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Composition model, local application

Two activity coefficient models have been developed for vapor-liquid equilibrium of electrolyte systems. The first model is an extension of the Pitzer equation and is applicable to aqueous electrolyte systems containing any number of molecular and ionic solutes. The validity of the model has been shown by data correlation studies on three aqueous electrolyte systems of industrial interest. The second model is based on the local composition concept and is designed to be applicable to all kinds of electrolyte systems. Preliminary data correlation results on many binary and ternary electrolyte systems suggest the validity of the local composition model. [Pg.86]

The Wohl-type models find only limited application today. They are presented, however, because they represent a simple example of how expressions for are developed. The obtained expressions for the activity coefficient are also easier to use than those of the local composition models. [Pg.465]

This predictive capability of the local composition models - considering the large number of available binary data - is extremely important in practice, because industrial applications require multicomponent data in the typical case. [Pg.478]

On the other hand it was pointed out in Section 13.13, that one of the main advantages of the local composition models is exactly their ability to predict multicomponent behavior from binary data alone. And this represents a commonly used approach in industrial applications. [Pg.487]

It has been stated that the global LSER equation (eq. 1.55) takes into consideration simultaneously the descriptors of the analyte and the composition of the binary mobile phase and it can be more easily employed than the traditional local LSER model [79], The prerequisite of the application of LSER calculations is the exact knowledge of the chemical structure and physicochemical characteristics of the analyses to be separated. Synthetic dyes as pollutants in waste water and sludge comply with these requirements, therefore in these cases LSER calculations can be used for the facilitation of the development of optimal separation strategy. [Pg.27]

Several length-scales have to be considered in a number of applications. For example, in a typical monolith reactor used as automobile exhaust catalytic converter the reactor length and diameter are on the order of decimeters, the monolith channel dimension is on the order of 1 mm, the thickness of the catalytic washcoat layer is on the order of tens of micrometers, the dimension of the pores in the washcoat is on the order of 1 pm, the diameter of active noble metal catalyst particles can be on the order of nanometers, and the reacting molecules are on the order of angstroms cf. Fig. 1. The modeling of such reactors is a typical multiscale problem (Hoebink and Marin, 1998). Electron microscopy accompanied by other techniques can provide information on particle size, shape, and chemical composition. Local composition and particle size of dispersed nanoparticles in the porous structure of the catalyst affect catalytic activity and selectivity (Bell, 2003). [Pg.138]

The novel approach for calculation of pore size distributions, which is reported in the current study is based on recent developments in the materials science and in the theory of inhomogeneous fluids. First, an application of experimental adsorption data for well-characterized MCM-41 silicas enabled proper calibration of the pore size analysis. Second, an application of a modem theory to describe the behavior of inhomogeneous fluids in confined spaces, that is the non-local density functional theory [6], allowed the numerical calculation of model isotherms for various pore sizes. In addition, a practical numerical deconvolution method that provides a "best fit" solution representing the pore distribution of the sample was implemented [7, 8]. In this paper we describe a deconvolution method for estimating mesopore size distribution that explicitly allows for unfilled large pores, and a method for creating composite, or hybrid, models that incorporate both theoretical calculations and experimental observations. Moreover, we showed the applicability of the new approach in characterization of MCM-41 and related materials. [Pg.72]

The genesis of the reactor design equations is the conservation of mass. Since reactor operations involve changes in species compositions, the mass balance is written for individual species, and it is expressed in terms of moles rather than mass. Species balances and the reactor design equations are discussed in detail in Chapter 4. To obtain a complete description of the reactor operation, it is necessary to know the local reaction rates at all points inside the reactor. This is a formidable task that rarely can be carried out. Instead, the reactor operation is described by idealized models that approximate the actual operation. Chapters 5-9 cover the applications of reactor design equations to several ideal reactor conflgurations that are commonly used. [Pg.14]

Simple GC methods based on UNIFAC, containing corrections for the FV effects, satisfactorily predict the solvent activities and VLE for binary and ternary polymer solutions. They are less successful for the prediction of LEE if the parameters are based on VLE. They are much more successful if the parameters are based on LEE data. The combination of a simple FV expression such as that employed in the Entropic-FV model and a local composition energetic term such as that of UNIQUAC seems to be a very promising tool for both VLE and LLE in polymer solutions. We expect that such tools may find widespread use in the future for practical applications. [Pg.735]

As explained above, experimental data with nitrating acids of compositions typical of those employed industrially cannot be reconciled with theoretical models assuming a uniform rate of reaction through either or both phcises. Such models will only apply to slow reactions. The other extreme is an instantaneous reaction, which would lead to reaction taking place at a reaction plane. This cannot be applicable to mononitrations since nitric acid is always found in the organic phase. Development of a model to describe the overall rate demands a knowledge of the locale of the reaction. Conflicting opinions have been expressed... [Pg.199]


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