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Freundlich isotherm parameters constant

Figure 4 Comparison of sorption models. Several commonly used sorption models are compared with respect to the independent constants they require. These constants are vahd only under specific conditions, which must be specified in order to properly use them. In other words, the constants are conditional with respect to the experimental variables described in the third column of the figure. is the radionuclide distribution constant K and n are the Freundlich isotherm parameters and are surface complexation constants for protonation and deprotonation of surface sites K-, are surface complexation constants for sorption of cations and anions in the constant... Figure 4 Comparison of sorption models. Several commonly used sorption models are compared with respect to the independent constants they require. These constants are vahd only under specific conditions, which must be specified in order to properly use them. In other words, the constants are conditional with respect to the experimental variables described in the third column of the figure. is the radionuclide distribution constant K and n are the Freundlich isotherm parameters and are surface complexation constants for protonation and deprotonation of surface sites K-, are surface complexation constants for sorption of cations and anions in the constant...
Figure 4 Comparison of sorption models. Several commonly used sorption models are compared with respect to the independent constants they require. These constants are valid only under spedlic conditions, which must he specified in order to properly use them. In other words, the constants are conditional with respect to the experimental variables described in the third column of the figure. is the radionuclide distrihution constant K and n are the Freundlich isotherm parameters and f3 are surface complexation constants for protonation and deprotonation of surface sites K, K-, 13, are surface complexation constants for sorption of cations and anions in the constant capacitance model and TLM, respectively C, Ci, and are capacitances for the electrical double layers rr, ov, and oj, are surface charges at different surface planes (Me) and (S) are concentrations of the sorbing ions and the surface sites, (M), (L) are concentrations of other cations and ligands in solution, respectively I is the ionic strength of the background electrolyte and 5a are the site density and specific surface of the substrate, respectively. The requirements of the DLM are similar to those of the constant capacitance model. Figure 4 Comparison of sorption models. Several commonly used sorption models are compared with respect to the independent constants they require. These constants are valid only under spedlic conditions, which must he specified in order to properly use them. In other words, the constants are conditional with respect to the experimental variables described in the third column of the figure. is the radionuclide distrihution constant K and n are the Freundlich isotherm parameters and f3 are surface complexation constants for protonation and deprotonation of surface sites K, K-, 13, are surface complexation constants for sorption of cations and anions in the constant capacitance model and TLM, respectively C, Ci, and are capacitances for the electrical double layers rr, ov, and oj, are surface charges at different surface planes (Me) and (S) are concentrations of the sorbing ions and the surface sites, (M), (L) are concentrations of other cations and ligands in solution, respectively I is the ionic strength of the background electrolyte and 5a are the site density and specific surface of the substrate, respectively. The requirements of the DLM are similar to those of the constant capacitance model.
The Langmuir equation has a strong theoretical basis, whereas the Freundlich equation is an almost purely empirical formulation because the coefficient N has embedded in it a number of thermodynamic parameters that cannot easily be measured independently.120 These two nonlinear isotherm equations have most of the same problems discussed earlier in relation to the distribution-coefficient equation. All parameters except adsorbent concentration C must be held constant when measuring Freundlich isotherms, and significant changes in environmental parameters, which would be expected at different times and locations in the deep-well environment, are very likely to result in large changes in the empirical constants. [Pg.830]

Because the equations are for straight lines, only two pairs of values of the respective parameters are required to solve the constants. For the Freundlich isotherm, the required pairs of values are the parameters ln(XIM) and ln[C for the Langmuir isotherm, the required pairs are the parameters C]I(XIM) and [C]. [Pg.409]

The above surface complexation models enable adsorption to be related to such parameters as the number of reactive sites available on the oxide surface, the intrinsic, ionization constants for each type of surface site (see Chap. 10), the capacitance and the binding constants for the adsorbed species. They, therefore, produce adsorption isotherms with a sounder physical basis than do empirical equations such as the Freundlich equation. However, owing to differences in the choice of adjustable... [Pg.257]

Using the techniques of analytic geometry, let us derive the Freundlich constants in a little more detail than used in the derivation of the constants in the discussion of reverse osmosis treated previously. As mentioned, the straight-line form of the equation requires only two experimental data points however, experiments are normally conducted to produce not just two pair of values but more. Thus, the experimental resnlts must be reduced to just the two pairs of values required for the determination of the parameters therefore, assuming there are m pairs of values, these m pairs must be reduced to just two pairs. Once the reduction to two pairs has been done, the isotherm equation may be then be written to just the two pairs of derived values as follows ... [Pg.410]

As mentioned in Section 3.7.1.2, there is a considerable scatter of solubility product values obtained in the molten KCl-NaCl eutectic using different methods of solubility determination. This disagreement in the solubility parameters may be explained by differences in the sizes of oxide particles whose solubility is to be determined. The difference in size causes the scatter of the solubility data according to the Ostwald-Freundlich equation and the employment of the isothermal saturation method, which implies the use of commercial powders (often pressed and sintered), leads to values which are considerably lower than those obtained by the potentiometric titration technique where the metal-oxides are formed in situ. Owing to this fact, the regularities connected with the effect of physico-chemical parameters of the oxides or the oxide cations should be derived only from solubility data obtained under the same or similar experimental conditions. However, this does not concern the dissociation constants of the oxides, since homogeneous acid-base equilibria are not sensitive to the properties of the solid phase of... [Pg.343]

The transfer rate in the mixed side-pore model is proportional to the difference in concentration between the flowing-water and immobile-water phases. The transfer-rate constant kgA is a characteristic-rate parameter for diffusion in the immobile-water phase. Without the Freundlich sorption mechanism, this third model is the same as the dead-end pore model developed by Coats and Smith (19). The Freundlich sorption isotherm was included by van Genuchten and Wierenga (18) in their study, but they solved for the linear case only. Grove and Stollenwerk (20) described a similar model but included Langmuir sorption and a continuous immobile-water film phase. [Pg.248]

The first two-box model includes a reversible Freundlich reaction followed by an irreversible first order process. There are four independent parameters the Freundlich parameters, K and n, a reversible rate constant, r, and an irreversible rate constant, k. Initial estimates for the Freundlich parameters were obtained from independent isotherm fits of the data after approximately 2 weeks of adsorption. Fitting the kinetic data by eye provided the initial estimates for r and k. [Pg.187]

A third approach for CDI modeling is to quantify experimental data for salt adsorption in the electrodes as function of salt concentration in the external bath (recycle volume) using one of several adsorption isotherms, such as those based on the Langmuir or Freundlich equation. From the fitted parameters such as equilibrium constant K, useful information can be extracted on the interaction energy between ion and substrate. The fitted isotherms can also be used to predict adsorption at other values of the reservoir ionic strength. [Pg.428]

This method consists to find the thermodynamic model (Henry, Langmuir, Fowler, Freundlich...) which gives the best fit with adsorption isotherms measured at various temperatures [7], The parameter of the model Kmodei is temperature dependent. It can be related to the dimensionless equilibrium constant of adsorption K(T) by the... [Pg.285]


See other pages where Freundlich isotherm parameters constant is mentioned: [Pg.288]    [Pg.288]    [Pg.656]    [Pg.327]    [Pg.32]    [Pg.286]    [Pg.427]    [Pg.432]    [Pg.278]    [Pg.174]    [Pg.211]    [Pg.76]    [Pg.242]    [Pg.263]    [Pg.287]    [Pg.97]    [Pg.395]    [Pg.486]    [Pg.128]   


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