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Residual chemical potential

X is the scalar distance between the solute molecule and the center of the imaginary membrane, with the LJ parameters of the solute used as reducing parameters. The residual chemical potential for a pure fluid (which would correspond to component 2 in its pure state at the state conditions of cell A) can then, for example, be found using the expression... [Pg.785]

In contrast chemical and electrolytic polishing enables a smooth level surface to be produced without any residual stress being developed in the surface because the surface is removed by dissolution at relatively low chemical potential and at relatively low rates is such a way that metallic surface asperities are preferentially removed. For this to be most effective the solution properties must be optimised and the pretreatment must leave an essentially bare metal surface for attack by the electrolyte. [Pg.300]

The subscripts 1,2,3 refer to the main solvent, the polymer, and the solvent added, respectively. The meanings of the other symbols are n refractive index m molarity of respective component in solvent 1 C the concentration in g cm"3 of the solution V the partial specific volume p the chemical potential M molecular weight (for the polymer per residue). The surscript ° indicates infinite dilution of the polymer. [Pg.22]

Coenzyme A (see also p. 106) is a nucleotide with a complex structure (see p. 80). It serves to activate residues of carboxylic acids (acyl residues). Bonding of the carboxy group of the carboxylic acid with the thiol group of the coenzyme creates a thioester bond (-S-CO-R see p. 10) in which the acyl residue has a high chemical potential. It can therefore be transferred to other molecules in exergonic reactions. This fact plays an important role in lipid metabolism in particular (see pp. 162ff), as well as in two reactions of the tricarboxylic acid cycle (see p. 136). [Pg.12]

Acyl residues are usually activated by transfer to coenzyme A (2). In coenzyme A (see p. 12), pantetheine is linked to 3 -phos-pho-ADP by a phosphoric acid anhydride bond. Pantetheine consists of three components connected by amide bonds—pantoic acid, alanine, and cysteamine. The latter two components are biogenic amines formed by the decarboxylation of aspartate and cysteine, respectively. The compound formed from pantoic acid and p-alanine (pantothenic acid) has vitamin-like characteristics for humans (see p. 368). Reactions between the thiol group of the cysteamine residue and carboxylic acids give rise to thioesters, such as acetyl CoA. This reaction is strongly endergonic, and it is therefore coupled to exergonic processes. Thioesters represent the activated form of carboxylic adds, because acyl residues of this type have a high chemical potential and are easily transferred to other molecules. This property is often exploited in metabolism. [Pg.106]

Creatine (N-methylguanidoacetic acid) and its phosphorylated form creatine phosphate (a guanidophosphate) serve as an ATP buffer in muscle metabolism. In creatine phosphate, the phosphate residue is at a similarly high chemical potential as in ATP and is therefore easily transferred to ADP. Conversely, when there is an excess of ATP, creatine phosphate can arise from ATP and creatine. Both processes are catalyzed by creatine kinase [5]. [Pg.336]

Using this approach, a model can be developed by considering the chemical potentials of the individual surfactant components. Here, we consider only the region where the adsorbed monolayer is "saturated" with surfactant (for example, at or above the cmc) and where no "bulk-like" water is present at the interface. Under these conditions the sum of the surface mole fractions of surfactant is assumed to equal unity. This approach diverges from standard treatments of adsorption at interfaces (see ref 28) in that the solvent is not explicitly Included in the treatment. While the "residual" solvent at the interface can clearly effect the surface free energy of the system, we now consider these effects to be accounted for in the standard chemical potentials at the surface and in the nonideal net interaction parameter in the mixed pseudo-phase. [Pg.104]

Translating the thermodynamic concept of interacting surfaces to our basic COSMO-RS, the residual part of the chemical potential of a compound i in a solvent S is found by a summation of the chemical potentials of the surface segments of i. Starting from Eq. (5.10) we have... [Pg.100]

Dietary exposure to pesticides (or to xenobiotics in general) is determined by calculating the product of the amount of chemical in or on the food and the total quantity of food consumed. The quantity of chemical potentially consumed in foods can be estimated from data obtained from residue field trials, metabolism studies, and/or monitoring data. Information from these sources is then analyzed with one of several available models containing food consumption factors from surveys conducted by the United States Department of Agriculture (USDA). For calculation of... [Pg.413]

