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Other Model Isotherms

Hoory and Prausnitz have suggested extending the van der Waais isotherm [Eq. (3.41)] to a binary. system using the approximations [Pg.114]


Similar to several other models, isotherm (93) has the virial form, with a linear dependence in the interaction term. The essential difference between them is related to another driving parameter of the system, which is called the electrical variable and which characterizes the state of the electrode while the bulk concentration of active species changes. The Frumkin isotherm is valid for a fixed... [Pg.107]

Eijuillbrium. Among the aspects of adsorption, equiUbtium is the most studied and pubUshed. Many different adsorption equiUbtium equations are used for the gas phase the more important have been presented (see section on Isotherm Models). Equally important is the adsorbed phase mixing rule that is used with these other models to predict multicomponent behavior. [Pg.285]

As noted in Chapter 1, the most simple and theoretically sound model for drug-receptor interaction is the Langmuir adsorption isotherm. Other models, based on receptor behavior (see Chapter 3), are available. One feature of all of these models (with the exception of some instances of the... [Pg.244]

In conclusion, we have reviewed how our kinetic model did simulate the experiments for the thermally-initiated styrene polymerization. The results of our kinetic model compared closely with some published isothermal experiments on thermally-initiated styrene and on styrene and MMA using initiators. These experiments and other modeling efforts have provided us with useful guidelines in analyzing more complex systems. With such modeling efforts, we can assess the hazards of a polymer reaction system at various tempera-atures and initiator concentrations by knowing certain physical, chemical and kinetic parameters. [Pg.355]

This technique should give reasonable results for isothermal, first-order reactions. It and other modeling approaches are largely untested for complex and nonisothermal reactions. [Pg.291]

The problems associated with the application of this (or any other) model have been discussed. Because of the form of the typical isotherm, which exhibits a broad plateau region, fitting of experimental results to the model requires that data be obtained over a very broad range of concentrations. This is often very difficult to accomplish in practice, especially when difference methods are used to determine the amount of polymer adsorbed. Evaluation of adsorption in real systems is further complicated by a lack of knowledge of the available solid surface area. The latter may be affected by particle size, shape and surface topography and by polymer bridging between particles. [Pg.35]

It is important to differentiate between the two different types of sorption/ desorption tests (i. e.,batch and column-leaching), and the sorption characteristics determined from one should not be confused with the other. Sorption isotherms obtained with batch equilibrium tests are applied mainly to solid suspensions. The physical model, assumed with this situation, is one of a completely dispersed solid particle system, where all solid particle surfaces are exposed and available for interactions with the contaminants of concern. In contrast, column-leaching tests are performed with intact solid samples, and the sorption characteristics obtained from them are the results of contaminant interactions with a structured system where not all-solid particle surfaces are exposed or available for interactions with the contaminants. [Pg.233]

There are a good number of sorption/desorption isotherm models which were developed in order to reflect the actual sorption/desorption processes occurring in the natural environment. Some models have a sound theoretical basis however, they may have only limited experimental utility because the assumptions involved in the development of the relationship apply only to a limited number of sorption/desorption processes. Other models are more empirical in their derivation, but tend to be more generally applicable. [Pg.233]

The assumption of linear chromatography fails in most preparative applications. At high concentrations, the molecules of the various components of the feed and the mobile phase compete for the adsorption on an adsorbent surface with finite capacity. The problem of relating the stationary phase concentration of a component to the mobile phase concentration of the entire component in mobile phase is complex. In most cases, however, it suffices to take in consideration only a few other species to calculate the concentration of one of the components in the stationary phase at equilibrium. In order to model nonlinear chromatography, one needs physically realistic model isotherm equations for the adsorption from dilute solutions. [Pg.292]

As many other models, even the Toth isotherm was originally derived for the study of gas-solid equilibria. However, it has been extended to the description of liquid-solid system. This isotherm assumes a continuous and wide adsorption energy distribution. The equation of the Toth isotherm is... [Pg.295]

When Af= 1, the model yields a concave down isotherm. The magnitndes of and fc for each species determine their relative affinities and therefore their ability to snppress each other s isotherms. [Pg.311]

