocomposites. For this nanocomposite film, montmorillonite is dispersed homogeneously within the polyimide matrix and oriented parallel to the film surface. No significant change was found in the solubility values at equilibrium between the non-clay fihns and clay loading films, over the range of testing vapor activity levels studied. The equilibrium solubility values of polyimide-clay nanocomposite films could be accurately estimated by the total value of the independent unfilled polymer and the clay powder itself. The results of sorption studies showed that the polymer matrix and clay filler have similar organic vapor absorption properties, and the clay has neither a synergetic or antagonistic effect on the solubility of organic vapor in the polyimide matrix. Comparison of the solubility coefficient values obtained for the non-clay films and clay loading films showed the values to be reasonably consistent, over the range of vapor activity levels studies. Because of the imperceptible changes in equilibrium solubility between the polyimide-clay hybrid and the simple polyimide matrix, over the 89 entire range of activity levels studied, the organic vapor solubility coefficient values were not effected by the presence of the clay inclusion. According to the dual mode sorption model, the solubility coefficient value would appear to be a constant value, represented by Henry's law constant, kg, at medium and high vapor activity. Compared with the water sorption data, the small values of kg and the large values of CH (Langmuir capacity constant) are characteristic of ethyl acetate vapor sorption in the polyimide films. The exponential relationship found between the average diffusion coefficient and the vapor activity for the test systems evaluated can be explained by 'plasticizing' of the polymer matrix by the organic vapor, thus enhancing polymer chain segmental mobility as penetrant molecules are inserted between polymer segments, and resulting in an increasing in more free volume available for penetrant diffusion. The free-volume theory well described the molecular origin of the exponential dependence of the diffusivity on penetrant concentration and polymer free volume. The observed increase in the diffusion coefficient, with increased solute content in the polymer, should not lead to a value larger than that of the solute self-diffusion coefficient. In this study, the diffirsion coefficient increase around tenfold, over a vapor activity range from the vacuum state to saturated state. In the case of the polyimide-clay nanocomposite of 1.25 v/v% clay loading, the diffusion coefficients increase about six-fold, when vapor activity increased from 0.3 to 0.7 . Such dependence found between the diffusion coefficient and the clay loading content of the nanocomposites can be the result of the effect of the aspect ratio and 90 tortuosity. Due to the specific structure, it is assumed that montmorillonite was dispersed homogeneously and disposed parallel to the film structure. As a result, the polyimide-clay nanocomposite had excellent vapor barrier properties. Only a small volume fi'action of clay will result in a significant decrease in the diffusion coefficient. The diffusion coefficient of a 5.0 v/v% clay/polyimide film at vapor activity a, =I0.68 is only one third of the diffusion coefficient value of the comparable non-clay polyimide film. The greater the level of clay loading, the lower the effectiveness of penetrant diffusivity, at the same penetrant concentration. This result is well explained by an increase in the tortuosity factor. The effective clay aspect ratio of approximately 100 from the ethyl acetate sorption in the present studies