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120   ACTIVATED CARBON

                     fluxes was obtained by exposure of the membranes to polypropylene (Jones and
                     Koros, 1994b). Jones and Koros (1995) also reported a solution to the problem
                     concerning the adverse effects of humidity by coating a thin layer of hydrophobic
                     polymer (e.g., Teflon) on the CMS membranes. Although small losses in selec-
                     tivity and productivity occur as a result of the resistance caused by adding the
                     polymer layer, the composite membranes are still very attractive when compared
                     with conventional polymer membranes (Jones and Koros, 1995).
                       An interesting method for coating the polymer layer on macroporous support
                     was described by Shiflett an Foley (1999). The polymer solution was sprayed on
                     the support with an ultrasonic nozzle, which generated droplets with relatively
                     uniform sizes and also minimized penetration into the support. A sintered stainless
                     steel tubing was used as the support, and a 25 wt % solution of polyfurfural alco-
                     hol (PFA) in acetone was sprayed through the nozzle. The ultrasonic nozzle was
                     operated at 40 kHz (the standard frequency for laboratory ultrasound cleaner).
                                                                                  ◦
                     The deposited film was subsequently pyrolyzed at a heating rate of 5 C/min
                           ◦
                     to 450 C for 2 h in He. SEM images showed the resulting membrane surface
                     to be uniform and defect-free. A comparison of the performance of this CMS
                     membrane and that prepared by pyrolysis of hollow-fiber polyimide membrane
                     is given in Table 5.10. The performance of a polysulfone hollow-fiber membrane
                     is also included in the comparison. Polysulfones are used for air separation, and
                     the dependence of their air separation properties on the structures of different
                     polysulfones has been discussed in detail by Pixton and Paul (1994). Although
                     the separation factor is higher for the PFA-derived membrane than the others, its
                     O 2 fluxis muchlower.
                       Diffusion in CMS membranes clearly follows that of surface diffusion or dif-
                     fusion of adsorbate in micropores. The simple kinetic theory of Chen and Yang
                     (1992) described in Chapter 3 for predicting binary diffusivities from single-
                     component diffusivities should be applicable. Indeed, the predicted binary dif-
                     fusivities for CH 4 /C 2 H 6 in CMS prepared from pyrolysis of PFA by using the
                     simple theory agreed well with the experimental data (Chen and Yang, 1994).



                     Table 5.10. Comparison of fluxes and separation factors at 3 atm feed and room temper-
                     ature for three membranes

                       Membrane     Thickness (µm)       Fluxes (GPU)       Separ. Factor

                                                     O 2      N 2    H 2       O 2 /N 2
                       CMS 1            21.3         0.557   0.018   6.05      30.4
                       CMS 2            30–35       24       1.7   150         12
                       Polysulfone 3                20       3.6                5.5
                     1 CMS membrane by pyrolysis of polyfurfural alcohol ultrasonically sprayed on sintered stainless
                     steel (Shiflett and Foley, 1999).
                     2 CMS membrane by pyrolysis of hollow-fiber polyimide membrane (Jones and Koros, 1994a).
                     3 From Jones and Koros, 1994a.
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