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Sorption isotherms analysis

Gibbs free energies of water sorption, AG "(/l), can be extracted from isopiestic vapor sorption isotherms this analysis shows that AG (T) < AG", where AG" = -44.7 kj moH is the Gibbs free energy for vapor sorption at a free water surface at ambient condihons. Water absorbed by the membrane is therefore more strongly bound than water at a free bulk water surface this affirms the hydrophilic nature of water sorption in PEMs. [Pg.371]

Sorption Analysis. Specific surface areas and porosity can be calculated from the adsorption isotherm of nitrogen at — 196 °C. The method of Brunauer, Emmett, and Teller [4.29] is generally accepted for the evaluation of specific surface areas (BET surface area in square meters per gram). The two-parameter equation is applicable to carbon black. The BET surface area comprises the outer surface area as well as the surface area of the pores. [Pg.163]

The importance of adsorbent non-isothermality during the measurement of sorption kinetics has been recognized in recent years. Several mathematical models to describe the non-isothermal sorption kinetics have been formulated [1-9]. Of particular interest are the models describing the uptake during a differential sorption test because they provide relatively simple analytical solutions for data analysis [6-9]. These models assume that mass transfer can be described by the Fickian diffusion model and heat transfer from the solid is controlled by a film resistance outside the adsorbent particle. Diffusion of adsorbed molecules inside the adsorbent and gas diffusion in the interparticle voids have been considered as the controlling mechanism for mass transfer. [Pg.175]

Hageman et al. [3.13] calculated the absorption isotherms for recombinant bovine somatotropin (rbSt) and found 5-8 g of water in 100 g of protein, which was not only on the surface but also inside the protein molecule. Costantino et al. [3.72] estimated the water monolayer M0 (g/100 g dry protein) for various pharmaceutical proteins and for their combination with 50 wt% trehalose or mannitol as excipient. They compared three methods of calculating MQ (1) theoretical (th) from the strongly water binding residues, (2) from conventional adsorption isotherm measurements (ai) and (3) from gravimetric sorption analysis (gsa) performed with a microbalance in a humidity-controlled atmosphere. Table 3.5 summarizes the results for three proteins. The methods described can be helpful for evaluating RM data in protein formulations. [Pg.305]

Time Beach soilAvater with 0.01% surfactant from Missouri at pH 4, 7, 8.5, Puri et al. 1989) 5.70, 5.09, 4.76 (Visalia soilAvater with 0.01% surfactant from California at pH 4, 7, 8.5, Puri et al. 1989) 6.44, 6.66 (batch equilibrium-sorption isotherms 2-d, 10-d isotherm, regression analysis for sorption of uncontaminated Time Beach soil from water, Walters et al. 1989)... [Pg.1199]

The pore network connectivity is usually determined by gas sorption analysis [2-4] or mercury intrusion [5] based on percolation theory. Recently, Ismadji and Bhatia [6] have successfully employed the liquid phase adsorption isotherms to determine the pore network connectivity and the pore size distribution of three commercial activated carbons. In our recent study [7], the pore network connectivity of three commercial activated carbons was characterized using liquid phase adsorption isotherms of eight different compounds. In that study we used ester molecules with complex structure, as probe molecules. [Pg.123]

Two Independent methods have been utilized to examine the nature of the sorption Isotherm. An analysis of the experimental Isotherm compared to an extrapolation of the Infinite dilution behavior allows calculation of an enhancement number for any of the polymers at any given partial pressure. Calculation of a cluster number based on an Independent method shows very close concordance with the enhancement ntimber, providing strong support for the postulate that associated groups of water molecules sorb In the polymer, and account for the anomolous sorption. [Pg.447]

Comment. Gas sorption analysis is a well-established tool for the characterization of open porous solids. For aerogels the method provides reliable information on the surface area. However, care has to be taken in case of microporous aerogels here a well-equilibrated isotherm in combinatiOTi with the right choice of the evaluation range will still yield reliable values for the microporosity and the specific surface area. For detailed analysis of microporosity measurements with CO2 at 273 K are recommended. [Pg.482]

This definition, it should be noted, is somewhat in conflict with the definition of nanoscale objects, which typically have large relative porosities (> 0.4), and pore diameters between 1 and 100 nm. In order to classify porous materials according to the size of their pores the sorption analysis is one of the tools often used. This tool is based on the fact that pores of different sizes lead to totally different characteristics in sorption isotherms. The correlation between the vapor pressure and the pore size can be written as the Kelvin equation ... [Pg.178]