fell within the range reported in the literature. The observed increase in the barrier performance of the nanocomposite is attributed to the molecular level dispersion and specific geometry (thin plate) of the clay layers in the polymer entity. Those facts result in a large interfacial area between the clay and the polymer matrix and lead to excellent barrier properties. Thus, the clay loading content, sorbate concentration and specific geometry of the clay layers in the polymer matrix would provide the polyimide-clay nanocomposites with unique properties for application in the packaging area. 91 Recommendation and Proposed Future Studies Base on the results of this study, a number of recommendations for future research can be suggested. The following proposed studies might lead to a better understanding of the mass transfer of low molecular weight penetrants through the polyimide nanocomposites. 1. Due to the time constriction, this study only conducted one run for the sorption experiments involving the polyimide-clay nanocomposite films. It is proposed to duplicate the sorption experiments for the clay-loading polyimide films (1.25 v/v% ~ 5.0 v/v%) at vapor activity av = 0.21, 0.27, 0.34, 0.44, 0.55, 0.68. 2. Ethyl acetate was picked as the sorbate in this study because of its presence in many food flavor profiles. A similar study comparing the solubility and diffusion coefficient values should be made using a series of sorbates of varying molecular mass. 3. The current studies was conducted at RH = 0. It can be proposed that a similar investigation be conducted as a function of relative humidity (i.e. 50%, 95%) to investigate how the moisture affects the sorption mechanism for organic penetrants. . 92 "..‘..4. IF: “I” i . r In this study, all sorption measurements were conducted at ambient temperature. It is proposed that additional experiments be conducted over a range of temperatures, to investigate: i) whether the temperature dependence of the solubility, and diffusion coefficient values can be described by the Arrhenius equation, ii) whether the solubility, and diffusion values agree as a function of temperature. Sorption by non-clay and clay loading-polyimide fihns should be determined at lower ethyl acetate activity levels (i.e. a, = 0.01, 0.02, 0.05, 0.1) where feasible, to understand how well the experiment data fits the dual-mode sorption model. 93 APPENDICES 94 Appendix A Vapor-Liquid Equilibria for pure substances (V LPT)‘ Ethyl acetate (Ethanoic acid ethyl ester, Ethyl ethanoate): C4 H3 02 141-78-6 M = 88.1063 Coefficients: a] = 21.1891 a2 = 2838.03 a3 = -56.5630 T (°C) P (mmHg) —20 6.390 -15 9.149 -10 12.874 -8 14.629 -5 17.262 -4 18.681 0 24.359 2 27.462 4 30.893 6 34.679 8 38.848 10 43.432 12 48.463 14 53.973 16 59.998 18 66.576 20 73.745 21 77.564 22 81.546 23 85.697 24 90.022 25 94.527 30 119.950 40 187.850 60 417.980 I CRC Handbook of Thermophysical and Thermochemical Data. (David R. Lide & Henry V. Kehiaian) 95 Appendix B Basica Program for Diffusion Coefficient by "Consistency for Continuos Flow" Method" 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 160 170 180 190 200 210 215 220 230 235 240 250 260 270 280 290 300 305 310 320 330 REM sorption continuous flow experiment DIM F980), T(80), x(80), DF(80) REM time -- minute, D -- m /sec INPUT "Enter the thickness of the film (MIL) -- ", LL INPUT "Enter the steady state sorption value (mg) -- ", Fl NUM=0:N1=1:N2=1 DF(NUM+1) = F(NUM+1)/FI READ T(NUMI), F(NUM+1) DF(NUM+1) = F(NUM+1)/FI IF T(NUM+1) = 99.99 THEN 140 PRINT T(NUM+1), F(NUM+1) NUM = NUM+1 GOTO 80 GUESS = 10 ’SET INITIAL GUESS REM NEW-RAPHSON METHOD FOR 1=1 T0 NUM IF DF(I) < 0.05 AND DF(I+1) >= 0.05 THEN N1=I+1 IF DF(I) < 0.95 AND DF(I+1) >= 0.95 THEN N2=1 NEXT I FOR I = N1 T0 N2 A = 0.44313 * DF(I) 'SQRT(rr)/4 = 0.44313 x = GUESS FOR J: 1 To 10 B = SQR(X) c = EXP(-X) H=(0.5/B-B)* C x = x- ((B'l'C - A)/H) IF x <0 THEN GUESS = SQR(GUESS) : GOT0 215 NEXT J X(I) = 1/x GUESS = x NEXT 1 REM LINEAR REGRESSION ST = 0 SX = 0 : SXT = 0 STSQ = 0 ‘ Referenced by Burgess and Hernandez, 1998. 