Measurements of Ternary Diffusion Coefficients of Aqueous Blended Alkanolamine systems: Diethanolamine + N- methyldiethanolamine + Water

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Measurements of Ternary Diffusion Coefficients of Aqueous Blended Alkanolamine systems: Diethanolamine + N-methyldiethanolamine + Water Proceedings of European Congress of Chemical Engineering (ECCE-6) Copenhagen, 6- September 7 Measurements of Ternary Diffusion Coefficients of Aqueous Blended Alkanolamine systems: Diethanolamine + N- methyldiethanolamine + Water Po-Hsun Lin, a Chih-Chiang Ko, a Meng-Hui Li a,b a R&D Center for Membrane Technology and Department of Chemical Engineering, Chung Yuan Christian University, Chung Li, Taiwan 33, Republic of China b Corresponding author. Abstract Ternary diffusion coefficients of aqueous blended alkanolamine systems diethanolamine (DEA) + N-methyldiethanolamine (MDEA) + water using the Taylor dispersion technique have been measured for temperatures 3, 4 and 5 o C. The systems studied were aqueous solutions containing the total amine concentrations of, 3, and 4 kmol m -3 with three (or four) molar amine ratios. The corresponding mutual diffusion coefficients of aqueous DEA and aqueous MDEA solutions were also measured. Working equations for the ternary diffusion coefficients presented by Leaist et al. (998) was adopted to obtain the ternary diffusion coefficients. The main diffusion coefficients (D and D ) and the cross coefficients (D and D ) are reported as function of temperature and concentration of alkanolamines. The dependence of D ij on temperature, concentration, and viscosity of solutions were discussed. The predicted values from the Onsager phenomenological coefficients, the activity, and partial molar volume of component are also performed and compared with the measured values. Keywords: ternary diffusion coefficient, aqueous blended amines solutions, carbon dioxide capture, Taylor dispersion technique. Introduction A wide variety of alkanolamines, such as monoethanolamine (MEA), diglycolamine (DGA), diethanolamine (DEA), di-isopropanolamine (DIPA), N- methyldiethanolamine (MDEA), triethanolamine (TEA), -amino--methyl-lpropanol (AMP), and -piperidineethanol (-PE), can be used as absorbents for the removal of CO and H S from gas streams in the natural gas, petroleum chemical plants, and ammonia industries (Kohl and Nielsen, 997).

P. H. Lin et al. Diffusion coefficients, viscosity, and density are thermophysical properties and are needed in the evaluation of mass transport properties. The rate of molecular diffusion in liquid is normally the rate-determining factor in unit operations, such as the absorption of acid gases in alkanolamine solutions and heterogeneous gas-liquid chemical reactions. Diffusion coefficients are also useful for investigating the structure of liquids and for developing theories of liquid states (Tyrrell and Harris, 984). The mutual diffusion coefficients in aqueous alkanolamine solutions have been reported in the literature such as MEA, MIPA (monoisopropanolamine), DEA, DIPA, DGA, EDA (ethylenediamine) and TEA (Hikita et al., 98; Hikita et al., 98); MEA, DEA, MDEA, and DIPA (Snijder et al., 993); MDEA (Rowley et al., 997); TEA (Leaist et al., 998); DGA, TEA, AMP, and -PE (Chang et al., 5); DMEA (N,N-dimethylethanolamine), DEEA (N,N-diethylethanolamine), MIPA (monoisopropanolamine), PZ (piperazine) and sulfolane (Kao and Li, 6). The Taylor dispersion technique had been used frequently for measuring binary diffusion coefficients of various solutions (Taylor, 953; Alizadeh et al., 98; Baldauf and Knapp, 983; Leaist et al., 998). In the Taylor experiment a narrow band of solution is injected into a laminar carrier stream of different composition which flows in a long capillary tube. The injected solutes spread out as they flow along the tube. A differential refractometer monitors the broadened distribution of dispersed solutes as they flow out of the tube. The Taylor dispersion technique for measuring binary diffusion was extended to three- and four-component systems (Deng and Leaist, 99). Ternary diffusion coefficients in liquids reported in the literature were catalogued into four classes of systems, electrolytes (e.g., LiCl-NaClwater), electrolyte-non-electrolyte mixtures (e.g., KCl-glycine-water), nonelectrolytes in water (glycine sucrose - water), and organic liquids (e.g., acetonebenzene-cyclohexane) (Cussler, 976). Employing the advantages of each amine, the aqueous blended amines have been proposed to be used for acid gases removal in the absorption processes (Chakravarty et al., 985). Blended amines such as MEA + MDEA + H O, MEA + AMP+ H O have been suggested for acid gases removal (Kohl and Nielsen, 997). Some thermophysical properties such as density, viscosity, Henry s constant, diffusivity of a gas in liquid, and reaction kinetics data for the CO absorption into aqueous blended alkanolamine have been reported in the literature. The ternary mutual diffusivity coefficients of MEA + MDEA + H O were reported using the Taylor dispersion technique (Ko et al., 6). However, the ternary mutual diffusivity coefficient of DEA + MDEA + H O has not yet been reported in the literature. Thus, it is the objective of this research to measure the ternary mutual diffusivity coefficients in DEA + MDEA + H O systems.. Experimental Chemicals. DEA is Riedel-de Haën reagent grade with purity of 99 mol % and MDEA is Riedel-de Haën reagent grade with purity 98.5 mol %. A water purification system (the Barnstead EASYpure LF) is used to provide Type I reagentgrade water with a resistivity of up to 8.3 MΩ-cm and with a total organic carbon