One of the most challenging tasks in the theory of liquids is the evaluation of the excess entropy Sex, which is representative of the number of accessible configurations to a system. It is well known that related entropic quantities play a crucial role, not only in the description of phase transitions, but also in the relation between the thermodynamic properties and dynamics. In this context, the prediction of Sex and related quantities, such as the residual multiparticle entropy in terms of correlation functions, free of any thermodynamic integration (means direct predictive evaluation), is of primary importance. In evaluating entropic properties, the key quantity to be determined is the excess chemical potential (3pex. Calculation of ppex is not straightforward and requires a special analysis. [Pg.42]

The oxidation of propylene oxide on porous polycrystalline Ag films supported on stabilized zirconia was studied in a CSTR at temperatures between 240 and 400°C and atmospheric total pressure. The technique of solid electrolyte potentiometry (SEP) was used to monitor the chemical potential of oxygen adsorbed on the catalyst surface. The steady state kinetic and potentiometric results are consistent with a Langmuir-Hinshelwood mechanism. However over a wide range of temperature and gaseous composition both the reaction rate and the surface oxygen activity were found to exhibit self-sustained isothermal oscillations. The limit cycles can be understood assuming that adsorbed propylene oxide undergoes both oxidation to CO2 and H2O as well as conversion to an adsorbed polymeric residue. A dynamic model based on the above assumption explains qualitatively the experimental observations. [Pg.165]

The residual chemical potentials of benzene, p f aI,d P2 p> ar d that of C02 in the fluid phase, p[ are calculated by Widom s test particle insertion method, Eq. (6) [6], which has been embedded in all the simulation programs. [Pg.329]

In addition to the simulation data for K2, which were presented in the above sections, the simulation outputs provide more information to look insight into the factors influencing Kr According to Eq. (5), K2 is evaluated from the exponential of the difference between p pkT and f/kT. Therefore, it is important to know how the residual chemical potentials of benzene in two phases change with the temperature and densities. [Pg.331]

Figure 5 shows the pore density of pure C02, pp, and the residual chemical potentials of benzene, pffikTand fi[c kT, against the reciprocal temperature at constant fluid density, p ... [Pg.331]

The partial molar residual chemical potential of component one is therefore ... [Pg.127]

In this work, special attention was paid to minimising the potential residues from PET recycling. Some works have been published on active carbons from granulated non-used PET [4], but none concerning the use of plastic wastes. The advantage of the pyrolysis of post-consumer PET is that all the products obtained present interesting applications (i.e., chemical products, gases with calorific value and a solid that can be used as an active carbon), as a result of which residual wastes can be minimised considerably. The aim of this work was to obtain valuable active carbons from the solid residue from PET pyrolysis. [Pg.538]

The residual chemical potential of species a can be obtained from the residual Helmholtz free energy by differentiating by the number of moles of a (see Eq. (11.1)) ... [Pg.79]

The residual chemical potential is equal to the difference between the chemical potential of the system and the chemical potential of an ideal gas at the same temperature, molar volume, and composition. The difference given in Eq. (11.20) is between the system and an ideal gas at the same temperature, pressure, and composition. This is not the same as the residual chemical potential. However, the two quantities are related. If we consider an ideal gas with the same molar volume as the system, its pressure will be equal to p = RT/V, which will, in general, not be equal to the actual pressure p of... [Pg.81]


See other pages where Residual chemical potential is mentioned: [Pg.433]    [Pg.205]    [Pg.5]    [Pg.349]    [Pg.122]    [Pg.18]    [Pg.182]    [Pg.502]    [Pg.523]    [Pg.63]    [Pg.100]    [Pg.114]    [Pg.163]    [Pg.166]    [Pg.774]    [Pg.5]    [Pg.63]    [Pg.144]    [Pg.329]    [Pg.331]    [Pg.332]    [Pg.332]    [Pg.362]    [Pg.62]    [Pg.15]    [Pg.2009]    [Pg.46]    [Pg.958]    [Pg.958]    [Pg.522]    [Pg.36]   
See also in sourсe #XX -- [ Pg.134 , Pg.142 , Pg.144 , Pg.235 ]




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Chemical residue

Models for residual chemical potential and activity coefficient in the liquid phase

Partial molar residual chemical potential

Reduced residual chemical potential

Residual potential

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