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Species interaction

Various functional forms for / have been proposed either as a result of empirical observation or in terms of specific models. A particularly important example of the latter is that known as the Langmuir adsorption equation [2]. By analogy with the derivation for gas adsorption (see Section XVII-3), the Langmuir model assumes the surface to consist of adsorption sites, each having an area a. All adsorbed species interact only with a site and not with each other, and adsorption is thus limited to a monolayer. Related lattice models reduce to the Langmuir model under these assumptions [3,4]. In the case of adsorption from solution, however, it seems more plausible to consider an alternative phrasing of the model. Adsorption is still limited to a monolayer, but this layer is now regarded as an ideal two-dimensional solution of equal-size solute and solvent molecules of area a. Thus lateral interactions, absent in the site picture, cancel out in the ideal solution however, in the first version is a properly of the solid lattice, while in the second it is a properly of the adsorbed species. Both models attribute differences in adsorption behavior entirely to differences in adsorbate-solid interactions. Both present adsorption as a competition between solute and solvent. [Pg.391]

Chemisorption occurs when the attractive potential well is large so that upon adsorption a strong chemical bond to a surface is fonued. Chemisorption involves changes to both the molecule and surface electronic states. For example, when oxygen adsorbs onto a metal surface, a partially ionic bond is created as charge transfers from the substrate to the oxygen atom. Other chemisorbed species interact in a more covalent maimer by sharing electrons, but this still involves perturbations to the electronic system. [Pg.294]

As argued above, this result is found to work best for substances in which both the 1,1 and 2,2 forces are either London or dipole-dipole. Even the case of one molecule with a permanent dipole moment interacting with a molecule which has only polarizability and no permanent dipole moment-such species interact by permanent dipole-induced dipole attraction-is not satisfactorily approximated by Eq. (8.46). In this context the like dissolves like rule means like with respect to the origin of intermolecular forces. [Pg.525]

When more than one adsorbed species or more than two ion-exchanged species interact in some manner, equilibrium becomes more complicated. Usually, thermodynamics provides a sound basis for prediction. [Pg.1507]

Based upon the above-mentioned species interactions, pilot-scale testing is generally recommended to accurately size a biofilter bed for a multicomponent waste gas stream. [Pg.2193]

The response from sandwich membranes measurements of species interactions in situ. [Pg.305]

McClellan K, Altenburger R, Schmltt-Jansen M (2008) Pollution-induced community tolerance as a measure of species interaction in toxicity assessment. J Appl Ecol 45 1514... [Pg.53]

As noted earlier, the kinetics of electrochemical processes are inflnenced by the microstractnre of the electrolyte in the electrode boundary layer. This zone is populated by a large number of species, including the solvent, reactants, intermediates, ions, inhibitors, promoters, and imparities. The way in which these species interact with each other is poorly understood. Major improvements in the performance of batteries, electrodeposition systems, and electroorganic synthesis cells, as well as other electrochemical processes, conld be achieved through a detailed understanding of boundaiy layer stracture. [Pg.174]

By increasing the temperature of treatment, the species interacting via hydrogen bonding react via elimination of a water molecule and form a new (possibly strained) siloxane bond, according with the reaction path reported... [Pg.6]

It was shown that complexes 19 of the zwitterionic precursors of ortho-quinone methides and a bis(sulfonium ylide) derived from 2,5-di hydroxyl 1,4 benzoquinone46 were even more stable than those with amine N-oxides. The bis(sulfonium ylide) complexes were formed in a strict 2 1 ratio (o-QM/ylide) and were unaltered at —78 °C for 10 h and stable at room temperature under inert conditions for as long as 15—30 min (Fig. 6.18).47 The o-QM precursor was produced from a-tocopherol (1), its truncated model compound (la), or a respective ortho-methylphenol in general by Ag20 oxidation in a solution containing 0.50-0.55 equivalents of bis(sulfonium ylide) at —78 °C. Although the species interacting with the ylide was actually the zwitterionic oxidation intermediate 3a and not the o-QM itself, the term stabilized o-QM was introduced for the complexes, since these reacted similar to the o-QMs themselves but in a well defined way without dimerization reactions. [Pg.181]