Measurements of Ternary Diffusion Coefficients of Aqueous Blended Alkanolamine systems: Diethanolamine + N-methyldiethanolamine + Water 3 content of less than 5 ppb. The prepared aqueous alkanolamines solutions have been degassed by using ultrasonic cleaner (Branson, Model 35). The ternary mutual diffusion coefficients of DEA + MDEA + H O were measured in a Taylor dispersion apparatus. The experimental setup is the same as described in (Chang et al., 5). For ternary mutual diffusion measurements, the concentration of the injected solution is different from those of the binary system and will be described briefly. A metering pump was used to provide constant laminar flow at a rate of.8. ml/min. A pulse damper was installed downstream of the pump to reduce any pressure fluctuation from the pump. The carrier fluid flows through a six-port injection value (Rheodyne, Model 775i) at the upstream of the diffusion coil and then flows into a 36-stainless steel diffusion tube which was maintained at a constant temperature water bath with a thermometer (Hart Scientific model 5) with an accuracy of ±. K monitoring the temperature of the bath. The length of the tube is 5.8 m with an internal radius of.68 mm and is horizontally tempered in a cm coil radius. By switching a 6-way injection valve, a δ function pulse of μl of concentration profile is introduced into the carrier fluid. The injected pulse of the solute usually consists of a solution with small concentration (Δc + Δc ) greater than that of the carrier fluid. Dispersion of the pulse was established through the parabolic velocity profile of the laminar flow. The initial concentration differences (Δc, Δc ) were typically.5 mol dm -3. A few runs were made with concentration differences one-half as large, as suggested by Deng and Leaist (Deng and Leaist, 99). Since the results did not differ significantly, the measured diffusion coefficients can be interpreted as differential values at the composition of the carrier stream (c, c ). To prevent the secondary flows in a helical coil, the flow rate was controlled at.8-. ml/min to assure the validity of the condition De Sc, as suggested by Alizadeh et al. (98). The solvent reservoir and the capillary are temperature controlled by a thermostat. Between the six-way valve and the refractive index detector, the tube outsides the water bath was kept as short as possible and wrapped up well with heatinsulated materials. At the end of capillary, the concentration gradient was determined by a differential refractometer (Precision Instruments, IOTA ) with a cell volume of 8 μl. The instrument contains two cells: the sample cell and the reference cell. The instrument detects the difference in concentration between the sample and reference cell. The analog output was transferred to a computer system by an integrating converter INT5 (DataApex, Chromatography Station, CSW.7). In the data analysis system, the detector signal is collected and plotted as function of time. A least squared procedure (Deng and Leaist, 99) is applied to determine the ternary mutual diffusion coefficients. The working equation and the calculation procedure are described in the next section. The standard deviation of the D ik values, ±. -9 m s -, was estimated by repeating 3-5 sets of replicate runs. 3. Working equations for determination of ternary mutual diffusion coefficients Deng and Leaist (99) developed a simple least-squares procedure to calculate the ternary diffusion coefficients from the refractive index profiles. The working 3