96 340 SXSQ = 0 350 NN =N2 -N1 +1 360 FOR I =N1 T0 N2 370 ST = ST + T(I) 380 sx = sx + X(I) 390 SXT = SXT + X(I) * T(I) 400 SXSQ = SXSQ + X(I) * X0) 410 STSQ = STSQ + T(I) * T(I) 420 NEXT 1 430 SLOPE = (ST * SX - NN * SXT)/(ST * ST - NN * STSQ) 440 DUMI = (NN * SXT) - (SX * ST) 450 DUM2 = (NN * STSQ) - (ST * ST) 460 DUM3 = (NN * SXSQ) - (SX * SX) 470 DUM4 = SQR(DUM2 * DUM3) 480 R= DUMl/DUM4 490 LPRINT LL; "MIL, "; ' 1.25V% Clay/Polyimide Film at Ethyl Acetate Vapor" 500 LPRINT 510 LPRINT "Time (min) ", "Weight gain", " l/X", "Relative Percentage" 520 FOR I =' 1 TO NUM 530 LPRINT T(I), F(I), X(I), DF(I) 540 NEXT I 550 LPRINT 555 LPRINT "STEADY STATE SOLUBILITY "; FI; "mg" 560 LPRINT 570 DIFF = ((LL * 0.0000254)"2)/4/60 * SLOPE 580 LPRINT "DIFFUSION COEFFICIENT (mZ/sec) ="; DIFF 590 LPRINT 600 LPRINT "CORRELATION COEFFICIENT =", R 610 REM CONSISTENCY 620 F11 = F] / 4 630 I = 1 640 1 =1 + 1 650 IF DF(I) < 0.25 GOTO 640 660 T14 = T(I-1)+(T(l)- T(I-1))/(F(I)- F(I-1))*(F11 - F(I-1)) 670 I: I + 1 680 IF DF(I) < 0.5 GOTO 670 690 T12 = T(I-1)+(T(I)- T(I-1))/(F(I)- F(I-1))*(F11* 2 - F(I-1)) 700 IF I = NUM THEN 730 710 1 =1 +1 720 IF DF(1) < 0.75 GOTO 700 730 T34 = T(I -1)+(T(I)- T(I-1))/(F(I)- F(I - 1)) * (F11 * 3 - F(I-1)) 740 LPRINT 750 LPRINT "T El"; T14, " T U"; T12, " T U"; T34 760 x14 = 1/(SLOPE*T14) : x12 = l/(SLOPE'l‘TlZ) : x34 = 1/(SLOPE*T34) 770 PRINT "x14 "; x14, " x12 "; x12, " x34 "; x34 97 780 LPRINT "K1 "; X34/X14, " K2 "; X12/Xl4 790 LPRINT 800 END 810 DATA 820 DATA 830 DATA 99.99,99.99 98 Bibliography American Colloid Company web page, 1998. "American Colloid Company - industrial specialist". Web address "http://www.colloid.com/finechm.htm" Bandosz, T. J ., 1992. "Chemical and Structure Properties of Clay Minerals Modified by Inorganic and Organic Materials". Clay Minerals, 27, 435. Barr, C. D., 1997. "A Comparison of Solubility Coefficient Values Determined by Gravimetric and Isotatic Permeability Technologies", Master Thesis, School of Packaging, Michigan State University. Barrer, R. and Barrie, J ., 1957. Journal of Polymer Science, 23, 315. Blumstein, A., 1965. "Polymerization of Adsorbed Monolayers. 11. Thermal Degradation of the Inserted Polymer". Journal of Polymer Science, Part A. 3, 2665 Blumstein, R., 1974. "Acrylonitrile in Macromolecules". Apply. Polym. Symp, 25, P 81. Chicago, August 1974. Burgess, G. and Hernandez R. J ., 1998. PKG 985 course pack. Chen, Yan and Wang, Xinyu, 1997. (Institute Chemistry, Chinese Academy Science, Beijing, P. R. China). Gaofenzi Xuebao, 1, 73-78(Chinese). Coleman, M. R. and Koros, W. J., 1990. J. Membrane Sci, 50, 285. Crank, J. and Park, G. S., 1951. Trans. Faraday Soc., 45, 240. Crank J., 1975. "The Mathematics of Diffusion". Academic Press, New York, NY. 99 Dupont Corporate home page, 1999. "Dupont Packaging". Web address "http://www.dupont.com/packaging/" Dupont Polybon (polyimide), 1998. "DuPont Aerospace Enterprise". Web address "http://www.dupont.com/corp/markets/aerospacel" Flory P. J ., 1953. "Principles of Polymer Chemistry". Fukushima, Y. and Inagaki, S., 1987. "Synthesis of an Intercalated Compound of Montrnorillonite and 6-Polyamide". J. Inclusion Phenom, 5, 473 F ukushima, Y., Okada, A. and Kawasruni, M., 1988. "Swelling Behavior of montmorillonite by Poly-6-amide". Clay Miner. v. 