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Dispersion boundary positions

Figure 7. Dispersion boundary positions for the PDM system at low salinities. Figure 7. Dispersion boundary positions for the PDM system at low salinities.
Figure 7.8 Solutions of the ideal model in the case of a bi-Langmuir isotherm, (a) Bi-Langmuir isotherms with variable fl2 and t>2 coefficients and constant qs- Inset low-concentration part of the isotherm (with liquid phase concentration scale at the top of the inset), (b) Band profiles corresponding to the isotherms in (a). Only the rear dispersive boundaries of the profiles are shown. The position of the front shock depends on the sample size. Inset end of the profiles, on a different scale, (c) Bi-Langmuir isotherms with constant 2 and variable b2 coefficients. Inset low- concentration part of the isotherms, (d) Band profiles corresponding to the isotherms in (c). Inset enlargement of the end of the profiles. Figure 7.8 Solutions of the ideal model in the case of a bi-Langmuir isotherm, (a) Bi-Langmuir isotherms with variable fl2 and t>2 coefficients and constant qs- Inset low-concentration part of the isotherm (with liquid phase concentration scale at the top of the inset), (b) Band profiles corresponding to the isotherms in (a). Only the rear dispersive boundaries of the profiles are shown. The position of the front shock depends on the sample size. Inset end of the profiles, on a different scale, (c) Bi-Langmuir isotherms with constant 2 and variable b2 coefficients. Inset low- concentration part of the isotherms, (d) Band profiles corresponding to the isotherms in (c). Inset enlargement of the end of the profiles.
On a more positive note, it seems clear that steels can be made more resistant to the effects of hydrogen by incorporating as many strong, finely dispersed traps in the microstructure as is possible, while ensuring that there are no continuous trap sites (such as embrittled grain boundaries). [Pg.1241]

In a reactive transport model, the domain of interest is divided into nodal blocks, as shown in Figure 2.11. Fluid enters the domain across one boundary, reacts with the medium, and discharges at another boundary. In many cases, reaction occurs along fronts that migrate through the medium until they either traverse it or assume a steady-state position (Lichtner, 1988). As noted by Lichtner (1988), models of this nature predict that reactions occur in the same sequence in space and time as they do in simple reaction path models. The reactive transport models, however, predict how the positions of reaction fronts migrate through time, provided that reliable input is available about flow rates, the permeability and dispersivity of the medium, and reaction rate constants. [Pg.21]

The effect of advection and dispersion on the distribution of a chemical component within flowing groundwater is described concisely by the advection-dispersion equation. This partial differential equation can be solved subject to boundary and initial conditions to give the component s concentration as a function of position and time. [Pg.292]

Clearly, since it includes so many effects (see above), Ga can be positive or negative. Sometimes one effect will dominate, e.g., dispersion or solvent structural change. If the ca are determined empirically, they can also make up for fundamental limitations of the bulk electrostatic treatment (such as the intrinsically uncertain location of the solute/bulk boundary and also for systematic errors in the necessarily approximate model used for the solute. [Pg.19]

The study of the interfacial liquid-liquid phase however is complicated by several factors, of which the chief is the mutual solubility of the liquids. No two liquids are completely immiscible even in such extreme cases as water and mercury or water and petroleum the interfacial energy between two pure liquids will thus be affected by such inter-solution of the two homogeneous phases. In cases of complete intersolubility there is evidently no boundary interface and consequently no interfacial energy. On addition of a solute to one of the liquids a partition of the solute between all three phases, the two liquids and the interfacial phase, takes place. Thus we obtain an apparent interfacial concentration of the added solute. The most varied possibilities, such as positive or negative adsorption from both liquids or positive adsorption from one and negative adsorption from the other, are evidently open to us. In spite of the complexity of such systems it is necessary that information on such points should be available, since one of the most important colloidal systems, the emulsions, consisting of liquids dispersed in liquids, owe their properties and peculiarities to an extended interfacial phase of this character. [Pg.95]