Gravimetric vapour sorption analysis Raman spectroscopy X-ray diffraction Intrinsic solubility Isothermal microcalorimetry... [Pg.287]

Experiments Sorption equihbria are measured using apparatuses and methods classified as volumetric, gravimetric, flow-through (frontal analysis), and chromatographic. Apparatuses are discussed by Yang (gen. refs.). Heats of adsorption can be determined from isotherms measured at different temperatures or measured independently by calorimetric methods. [Pg.1504]

Loukidou et al. (2005) fitted the data for the equilibrium sorption of Cd from aqueous solutions by Aeromonas caviae to the Langmuir and Freundlich isotherms. They also conducted, a detailed analysis of sorption rates to validate several kinetic models. A suitable kinetic equation was derived, assuming that biosorption is chemically controlled. The so-called pseudo second-order rate expression could satisfactorily describe the experimental data. The adsorption data of Zn on soil bacterium Pseudomonas putida were fit with the van Bemmelen-Freundlich model (Toner et al. 2005). [Pg.86]

Duplessix et al. used water vapor pressure isotherm (i.e., water uptake vs external relative humidity) data combined with simultaneous isotherm differential microcalorimeter analysis to determine the average heat of absorption per water molecule for 1200 EW acid form samples. Hysteresis was seen between sorption and subsequent desorption curves at 25 °C, and nonzero water content remained at zero relative humidity, indicating the presence of tightly... [Pg.320]

Still, this theory is over-simplified, and holds only for a limited part of the sorption isotherm, which is usually the case for relative pressures between 0.05-0.30, and the presence of point B (Fig. 1.14). Thus, isotherms of Types II (macroporous polymer supports) and IV (mesoporous polymer supports), but not Type I and III, are those amenable to BET analysis [21, 80]. Attention should also be paid to the constant C, which is exponentially related to the enthalpy of adsorption of the first layer. A negative or high value of C exceeding 200-300, is likely to indicate the presence of micropores and the calculated surface area should be questioned since the BFT theory would not be applicable [79, 80]. [Pg.21]

Contact angle measurements Isothermal microcalorimetry Gravimetric sorption Inverse gas chromatography Differential scanning calorimetry Thermogravimetric analysis Isothermal microcalorimetry Infra red analysis X-ray diffraction... [Pg.69]

Frontal analysis brings with it the requirement of the system to have convex isotherms (see Section 1.2.6). This results in the peaks having sharp fronts and well-formed steps. An inspection of Figure 1.3 reflects the problem of analytical frontal analysis— it is difficult to calculate initial concentrations in the sample. One can, however, determine the number of components present in the sample. If the isotherms are linear, the zones may be diffuse. This may be caused by three important processes inhomogeneity of the packing, large diffusion effects, and nonattainment of sorption equilibrium. [Pg.6]

For a resolution of question (3), either MASC or the simpler SSHTZ program was run under both isothermal and adiabatic conditions, with effective mass transfer coefficients chosen to simulate the stable portion of the sorption fronts. Fortunately, in most cases described below, the programs predicted that the steady-state MTZ lengths did not change by more than 10Z or so between the two extremes. Thus, an extensive analysis of the wall effects in the various columns was not required for proper interpretation of MTZ data. [Pg.86]

The assumption of equilibrium sorption has been supported by the long anticipated residence times in an installed barrier (e.g., days for a barrier thickness of 1-2 m), and by batch kinetic data reported by Cantrell (1996) that indicate near-equilibrium is achieved on the order of one day. Similar assumptions have been applied to the analysis of GAC barriers (e.g., Schad and Gratwohl, 1998). Cantrell (1996) also observed linear isotherms for Sr concentrations below approximately 0.1 mg/L, although this result should be viewed as particular to the specific experimental conditions. Although these results lend support to the simplified modeling approach, more data are clearly needed to better evaluate the key assumption of linear equilibrium sorption. [Pg.128]

The grain size distributions of the two batches of SMZ were determined by sieve analysis. Chromate and PCE sorption isotherms for each batch of SMZ were prepared using methods described earlier (Li and Bowman 1997 Li and Bowman 1998). [Pg.171]

Surfactant equilibrium isotherms and sorption envelopes on kaolinite were determined in triplicate batch experiments for the appropriate solution chemistry conditions. After equilibration, the solids were separated by centrifugation at 7000 rpm for 30 min and aliquots of the supernatant were taken for analysis. Residual SDS and Tween 80 concentrations (Ssurf, mM) were determined after taking into account dilution factors and system losses,... [Pg.190]


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See also in sourсe #XX -- [ Pg.9 ]




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