23, 27 Gavara, R. and R. J. Hernandez, 1993. "Consistency Test for Continuos Flow Permeability Experimental Da ". Journal of Polymer Film and Sheeting, 9: 126 Ghosh, M. K., 1996. "Polyimides Fundamental and Applications". Gilman, J. W., Kashiwagi, T., and Lichtenhan, J. D., 1997. Web address "http://flame.cfr.nist.gov/bfrlpubs/fire97/art01 5 .htrnl" Greenland, D. J ., 1963. "Adsorption of Polyvinyl Alcohol by Montrnorillonite". Journal of Colloid Science, 18, 647. Gu, Jiajin, 1997. "The Barrier Characteristics of Clay/Polyimide Nanocomposites", Master Thesis, School of Packaging, Michigan State University. Fukushima, Y., and Inagaki, S., 1987. “Synthesis of an Intercalated compound of Montomorilonite and 6-Polyamide”. J. Inclusion Phenom, 5, 473, Hernandez, R. J., Giacin, J. R., and Baner, A. L., 1986. "The Evaluation of the Aroma Barrier Properties of Polymer F ihns". Journal of Plastic Film and Sheeting, 2(3); 1 87-21 1 100 Hernandez, R. J ., Giacin, J. R., and Grulk, E. A., 1992 "The Sorption of Water Vapor by an Amorphous Polyamide". J. Membrane Sci, 65: 187-199. Hernandez, R. J ., 1994. "Effect of Water Vapor on the transport properties of oxygen through polyamide packaging materials". J. of Food Engineering 22: 495-507. Hernandez, R. J. 1998. Personal communication. Nov. 23, 1998. Hirschfelder, J. 0., Curtis, C. F., and Bird, R. B., 1954. Molecular Theory of Gases and Liquids, New York, P294. Hopfenberg H. B. and Stannett V., 1973. "Physics of Glassy Polymers" (Ed. By R. N. Haward) Applied Science Publishers, Banking. Chapter 9, 504. Kato, C., Kuroda, K., and Misawa, M., 1979. "Preparation of Montrnorillonite- nylon Complexes and Their Thermal Properties". Clays Clay Miner., v. 27, 129 - 136 Koros, W. J., Fleming, G., K., Jordan, S. M., Kim, T. H., and Hoehn, H. H., 1988. Prog. Polymer Sci., 13, 339. Kim, Y.; Lee, W. K., Cho, W. J., Ha, C. S., Ree, M., and Chang, T., 1997. (Department of Polymer Science and Engineering, Pusan National University, Pusan, 609-735 S. Korea). "Morphology of organic-inorganic hybrid composites in thin films as multi-chip packaging material." Polymer Int. 43(2), 129-136 (ENG). Kim, T. H., Koros, W. J., Husk, G. R., and O'Brien, K. C., 1988. J. Membrane Sci, 37, 45. Lagaly, G., and Beneke, K., 1975. "Intercalation and Exchange Reactions of Clay Minerals and Non-clay Layer Compounds". American Mineralogist, 60, 650 - 658. Lan, T., 1994. "Polymer-Clay Nanocomposite", Ph. D. dissertation, Michigan State University. 101 Lan, T., and Pinnavaia T., 1994(a). "0n the Nature of Polyimide-Clay Hybrid Composites", Chemistry of Materials, American Chemical Society, Vol. 6, (5), 573-575. Li, Qiang and Zhao, Zhudi, 1997 (State Key Lab. Engineering Plastic, Institute Chemistry, Chinese Academy Science, Beijing, P. R. China). Gaofenzi Xuebao 1997, (2), 188-193 (Ch). Mark, J. E., 1995. (Polymer Research Center, University Cincinnati) Int. SAMPE Tech. Conf 27, 539-548. Meares, P., 1993. European Polymer Journal, 29, 237. Mehrotra, V., and Giannelis, E. P., 1990. "Polymer Based Molecular Composites", MRS Symp. Proc., D. W. Schaefer J. E. Mark, Eds., MRS. Pittsburgh, 171. Messersmith, P. B. and Giannelis, E. P., 1993. "Polymer-layered silicate nanocomposites". Chem. Mater. 