P. H. Lin et al. equations, representing the detector signal, to calculate ternary diffusion coefficients are as follows, t R D () ( t t ) R D ( ) ( t t ) R v t vmax W exp W exp = + B + Bt t + r t r t () where v max is the height of the eluted solute peak relative to the baseline, t R the mean retention time, r the inner radius, B the baseline detector voltage, B t is representing a small linear drifts in the baseline signal. D and D denote two overlapping Gaussians, centered on time t R with variances r L / 4DU and r L / 4DU where L is the length of the tube, U the mean speed of stream. In eq, W and ( - W ) give the normalized weights of the exponential terms and are expressed in terms of a, b, D, and D as follows, W = ( a + bα ) D ( a + bα ) D + ( a bα ) D The parameters a and b are constants for a given system and carrier stream composition (Deng and Leaist, 99). In eq, α is the fraction of the initial refractive index contributed by solute : ( R Δc + R Δ ) α (3) = RΔc / c where Δc and Δc are injected solution concentration ( c +Δc, c +Δc ) difference to the concentration ( c, c ) of the carrier stream. In eq 3, R and R are the molar refractivities of the solutes, dn R i = (4) dc i where n is the refractive index profile. The value of R i is evaluated at the carrier stream composition, c i. For each solution stream with solutes concentration ( c, c ), 6 to injected solutions with various values of α were performed. As mentioned by Deng and Leaist (99), the values of α are widely separated, such as. and. rather than.4 and.6. The values of v max, B, B, a, b, D, and D are determined by a leastsquare method. After the values of a, b, D, and D determined from the refractive index profile for solution stream with solutes concentration ( c, c ), the ternary mutual diffusion coefficients can be calculated from the following equations (Deng and Leaist, 99): D ( a b) ( D D ) a = D + (5) b () 4

Measurements of Ternary Diffusion Coefficients of Aqueous Blended Alkanolamine systems: Diethanolamine + N-methyldiethanolamine + Water 5 R a D = ( a)( D D ) (6) R b D D R ( a + b)( a b) ( D D ) = (7) R b ( a b) ( D D ) a = D + (8) b where D ii is the main diffusion coefficient and D ij the cross diffusion coefficient. 4. Results and Discussion To test the accuracy of the apparatus, the mutual diffusion coefficients of DEA () + water were measured at. kmol m -3 and atmospheric pressure. The measured mutual diffusion coefficients of DEA () + water were.6 ±.,.76 ±.5,.969 ±.5,.9 ±.5, and.476 ±.6-9 m s - for 3, 4, 5, 6, and 7 o C, respectively. The standard deviation was obtained from 4 to 6 replicated runs. A comparison between the measured mutual diffusion coefficients and the literature values (Hikita et al., 98; Snijder et al., 993) for this system is shown in Figure. In Figure, the concentration of the data of Hikita et al. was at. kmol m -3 while the data of Snijder et al. was at. kmol m -3. The solid line in Figure was calculated using the correlation presented by Snijder et al. (993). As shown in Figure, the obtained mutual diffusion coefficients of DEA () + water are in good agreement with literature values. The ternary mutual diffusion coefficients of MgCl () + MgSO 4 () + H O for a total salt concentration of.4 kmol m -3 at 5 o C were also measured. The results are presented in Table. A comparison of the results is shown in Figure. The four mutual diffusion coefficients, D, D, D, D are generally in good agreement with the data of Deng and Leaist (99). The x-axis coordinate in Figure is relative molar ratio of amines and is defined as f c = (9) ( c + c ) where c and c are concentrations of the carrier stream. The ternary mutual diffusion coefficients of DEA () + MDEA () + H O for a total amine concentration of.5 kmol m -3 for temperatures 3, 35, 4 o C are presented in Table. The corresponding mutual diffusion coefficients in binary systems were also performed and are also presented in Table. The plot of ternary mutual diffusion coefficients vs. the relative concentration of solutes at 4 o C is shown in Figure 3. In Figure 3, the binary mutual diffusion coefficients calculated from the equation of Snijder et al. (993) are also shown for the purpose of comparison. 5

