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Scale composition

A particularly useful concept in synthesizing MENs is the notion of corresponding composition scales. It is a tool for incorporating thennodynamic constraints... [Pg.47]

Equation (3.5) can be used to establish a one-to-one correspondence among all composition scales for which mass exchange is feasible. Since most environmental applications involve dilute systems, one can assume that these systems behave ideally. Hence, the transfer of the pollutant is indifferent to the existence of other species in the waste stream. In other words, even if two waste streams contain species that are not identical, but share the same composition of a particular pollutant, the equilibrium composition of the pollutant in an MSA will be the same for both waste streams. Hence, a single composition scale, y, can be used to represent the concentration of the pollutant in any waste stream. Next, (3.5) can be employed to generate Ns scales for the MSAs. For a given set of corresponding composition scales y,x, X2,..., xj,..., it is thermodynamically and practically feasible to transfer the pollutant from any waste stream to any MSA. In addition, it is also feasible to transfer the pollutant from any waste stream of a composition y/ to any MSA which has a composition less than the xy obtained from (3.5b). [Pg.49]

Next, a global representation of all process lean streams is developed as a lean composite stream. First, we establish Ns/> lean composition scales (one for each process MSA) that are in one-to-one coirespondence with the rich scale according to the method outlined in Section 3.5. Next, the mass of pollutant that can be gained by each process MSA is plotted vei us the composition scale of that MSA. Hence, each i xx ess MSA is represented as an arrow extending between supply and target compositions (see Fig. 3.5 for a two-MSA example). Ihe vertical distance between the arrow head and tail is given by... [Pg.50]

The CID is a useful tool for insuring diermodynamic feasibility of mass exchange. On this dia am, N,p + 1 corresponding composition scales are generated. First, a composition scale, y, for the waste streams is established. Then, Eq, (3.5) is employed to create Nsp corresponding composition scales for the process MSAs. On the CID, each process stream is represented as a vertical arrow whose tail corresponds to its supply composition while its head represents its target composition. Next, horizontal lines are drawn at the heads and tails of the arrows. These horizontal lines define a series of composition intervals. The number of intervals... [Pg.105]

Corresponding composition scales for reactive mass exchange... [Pg.193]

Corresponding Composition Scales for Reactive IVfass Exchange... [Pg.193]

Now that a procedure for establishing the corresponding composition scales for the rich lean pairs of stream has been outlined, it is possible to develop the CID. The CID is ccHistructed in a manner similar to that described in Chapter Five. However, it should be noted that the conversion among the corresponding composition scales may be more laborious due to the nonlinearity of equilibrium relations. Furthermore, a lean scale, xj, represents all forms (physically dissolved and chemically combined) of the pollutant. First, a composition scale, y, for component A in... [Pg.199]

The selectivity values at both ends of the surface composition scale are related to the intrinsic selectivity coefficients by (91) ... [Pg.277]

Debye-Huckel effects are significant in the dilute range and are not considered, and (2) the usual composition scale for the solute standard state is molality rather than mole fraction. Both of these problems have been overcome, and the more complex relationships are being presented elsewhere (17). However, for most purposes, the virial coefficient equations for electrolytes are more convenient and have been widely used. Hence our primary presentation will be in those terms. [Pg.456]

Whether p 7, and a, refer to a mole fraction composition scale or to a molality composition scale will be clear from the context in which they are used. We will not attempt to use different S5mbols for each scale. [Pg.359]

Figure 1135 Estimation of formation temperature from measured 8D values of coexisting kaolinite and aqueous solution on the isotope composition scale. The kaolinite-pure water line is from Liu and Epstein (1984). Dashed lines show the shift induced by increasing salinity of solution. Reprinted from J. Horita, D. R. Cole, and D. J. Wesolowski, Geo-chimica et Cosmochimica Acta, 57, 4703-4711, copyright 1993, with kind permission from Elsevier Science Ltd., The Boulevard, Langford Lane, Kidlington 0X5 1GB UK. Figure 1135 Estimation of formation temperature from measured 8D values of coexisting kaolinite and aqueous solution on the isotope composition scale. The kaolinite-pure water line is from Liu and Epstein (1984). Dashed lines show the shift induced by increasing salinity of solution. Reprinted from J. Horita, D. R. Cole, and D. J. Wesolowski, Geo-chimica et Cosmochimica Acta, 57, 4703-4711, copyright 1993, with kind permission from Elsevier Science Ltd., The Boulevard, Langford Lane, Kidlington 0X5 1GB UK.
The two extremes on the styrene-butadiene block copolymer composition scale are homopolymers of butadiene or styrene, respectively. To test the usefulness of homopolymers as dispersants, polybutadiene (PB) was carboxylated by adding thioglycolic acid, and polystyrene (PS) having carboxylic groups was prepared by copolymerizing small amounts of acrylic acid (AA) into the styrene chain. Adsorption experiments with these carboxylated homopolymers are listed in Table V. In the first... [Pg.403]

For a given solute, different solvents show different departures from ideal behaviour, both in terms of the concentration required to observe the onset of such deviations and in terms of their direction and magnitude. It is first necessary to specify the composition scale employed. For aqueous solutions the molality scale, moles of solute per kg of water, denoted by m, is frequently used. This scale becomes less useful when several solvents are compared, since in one kg batches of diverse solvents there are a variable number of moles of solvent (1 /[Ml kg mol 1]) and they occupy different volumes (l/[molality scale is in common use for dilute electrolyte solutions in solvents used for electrochemical purposes as it is for their aqueous solutions. However, even the change from water to heavy water, D20, requires caution in this respect, and the... [Pg.81]

As mentioned above you will be studying mixtures of cholesteryl nonanoate and cholesteryl chloride rather than the pure materials. Mixtures are used for the convenience of working at temperatures closer to room temperature. To prepare a mixture of a given composition, use the mole fraction composition scale. A mole fraction of a component in a mixture is defined as the number of moles of that component in the mixture divided by the total number of moles of all components in the mixture. To actually prepare a mixture, add the desired amounts of each component to a screw cap vial. Mix the components physically with a spatula to make a reasonably uniform mixture of the solids. Place the vial in a sample oven whose temperature has been set to about 100°C and allow the solids to melt and mix. [Pg.465]


See other pages where Scale composition is mentioned: [Pg.527]    [Pg.47]    [Pg.48]    [Pg.56]    [Pg.69]    [Pg.81]    [Pg.107]    [Pg.111]    [Pg.126]    [Pg.134]    [Pg.160]    [Pg.195]    [Pg.200]    [Pg.202]    [Pg.234]    [Pg.193]    [Pg.117]    [Pg.118]    [Pg.56]    [Pg.211]    [Pg.354]    [Pg.362]    [Pg.374]    [Pg.182]    [Pg.141]    [Pg.95]    [Pg.184]    [Pg.42]    [Pg.104]    [Pg.69]    [Pg.7]    [Pg.271]    [Pg.308]   
See also in sourсe #XX -- [ Pg.36 ]




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