5, 1064 - 1066. Messersmith, P. B. and Giannelis, E. P., 1995. "Synthesis and Barrier Properties of Poly (8 - caprolactone) - Layered Silicate Nanocomposites". Journal of Polymer Science, 33(7), 1047-1057. Michaels, A., Vieth, W., and Barrie, J ., 1963. Journal of Applied physics, 34(1), 1 & l3. Myunghoon Lee, 1994. "Sorption of Organic Penetrants by Amorphous Polyamide" Master Thesis, School of Packaging, Michigan State University. Nakamura, A., Ninomiya, K., Tamura, Y., 1989. Kagaku Kogaku, 53, 646. Nanocor, Inc. web page, 1997. "Nanocomposites". Web address "http://www.nanocor.com/ " Neogi, P., 1996. "Diffusion in Polymers" Nielsen, L., 1967. Journal of Macromolecular Science Chemistry, Al (5), 929 102 Okada, A., Kawasumi, M., Usuki, A., Kojima, Y., Kurauchi, T., and Kamigaito, 0., 1990. Mat. Res. Soc. Symp. Proc. 171, 45-50. Okamoto K., Tarnihara N., Watanabe H., Tanaka K., Kita H., Nakamura A., Kusuki Y., and Nakagana K., 1992. " Sorption and Diffusion of Water Vapor in Polyimide Films ". Journal of Polymer Science: Polymer Physics Edition 30: 1223. Okamoto K., 1996. "10 Sorption and Diffusion of Water Vapor in Polyimide Film", Polyimides, Fundamentals and Applications. Pace, R. J ., and Datyner, A., 1980. "Model of Sorption of Simple Molecules in Polymers" Journal of Polymer Science: Polymer Physics Edition, Vol. 18, 1103 - 1124. Paul D. R., and Yampol'skii,Y. P., 1994. Polymeric gas separation membranes. Perrin, L., Nguyen Q. T., Clement R., and Neel J ., 1996. "Sorption and Diffusion of Solvent Vapors in PVA Membranes of Different Crystallinity Degrees" Polymer International, Vol. 39, No, 3, 251 - 260. Pinnavaia, 1997. Web address "http://slater.cem.msu.edu/~pinnweb/nanocomposites.html" Ruiz-Hitzky, E., 1993. "Conducing Polymers Intercalated in Layered Solids". Adv. Mater. 2(1), 545 - 547. Taylor, John R., and Hemandaz, R. J ., 1982. "An Introduction of Error Analysis", University Science Books. Tohoh, M., 1992. European Patent, 0479031 Toshiyuki Momma, 1997. Corrosion Research Center, University of Minnesota. Web Page: "http://www.cems.umn.edu/crc/NanoComposite_Momma.htrnl" 103 Triton Systems Inc., 1997. Web Page: http://www.aro.ncren.net/arowash/rt/a_l page8 1 .htrnl" Usuki, A., Okamoto K., Okada, A., and Kurauchi T., 1989. US. Patent 4,889,885. Usuki, A., Koiwai, A., Kojima, Y., and Okada, A., 1995. "Interaction of Nylon 6-clay Surface and Mechanical Properties of Nylon 6-Clay Hybrid." J. of Applied Polymer Sci, v.5, No. 1,119-123 Usuki, A., Okamoto, K., Okada, A., and Kurauchi, T., 1995(a). "Synthesis and Properties of Acrylic Resin-Clay Hybrid". Japanese Journal of Polymer Science and Technology, v.52, No. 11, 727 - 733 Vaia, R. A., Ishii, H., and Giannelis, E. P., 1993. "Synthesis and Properties of two- dirnensional nanostructures by direct intercalation of Polymer melts in layered silicates". Chem. Mater., v. 5, 1694 - I996. Vaia, Richard A.; Sauer, Bryan B.; Tse, Oliver K.; Giannelis, and Emmanuel P., 1997. (Department of Materials Science and Engineering, Cornell University, Ithaca, NY 14853 USA). J. Polymer Science, Part B: Polymer Physics 35(1), 59-67 (Eng), Wiley. Vieth, W. R., Howell J. M., and Hsieh, J. H., 1976. "Dual Sorption Theory" Journal Membrane Sci, 1, 177. Vieth, W., Tam, P. and Michaels, A., 1966. Journal of Colloid and Interface Science, 22, 360-370. Wensa, 1999. "Polymer-Clay Nanocomposites" Web Page:"http://www.geocities.com/Tokyo/Garden/21 16/nano_polymer.htm" Yano, K., Usuki, A., Okada, A., Kurauchi, T., and Kamigaito, 0., 1991. "Synthesis and Properties of Polyimide-Clay Hybrid". Polymer Preprint, 32(1), 65. Yano, K., Usuki, A., Okada, A., Kurauchi, T., and Kamigaito, 0., 1993. "Synthesis and Properties of Polyimide-Clay Hybrid". J. Polymer Sci. : Part A: Polymer Chemistry, v. 31, 2493. 104 Yano, K., Usuki, A., and Okada, A., 1997. "Synthesis and Properties of Polyimide-Clay Hybrid Fihns". J. Polymer Science: Part A: Polymer Chemistry, 35(11), 2289-2294. Ziegel, K. D., Frensdorff, H. K., and Blair, D. E., 1969. "Measurement of Hydrogen Isotope Transport in PVC F ihns by Permeation Rate Method". Journal of Polymer Science, Part A-2, 7: 809 105