P. H. Lin et al. 3 DEA () + H O 9 D ik /(m s - ).8 3. 3. 3.4 /T (K) Figure : Mutual diffusion coefficients of aqueous DEA (. kmol m -3 ) solution., data of Snijder et al. (993); data of Hikita et al. (98) at. kmol m -3 ;, this study; solid line, calculated using equation of Snijder et al. (993) Table : Ternary diffusion coefficients of MgCl () + MgSO 4 () + H O for a total salt concentration of.4 kmol m -3 at 5 o C Conc./(kmol m -3 ) 9 D ij /( m s - ) c c D D D D R /R.4.468.473*..3.7 -.63 -.39.5.99.39* -.* -.46*.54*.98*...84 -.3 -..539.96.5* -.3* -.4*.6*.98*.3..8.5 -..593.5.4* -.8* -.7*.65*.98*.4.87.83* * Data of Deng and Leaist (99) 6

Measurements of Ternary Diffusion Coefficients of Aqueous Blended Alkanolamine systems: Diethanolamine + N-methyldiethanolamine + Water 7 3 Data of Deng and Leaist (99) D D D D This study D D D D 9 D ik /(m s - ) -..5. f Figure : Ternary mutual diffusion coefficients of MgCl () + MgSO4 () + H O at a total salt concentration of.4 kmol m -3 and 5 o C Table : Ternary diffusion coefficient of DEA () + MDEA () + H O for a total amine concentration of.5 kmol m -3 Conc./(kmol m -3 ) 9 Dij/(m s - ) t/ o C 3 4 5 c c D D D D.5.469.5..459 -.68.4.498..5.466 -.73.4.5.5..467 -.9.8.53..5.475 -.4..548.5.548.5.586.5..554 -..8.6..5.66 -.3..7.5..66 -.9..74..5.64 -.37..7.5.7.5.739.5..768 -...798..5.796 -.9.7.854.5..758 -.5 -.7.854..5.779 -.36.7.877.5.878 7

P. H. Lin et al. DEA () + MDEA () + H O at.5 kmol m -3 and 4 o C 9 D ik /(m s - ) -..5. f Figure 3: Ternary diffusion coefficients of DEA () + MDEA () + H O solutions at a total concentration of.5 kmol m -3 and 4 o C., D ;, D ;, D ;, D ; Solid lines: smoothed values. Binary values of D and D :,, calculated from eq of Snijder et al. (993) At the limiting condition of f (i.e., c ), the main mutual diffusion coefficient D approaches the binary value for DEA + H O, as shown in Figure 3. In this limit, D, the diffusion of MDEA due to the concentration gradient of DEA, vanishes because the gradient in DEA cannot produce a coupled flow of MDEA if the solution is free of MDEA, as shown in Figure 3. Similarly, as f (i.e., c ), the D is approaching the binary diffusion value in MDEA + H O; D vanishes due to free of DEA in solution, as shown in Figure 3. The ratio of D to D varies from -.3 to -.9 while the ratio of D to D about.3 to.. Thus, for DEA the cross diffusion effect due to the concentration gradient of MDEA is larger than that for MDEA due to the concentration gradient of DEA. In Figure 4, the main diffusion coefficients D of DEA () + MDEA () + H O solutions as function of temperatures at a total of.5 kmol m -3 are shown. As shown in Figure 4, D increases as the temperature increase at the same molar ratio; D increases as the molar ratio increases at the same temperature. The main diffusion coefficients D of DEA () + MDEA () + H O solutions as function of temperatures at a total of.5 kmol m -3 are shown in Figure 5. Similarly, D increases as the temperature increase at the same molar ratio; D increases as the molar ratio increases at the same temperature. 8