Multiparticle collision dynamics provides an ideal way to simulate the motion of small self-propelled objects since the interaction between the solvent and the motor can be specified and hydrodynamic effects are taken into account automatically. It has been used to investigate the self-propelled motion of swimmers composed of linked beads that undergo non-time-reversible cyclic motion [116] and chemically powered nanodimers [117]. The chemically powered nanodimers can serve as models for the motions of the bimetallic nanodimers discussed earlier. The nanodimers are made from two spheres separated by a fixed distance R dissolved in a solvent of A and B molecules. One dimer sphere (C) catalyzes the irreversible reaction A + C B I C, while nonreactive interactions occur with the noncatalytic sphere (N). The nanodimer and reactive events are shown in Fig. 22. The A and B species interact with the nanodimer spheres through repulsive Lennard-Jones (LJ) potentials in Eq. (76). The MPC simulations assume that the potentials satisfy Vca = Vcb = Vna, with c.,t and Vnb with 3- The A molecules react to form B molecules when they approach the catalytic sphere within the interaction distance r < rc. The B molecules produced in the reaction interact differently with the catalytic and noncatalytic spheres. [Pg.134]

Schneider, 1984 Schneider and Schwyn, 1987 Schneider, 1988 Cornell et al., 1989). Perchlorate solutions that contain the dinuclear Fe2(OH)24+ to about 10 % of the total iron concentration can be kept unchanged for several weeks. This is by no means trivial, because it was recognized many years ago that solutions containing Fe2(OH)24+ to a significant degree are supersaturated with respect to solid phases such as FeO(OH) (Biedermann and Schindler, 1957). The low molecular species interact to produce species with a higher nuclearity (equation 7) ... [Pg.50]

These dynamic strategies also play important roles in the chemical defense of benthic organisms. Only in recent years have marine scientists started to apply methods that allow these defensive strategies to be monitored. This opens the field for the identification of signals that play a role in species-species interactions in the marine environment and for the elucidation of hormones responsible for regulating the production of secondary metabolites. [Pg.217]

Bais, Fl.P., Vepachedu, R., Gilroy, S., Callaway, R.M. and Vivanco, J.M. (2003). Allelopathy and exotic plant invasion From molecules and genes to species interactions. Science 301 1377-1380. [Pg.146]

When ions are formed by electron transfer, the resulting charged species interact according to Coulomb s law,... [Pg.211]

A basic exposition of Gibbs phase rule is essential for understanding phase solubility analysis, and detailed presentations of theory are available [41,42]. In a system where none of the chemical species interact with each other, the number of independently variable factors (i.e., the number of degrees of freedom, F) in the system is given by... [Pg.335]

In the two-state model [20,21] the two different species interact and the interaction can be expressed using the regular solution model. Thus the Gibbs energy of the liquid is... [Pg.144]

Au particle size as well as the BET SA of the catalysts, the reducibility of Au oxide species, and the associated Fe203 to Fe304 species interacting with the Au. A summary table is provided in Table 127. [Pg.264]

Several reactions are possible in the formation of chlorine dioxide [5] and in reality a group of reactions and species interactions take place in the hypochlorite solution. Usual reaction components are NaOCl, HOC1, HC1, Cl-, HCIO2, NaCICU, CIO2, NaCl, H20, etc. In understanding the model presented in this chapter, a few of the reactions are presented below ... [Pg.321]


See other pages where Species interaction is mentioned: [Pg.1714]    [Pg.1871]    [Pg.2193]    [Pg.179]    [Pg.46]    [Pg.54]    [Pg.316]    [Pg.176]    [Pg.125]    [Pg.367]    [Pg.282]    [Pg.11]    [Pg.97]    [Pg.93]    [Pg.37]    [Pg.183]    [Pg.200]    [Pg.412]    [Pg.314]    [Pg.72]    [Pg.90]    [Pg.246]    [Pg.254]    [Pg.261]    [Pg.232]    [Pg.534]    [Pg.7]    [Pg.145]    [Pg.167]    [Pg.399]   
See also in sourсe #XX -- [ Pg.556 , Pg.562 ]




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Associative interactions between kraft lignin species

Climate Effects on Species Interactions and Ecosystem Structure

Cyclic species, transannular interactions

Diffusion of Interacting Species

Electron-neutral species interaction

Electron-neutral species interaction potentials

Hydrogen, molecular, interaction with hydrocarbon species

Interacting species

Interacting species

Interaction Between Surfactant, Agrochemical and Target Species

Interactions among species, positive

Interactions with adsorbed species

Linear species orbital interactions

Metal species interaction with biological

Migration and Predator-Prey Interaction Between Two Species

Neutral species, interaction between

Nonrandom interactions between kraft lignin species

Paramagnetic species dipolar interaction

Radical-surface interactions species

Reactive oxygen species interactions

Reactive oxygen species water interactions

Support interactions, silver species

Surface Electrode Reaction Involving Interactions Between Immobilized Species

Surfactant interactions with oppositely charged species

Surfactants Interactions with inorganic species

Templating species, interaction with

Templating species, interaction with zeolites

Toxicology-species extrapolation toxicologic interactions

Trigonal pyramidal species orbital interactions

Zeolites interactions with adsorbed species

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