Abstract To design an adsorption cartridge, it is necessary to be able to predict the service life as a function of several parameters. This prediction needs a model of the breakthrough curve of the toxic from the activated carbon bed. The most popular equation is the Wheeler-Jonas equation. We study the properties of this equation and show that it satisfies the constant pattern behaviour of travelling adsorption fronts. We compare this equation with other models of chemical engineering, mainly the linear driving force (LDF) approximation. It is shown that the different models lead to a different service life. And thus it is very important to choose the proper model. The LDF model has more physical significance and is recommended in combination with Dubinin-Radushkevitch (DR) isotherm even if no analytical solution exists. A numerical solution of the system equation must be used. [Pg.159]

Other modeling efforts include soil acidification models of the macroscopic type that account for the process of S04 sorption in different ways. These approaches, which assume equilibrium conditions to prevail, include the adsorption isotherm, solubility product, and anion exchange. Prenzel (1994) discussed the various limitations of the above approaches in their capability to account for changes in pH. Recently, Fumoto and Sverdrup (2000) used a constant capacitance approach to describe the pH dependency of S04 sorption isotherms in an andisol. Other modeling efforts of S04 isotherms were reported by Gustafsson (1995) in a spodosol. Such isotherm models are of the equilibrium type and include linear and Temkin types of models. [Pg.318]

The major advantage of the Langmuir isotherm (Eq. 3.13) is that it can be inverted and solved for q in closed-form. This cannot be done with the Volmer isotherm (see next section), or with many other important isotherms, such as the Fowler or the virial isotherms (see below. Sections 3.1.6 and 3.2.3.1). Such isotherms are often called implicit isotherms. The other conditions of validity of the Langmuir model are the ideal behavior of the gas phase, the absence of adsorbate-adsorbate interactions, and the localized character of adsorption. [Pg.74]

As noted in Chapter 1, the most simple and theoretically sound model for drug-receptor interaction is the Langmuir adsorption isotherm. Other models, based on receptor behavior (see Chapter 3), are available. One feature of all these models (with the exception of some instances of the operational model) is that they predict symmetrical curves. A symmetrical curve is one where the half-maximal abscis-sal point (EC50, concentration of x that yields 50% of the maximal value of y) and the inflection point of the curve (where the slope is zero) are the same see Figure 12.17A. However, many experimentally derived dose-response curves are not symmetrical because of biological factors in the system. Thus, there can be curves where the EC50 does... [Pg.292]

After exposing the model catalysts to CO molecules by molecular beam pulses with typical widths of 40 ms (resulting in maximal effective pressures of 2 X 10 mbar) and at a constant isotropic O2 pressure of 5 x 10 mbar, the resulting product molecules (CO2) were detected within isothermal conditions by an absolutely calibrated quadrupole mass spectrometer. From the integral of the detected CO2 pulses, the absolute number of formed CO2 per cluster could be obtained. Dividing this number by the reaction time (40 ms) and the number of atoms in the clusters results in the TOFs of this reaction for various cluster sizes with an estimated accuracy of 10%. From these results, a reaction probability can then be defined by dividing the TOF by the total flux of CO (composed of the direct adsorption or adsorption through reverse spillover) on the cluster. With these two numbers, a catalytic process is defined and allows the cluster s catalytic properties to be compared to other model systems. [Pg.148]

The Langmuir local isotherm that supposes localised sites and no lateral interaction between adsorbed molecules, is the most widely used because of the impossibility of having access to the real values of the parameters used in other models such as the interaction energy between two adsorbed molecules. [Pg.492]

Classical thermodynamic models of adsorption based upon the Kelvin equation [21] and its modihed forms These models are constructed from a balance of mechanical forces at the interface between the liquid and the vapor phases in a pore filled with condensate and, again, presume a specihc pore shape. Tlie Kelvin-derived analysis methods generate model isotherms from a continuum-level interpretation of the adsorbate surface tension, rather than from the atomistic-level calculations of molecular interaction energies that are predominantly utihzed in the other categories. [Pg.206]