Measurements of Ternary Diffusion Coefficients of Aqueous Blended Alkanolamine systems: Diethanolamine + N-methyldiethanolamine + Water 9 9 D ik /(m s - ) DEA () + MDEA () + H O.5 kmol m -3 D, 3 o C D, 4 o C D, 5 o C..5. f Figure 4: Comparison of main diffusion coefficients (D ) of aqueous DEA + MDEA solutions at different temperatures.,, : calculated using eq of Snijder et al. (993) 9 D ik /(m s - ) DEA () + MDEA () + H O.5 kmol m 3 D, 3 o C D, 4 o C D, 5 o C..5. f Figure 5: Comparison of main diffusion coefficients (D ) of aqueous DEA + MDEA solutions at different temperatures.,, : calculated using eq of Snijder et al. (993) The ternary mutual diffusion coefficients of DEA () + MDEA () + H O for temperatures 3, 35, 4 o C are presented in Tables 3, 4, and 5, for a total amine 9

P. H. Lin et al. concentrations of 3., 3.5, and 4. kmol m -3, respectively. The dependence of the ternary mutual coefficients on the temperature and molar ratio of amine is similar as in total amine concentration of.5 kmol m -3 solution. Table 3: Ternary diffusion coefficient of DEA () + MDEA () + H O for a total amine concentration of 3. kmol m -3 Conc./(kmol m -3 ) 9 Dij/(m s - ) t/ o C 3 4 5 c c D D D D 3..4.5.5.33 -.4.84.43...378 -.38.9.55...44 -.7.9.545.5.5.46 -.79.7.545 3..496 3..586.5.5.56 -.9.4.64...57 -.4.3.639...53 -.55.3.65.5.5.55 -.7..673 3..647 3..65.5.5.68 -.78..683...67 -.46..753...677 -.8 -.8.8.5.5.696 -.7.6.8 3..795 Table 4: Ternary diffusion coefficient of DEA () + MDEA () + H O for a total amine concentration of 3.5 kmol m -3 Conc./(kmol m -3 ) 9 Dij/(m s - ) t/ o C 3 4 5 c c D D D D 3.5.369..5.335 -.97.6.436.5..354 -..4.457..5.356 -.4.9.45.5..48 -.3.5.46 3..465 3.5.47..5.456 -.66.6.496.5..46 -.58.7.54..5.465 -.6.33.6.5..479 -.7.9.6 3..59 3.5.65..5.6 -.77.4.658.5..68 -.99.9.689..5.643 -.5 -..755.5..666 -.36.5.757 3..738

Measurements of Ternary Diffusion Coefficients of Aqueous Blended Alkanolamine systems: Diethanolamine + N-methyldiethanolamine + Water Table 5: Ternary diffusion coefficient of DEA () + MDEA () + H O for a total amine concentration of 4. kmol m -3 Conc./(kmol m -3 ) 9 Dij/(m s - ) t/ o C 3 4 5 c c D D D D 4..34. 3..3 -.95.3.4.5.5. -.37.46.37.5.5.33 -.4.43.389 3...66 -.4.3.4 4..4 4..47. 3..7 -.4.9.47.5.5.89 -.5.6.44.5.5.34 -.53.3.46 3...36 -.98.36.53 4..59 4..5. 3..44 -.3.8.549.5.5.478 -.45.5.57.5.5.495 -.49 -.9.6 3...53 -.58.6.63 4..669 DEA () + MDEA () + H O 3 o C 9 D ik /(m s - ) D,.5 kmol m 3 D, 3. kmol m 3 D, 3.5 kmol m 3 D, 4. kmol m 3..5. f Figure 6: Comparison of main diffusion coefficients (D ) of DEA () + MDEA () + H O solutions at different concentrations. Lines: smoothed;,,, : calculated using eq of Snijder et al. (993) At 3 o C, the plot of D as function of various total amine concentration is shown in Figure 6. As shown in Figure 6, at the same amine molar ratio D decreases as the

