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Surfaces solids chemical behavior

The energetics and wetting properties of solid-state materials are of great importance in the performance of pharmaceutical and chemical materials. A detailed knowledge on the surface chemical behavior will assist in predicting surface properties such as solubility, adhesion, surfactant adsorption, and many others. [Pg.37]

We believe that better understanding of the behavior of macromolecules at the solid surfaces will facilitate further progress in chemical design of the composite sorbents as well as other bioseparation media such as membranes, fibers etc. and their application in various fields. [Pg.136]

Gold nanoparticles (NP) are just one of a variety of ways to modify the chemical behavior of surfaces by entities that can be described by their solid-state rather than... [Pg.278]

The solid phase of the subsurface is a porous medium composed of a mixture of inorganic and organic natural materials in various stages of development. The surface area and the surface (chemical) properties of the solid phase are major factors that control the behavior of chemicals. [Pg.4]

Soil organic matter is found wherever organic matter is decomposed, mainly in the near surface. However soil organic matter may also be transported as suspended particles into deeper layers of the vadose zone or via surface- and groundwaterforming sediments. Although these components form a minor part of the total solid phase, they are of major importance in defining the surface properties of the solid phase and have a great impact on the chemical behavior. [Pg.14]

Such pentacarbonyl species can be further decarbonylated when the sample is heated to 373 K under an inert gas stream and under reduced pressure. This slow decarbonylation process provides the surface Mo(CO)3 species depicted in Figure 9.4, which is stable up to 473 K [14]. In contrast with the relevant chemical behavior in solution (9.1 and 9.2), in the solid state, where the species are somewhat diluted and present low mobility, no dimeric species have been identified as resulting from penta- or tricarbonyl species. Heating to 673 K gives rise to the evolution of H2, CO, CO2 and CH4, due to redox reactions between the metal center and the OH surface groups. The resulting oxidation states, as determined by XPS measurements, are mainly II and IV, besides some Mo(0) species ]20]. It is worth underHn-... [Pg.355]

We begin with a discussion of the most common minerals present in Earth s crust, soils, and troposphere, as well as some less common minerals that contain common environmental contaminants. Following this is (1) a discussion of the nature of environmentally important solid surfaces before and after reaction with aqueous solutions, including their charging behavior as a function of solution pH (2) the nature of the electrical double layer and how it is altered by changes in the type of solid present and the ionic strength and pH of the solution in contact with the solid and (3) dissolution, precipitation, and sorption processes relevant to environmental interfacial chemistry. We finish with a discussion of some of the factors affecting chemical reactivity at mineral/aqueous solution interfaces. [Pg.461]

While our primary interest in this text is internal flow, there are certain similarities with the classic aerodynamics-motivated external flows. Broadly speaking, the stagnation flows discussed in Chapter 6 are classified as boundary layers where the outer flow that establishes the stagnation flow has a principal flow direction that is normal to the solid surface. Outside the boundary layer, there is typically an outer region in which viscous effects are negligible. Even in confined flows (e.g., a stagnation-flow chemical-vapor-deposition reactor), it is the existence of an inviscid outer region that is responsible for some of the relatively simple correlations of diffusive behavior in the boundary layer, like heat and mass transfer to the deposition surface. [Pg.776]

EPITAXY. An oriented crystalline growth between two crystalline solid surfaces of different chemical composition, in which the surface of one crystal provides, through its lattice structure, preferred positions lor the deposition of the second crystal. This behavior is characteristic of some types of high polymers. [Pg.577]

The science of catalysis covers a large spectrum of phenomena. We observe—with some pride and joy—that this volume presents eight topics which, like the rainbow, form an almost systematic and complete sweep of the major classes of topics in catalysis. It spans from the most classical mechanistic study (P. W. Selwood), to a presentation of a hard practical application (M. Shelef et al). As we sweep across, we cover characterization studies of catalyst solids in terms of electronic (G. M. Schwab), surface chemical (H. A. Benesi and B. H. C. Winquist), as well as physicochemical and structural (F. E. Massoth) parameters, chemical reaction mechanisms and pathways (G. W. Keulks et al., and B. Gorewit and M. Tsutsui), and a topic on reactor behavior (V. Hlavacek and J, Votruba), which takes us from the single catalyst particle to the macroscopic total reactor operation. [Pg.412]

The three types of adsorption are (1) physical, (2) chemical, and (3) exchange adsorption. Especially important to the success of in situ treatment by Fe° are the soil characteristics, which affect soil sorptive behavior such as mineralogy, permeability, porosity texture, surface qualities, and pH. Physical adsorption is due to van der Waal s forces between molecules where the adsorbed molecule is not fixed on the solid surface but is free to move over the surface and may condense and form several superimposed layers. An important characteristic of physical adsorption is its reversibility. On the other hand, chemical adsorption is a result of much stronger forces with a layer forming, usually of one molecule thickness, where the molecules do not move. It is normally not reversible and must be removed by heat. The exchange adsorption and ion exchange process involves adsorption by electrical attraction between the adsorbate and the surface (Rulkens, 1998). [Pg.510]

Fig. 4.5. Potential singular point surface (dashed-dotted curve) for a ternary system with phase splitting behavior and the single reaction A + B C. RA = reactive azeotrope solid curve = chemical equilibrium surface. Fig. 4.5. Potential singular point surface (dashed-dotted curve) for a ternary system with phase splitting behavior and the single reaction A + B C. RA = reactive azeotrope solid curve = chemical equilibrium surface.
Reference conditions These are physical or chemical parameters that need to be assessed in conjunction with the analysis for standard compliance (e.g., temperature, pH, organic carbon content for soil or dissolved organic carbon, and total suspended solids for surface water) (depending on which factors influence chemical behavior and toxicity). [Pg.20]

Heterogeneous photochemical processes are concerned with the effect of light on interacting molecules and solid surfaces. The concept of photoinduced surface chemistry is commonly used to integrate these processes. As cited earlier, they involve surface phenomena such as adsorption, diffusion, chemical reaction and desorption [3]. Experiments and theoretical calculations make clear that the photochemical behavior of an adsorbed molecule can be very different from that of a molecule in the gas or liquid phase [4]. Photochemical reactions of this type involve molecules and systems of quite different complexity, from species composed of a few atoms in the stratosphere to large chiral organic molecules that presumably were formed in prebiotic systems. [Pg.51]

The situation here is very unusual in that the breaking of a single chemical bond at a solid surface can be direcdy recognized. Fig. 3 shows the electrolytic dissolution of two n-type Ge electrodes, where the supply of holes is limited, which is to be contrasted to the dissolution of a p-type electrode where there is an unlimited supply of holes at the surface (7). As shown in Fig. 4, the dissolution rate can also be limited by the supply of chemical species needed for the formation of the final ions in solution (7). Fig. 4 also shows that hydroxyl ions lead to formation of metagermanate ions much faster than do water molecules. A similar behavior has also been found with fluoride ions. [Pg.183]


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See also in sourсe #XX -- [ Pg.3 ]




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