The uptake(pH) curves were generated for two hypothetical materials, namely, alumina and silica whose surface area is 100 m /g. and whose pristine surface charging behavior corresponds to the model curves presented in Figs. 5.72 and 5.85, respectively. The model curves representing specific adsorption of Pb on these materials at low initial concentration ([surface sites] > > [total Pb]) were calculated to produce pHso S for 10 g solid/dm and in the presence of 10 mol dm inert electrolyte solution. For sufficiently low total Pb concentration the adsorption isotherms at constant pH are linear and the course of the calculated uptake(pH) curves is independent of the Pb initial concentration. The above solid to liquid ratio is typical for studies of specific adsorption, and pHjo = 5 is a realistic value for Pb adsorption on silica and alumina at this solid to liquid ratio, in view of the results of actual adsorption experiments compiled in Table 4.1. Lead has higher affinity to solid surfaces than most other divalent metal cations. The choice of the model curves from Fig. 5.72 (alumina) and 5.85 (silica), rather than model curves derived from any other set of experimental data analyzed in Section III, or calculated using any other model than TLM, or any other set of TLM parameters was arbitrary. This choice does not imply that TLM is favored over other models or that the experimental data used to derive these model curves are more reliable than other results used as examples in Section III,... [Pg.675]

Non-isothermal 1-D models for adiabatic PBMR and FBMR reactors utilizing Pd tubular membranes have been developed by Elnashaie et al [5.35], and applied to the catalytic ethylbenzene dehydrogenation reaction. In contrast to many other modelling studies their model takes into account intraparticle diffusional limitations. The catalyst particles... [Pg.183]

There are several other derivations of the Langmuir adsorption isotherm from statistical mechanics and thermodynamics. Although the model is physically unrealistic for describing the adsorption of gases on real surfaces, its successes, just like the success of other adsorption isotherms also based on different simple adsorption models, is due to the relative insensitivity of macroscopic adsorption measurements to the atomic details of the adsorption process. Thus the adsorption isotherm... [Pg.305]

The basis for the discussion of adsorption on charged surfaces is the surface complexation model. The precept for this model is the use of the standard mass-action and mass-balance equations from solution chemistry to describe the formation of surface complexes. Use of these equations results in a Langmuir isotherm for the saturation of the surface with adsorbed species. There are of course other models that satisfy these precepts, but which are not generally referred to as surface complexation models, for example, the Stern model (J). [Pg.33]

Other flexible isotherm models extending the Langmuir model are based on the theory of heterogeneous surfaces (Jaroniec and Madey, 1988) and on concepts provided by statistical thermodynamics (Hill, 1960). The latter approach allows deriving the following second-order isotherm model that is capable to describe inflection points in the isotherm courses ... [Pg.34]

The prediction of multicomponent equilibria based on the information derived from the analysis of single component adsorption data is an important issue particularly in the domain of liquid chromatography. To solve the general adsorption isotherm, Equation (27.2), Quinones et al. [156] have proposed an extension of the Jovanovic-Freundlich isotherm for each component of the mixture as local adsorption isotherms. They tested the model with experimental data on the system 2-phenylethanol and 3-phenylpropanol mixtures adsorbed on silica. The experimental data was published elsewhere [157]. The local isotherm employed to solve Equation (27.2) includes lateral interactions, which means a step forward with respect to, that is, Langmuir equation. The results obtained account better for competitive data. One drawback of the model concerns the computational time needed to invert Equation (27.2) nevertheless the authors proposed a method to minimize it. The success of this model compared to other resides in that it takes into account the two main sources of nonideal behavior surface heterogeneity and adsorbate-adsorbate interactions. The authors pointed out that there is some degree of thermodynamic inconsistency in this and other models based on similar -assumptions. These inconsistencies could arise from the simplihcations included in their derivation and the main one is related to the monolayer capacity of each component [156]. [Pg.325]

A thermodynamic model developed by Barba, Brandani and di Giacomo (1982) described the solubility of calcium sulphate in saline water. A system of equations based on Debye Hiickel and other models was used to describe isothermal activity coefficients of partially or completely dissociated electrolytes. Using binary parameters, good agreement was claimed between experimental and predicted values of calcium sulphate solubility in sea water and brackish brines including those with a magnesium content. [Pg.121]

From the literature, several possible methods for the solution of the balance equations presented are known. A classification firstly resulted from the fact that for some equations analytical solutions are available depending on the adsorption isotherm and boundary conditions chosen, while other models can be solved only numerically. A detailed overview of the numerical algorithms for the solution of... [Pg.307]

Among the theories of predicting mixed-gas adsorption equilibria from pure component adsorption isotherms, the ideal adsorbed solution theory (IAST) [14] has become the standard and often serves as a benchmark for the purpose of comparison by other models. IA ST is a thermodynamically rigorous theory based on the mixing of individual components at constant spreading pressure to form an ideal solution. It has the advantages that (1) no mixture data are required and (2) the theory is independent of the actual model of physical adsorption. [Pg.408]


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