P. H. Lin et al. total amine concentration increases which are the same behavior as for the binary mutual diffusion coefficient. The plot of D as function of various total amine concentration at 3 o C is shown in Figure 7. As shown in Figure 7, at the same amine molar ratio D decreases as the total amine concentration increases which are the same behavior as D. DEA () + MDEA () + H O 3 o C D,.5 kmol m-3 9 D ik /(m s - ) D, 3. kmol m-3 D, 3.5 kmol m -3 D, 4. kmol m -3..5. f Figure 7: Comparison of main diffusion coefficients (D ) of DEA () + MDEA () + H O solutions at different concentrations. Lines: smoothed;,,, : calculated using eq of Snijder et al. (993) DEA () + MDEA () + H O 3. kmol m -3 and 3 o C 9 D ik /(m s - ) D D.3... ln μ (mpa s) Figure 8: Main diffusion coefficients of aqueous DEA + MDEA solutions as functions of viscosity of solutions

Measurements of Ternary Diffusion Coefficients of Aqueous Blended Alkanolamine systems: Diethanolamine + N-methyldiethanolamine + Water 3 In the stokes-einstein equation, large spherical molecules diffusing into a dilute solution, the diffusion coefficients may proportional to the reciprocal of the viscosity of solvent. In Figure 8, the main diffusion coefficients, D and D, are plotted as function of viscosities of solutions. As shown in Figure 8, both of D and D decrease as the viscosity of solution increases. When ternary diffusion coefficients in liquids are not available, one can make estimates by assuming that the Onsager phenomenological coefficients are a diagonal matrix and the main-term coefficients are related to the binary values (Cussler, 984). The ternary diffusion coefficients in liquids can be calculated from the binary diffusion coefficients and the activity coefficients as follows, D ij n Dc i i cv l i μ l = δil + l= RT cnv n c () j ck j, n where D i is the mutual diffusion coefficient of binary system, Vi is the partial molar volume, δ il is Kronecker delta, for i = l, δ il =,i l, δ il =. The partial molar volume can be calculated as follows (Leaist and Kanakos, ), V i ρ M i ci = ρ ρ c c c ρ c The densities of DEA () + MDEA () + H O were calculated from the correlation of Hsu and Li (997). The partial molar volume of water is calculated from the following equation (Leaist and Kanakos, ), 3 3 cm dm cv cv cv 3 3 () = + + () In equation, the activity can be calculated from the activity coefficient and the mole fraction of component. The activity coefficients of amines are calculated from the UNIFAC model using the computer program of Sandler (6). The calculated partial molar volumes and the activities are listed in Table 6. The predicted results from eqs for ternary diffusion coefficients for DEA () + MDEA () + H O at a total of.5 kmol m -3 and at 5 o C as function of molar ratios of amine are shown in Figure 9. In Figure 9, the dotted lines denote the predicted values. Except for D, the predicted values for D, D, D are generally follows the trend of the experimental values. The abnormal behavior of predicated D may due to the activity coefficient prediction from the UNIFAC model. Nevertheless, as pointed out by Cussler (984) that the predicted values from equation can usually provide initial estimates values. Thus, we would not expect that accurate ternary diffusion coefficients can be obtained from eq. 3

P. H. Lin et al. Table 6: Calculations of partial molar volumes and activities at 3 o C used in eqs to c i (kmol m -3 ) c c V V 3 3-3 - 3 - (cm mol ) (cm mol ) (cm mol ) dc c V dln a dln a dln a dln a dc dc c dc c c.5. 93.97 9. 8.36 -.6.84.96 -.79..5 93.757 9.45 8.39 -.37.438.897 -.6.5. 93.49 9.86 8.3 -.46.76.588 -.7..5 93.4 9.45 8.79 -.33.8.378 -.87.5.5 93.94 9.84 8.454 -.95.7.984 -.8.. 93.74 9.7 8.49 -.93.36.944 -.7.. 93.33 9.4 8.359 -..84.43 -.3.5.5 93.7 9.6 8.348 -.3.83.338 -...5 93.8 9.9 8.5 -.48.66.97 -.89.5. 93.634 9. 8.48 -.65.339.634 -.94..5 93.38 9.76 8.45 -.56.57.465 -.97.5. 93.73 9.86 8.437 -.59.85.354 -.4. 3. 93.785 9.6 8.645 -.6.5.6 -.53.5.5 93.698 9.77 8.597 -.3.37.66 -.65.5.5 93.8 9.433 8.54 -.3.546.386 -.97 3.. 9.839 9.466 8.53 -.45.858.34 -.7 4