The concentration of a compound at a given location depends on (1) the rate of transformation of the compound (positive for production and negative for consumption), and (2) the rate of transport to or from the location. In Part III we discussed different kinds of transformation processes. Internal transport rates were introduced in Chapter 18. Remember that we have divided them into just two categories, the directed transport called advection and the random transport called diffusion or dispersion. The second Fickian law (Eq. 18-14) describes the local rate of change due to diffusion. The corresponding law for advective processes will be introduced in Chapter 22. In Chapter 19 we discussed transport processes across boundaries. [Pg.953]

In order to be consistent with other chapters, R(Ct) is defined as a positive number if the chemical is produced in the river and T(Ct) is positive if the net flux is directed from the river into the atmosphere or sediment. Note that (F(Ct) is a flux per unit volume its relation to the usual flux per area as defined, for instance, in Chapter 20, is given below (Eq. 24-15). Again we suppress the compound subscript i wherever the context is clear. The subscript Lagrange refers to what fluid dynamicists call the Lagrangian representation of the flow in which the observer travels with a selected water volume (the river slice ) and watches the concentration changes in the volume while moving downstream. Later the notion of an isolated water volume will be modified when mixing due to diffusion and dispersion across the boundaries of the volume is taken into account. [Pg.1105]

As for the pulse input, the evolving concentration, Cw(x,t), can be envisioned as the result of two simultaneous processes (1) advective transport along x at effective flow velocity u and (2) smoothing by dispersion relative to the moving front, x = ut. The front is a diffusive boundary (Section 19.4). The concentration relative to its mean position, x = ut, can be described by Eq. 19-52. Note that in Eq. 19-52 x is the distance relative to the moving front whereas in Eq. 25-28 we replace it by x = ut where now x is a fixed coordinate along the flow ... [Pg.1163]

The preceding paragraphs were a rough outline of the gradual dispersal of the miasma veiling the catalytic processes further, it should once more be underlined that catalysis, from the phenomenological standpoint, does not occupy any specific position in the group of processes which take place at phase boundaries. [Pg.3]

The creation of a protective coat or boundary layer (with a hydrophilic colloid) about such particles offers the best protection to crystal growth. Because protective barriers may or may not flocculate, the substrate particles, the sign (positive or negative), and the charge potential on the particle surface (including a double layer) govern the choice between flocculation or dispersion (deflocculation). [Pg.3603]

Where C, (t, z) is the concentration of the the / th component at position z and L is the column length. Boundary conditions characterize the injection and if the dispersion effects are neglected they can be described by rectangular pulses with duration tp at the column inlet. Assuming that the sample concentration is C0 i... [Pg.52]

Figure 8 shows the microemulsion interface positions for the PDM system in this regime. Convection is not indicated. The dispersion front boundaries were very irregular in shape, and, therefore, those positions are not plotted. However, estimates of the relative dispersion front velocity in each experiment are given in the first two entries of Table III. As is evident from the small difference between these values and those for the brine interface, the brine layer grew very slowly at these salinities. [Pg.205]

My, oo). This new phase boundary for the cloud point of the rubber is shown as the upper curve in Figure 1.34 and will correspond to an extent of conversion pcvphase dispersed in the thermoset (a-)phase and, as shown in Figure 1.34, the theoretical composition of the P-phase will be given by the position on the cloud-point boundary as shown. (It has been noted that this is not strictly correct due to polydispersity effects and the actual composition lies outside this line (Pascault et al, 2002)). [Pg.117]

The bounce-back collision typically employed at fluid-solid boundaries, where fluid particles are turned back in the direction they came from following collision with a solid wall, causes the effective wall position to extend one half lattice unit into the fluid from the solid surface (Stockman et al., 1997). This is not a serious problem for velocity computations in slow flows, but has the potential to be a significant problem for tracer/dispersion simulations. Increasing the number of lattice points inside a flow channel can reduce this error, but is computationally very expensive. [Pg.130]


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Dispersion positive

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