Measurements of Ternary Diffusion Coefficients of Aqueous Blended Alkanolamine systems: Diethanolamine + N-methyldiethanolamine + Water 5 DEA () + MDEA () + H O.5 kmol m -3 and 3 o C 9 D ik (m )s - ) -..5. f Figure 9: Ternary mutual diffusion coefficients of aqueous DEA () + MDEA () + H O solutions as functions of the relative DEA concentration at a total solute concentration.5 kmol m -3 and 3 o C., D ;, D ;, D ;, D ; lines: smoothed;, : calculated using eq of Snijder et al. (993). Dashed lines: calculated D ik using eq 5. Conclusion Ternary diffusion coefficients of aqueous blended alkanolamine systems diethanolamine (DEA) + N-methyldiethanolamine (MDEA) + water using the Taylor dispersion technique have been measured for temperatures 3, 4 and 5 o C. The systems studied were aqueous solutions containing the total amine concentrations of, 3, and 4 kmol m -3 with three (or four) molar amine ratios. For a DEA + MDEA + water system, D was found to be increase as the temperature and the molar ratio increase. Both of D and D decrease as the viscosity of solution increases. The ratio of D to D varies from -.3 to -.9 while the ratio of D to D about.3 to.. Thus, for DEA the cross diffusion effect due to the concentration gradient of MDEA is larger than that for MDEA due to the concentration gradient of DEA. The predicted values from the Onsager phenomenological coefficients, the activity, and partial molar volume of component are generally follows the trend of the experimental values. The predicted values can usually provide good initial estimates values. References Alizadeh, A., Nieto de Castro, C. A., and Wakeham, W. A., (98). Int. J. Thermophys.,, 43-84. Baldauf, W. and Knapp, H., (983). Chem. Eng. Sci., 38, 3-37. Chakravarty, T., Phukan, U. K., and Weiland, R. H., (985). Chem. Eng. Prog., 8, 3-36. Chang, L.-C., Lin, T.-I., and Li, M.-H., (5). Journal of Chemical and Engineering Data, 5, 77-84. Cussler, E. L., Multicomponent diffusion, Elsevier, Amsterdam (976). Cussler, E. L., Diffusion, Mass transfer in fluid system, Cambridge University Press, New York (984). Deng, Z. and Leaist, D. G., (99). Can. J. Chem. Eng., 69, 548-553. Hikita, H., Ishihawa, H., Uku, K., and Murakami, T., (98). J. Chem. Eng. Data, 5, 34-35. Hikita, H., Ishikawe, H., Murakaml, T., and Ishii, T. J., (98). J. Chem. Eng. Japan 4, 4-43. Hsu, C. H. and Li, M. H., (997). J. Chem. Eng. Data, 4, 5-57. Kao, C.-Z. and Li, M.-H., (6). J. Chin. Inst. Chem. Engrs., 37, 34-353. 5

P. H. Lin et al. Ko, C.-C., Lin, P.-H., and Li, M.-H. (6). "Measurements of Ternary Diffusion Coefficients of Aqueous Blended Alkanolamine systems: Monoethanolamine + N-methyldiethanolamine + Water." 7th International Congress of Chemical and Progress Engineering, Prague - Czech Republic, August 7-3. Kohl, A. L. and Nielsen, R. B., Gas Purification, Gulf, Houston (997). Leaist, D. G. and Kanakos, M. A., (). Phys. Chem. Chem. Phys.,, 5-. Leaist, D. G., Li, Y., and Poissant, R., (998). J. Chem. Eng. Data, 43, 48-55. Rowley, R. L., et al., (997). J. Chem. Eng. Data, 4, 3-37. Sandler, S. I., Chemical, Biochemical and Engineering Thermodynamics, John Wiley & Sons Inc., New York (6). Snijder, E. D., Riele, M. J. M. t., Versteeg, G. F., and Swaaij, W. P. M. v., (993). J. Chem. Eng. Data, 38, 475-48. Taylor, F. R. S., (953). Proc. R. Soc. London, A9, 86-3. Tyrrell, H. J. V. and Harris, K. R., Diffusion in Liquids, Butterworth, London (984). 6