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Aqueous systems distribution

Among the properties sought in the solvent are low cost, avadabihty, stabiUty, low volatiUty at ambient temperature, limited miscibility in aqueous systems present in the process, no solvent capacity for the salts, good solvent capacity for the acids, and sufficient difference in distribution coefficient of the two acids to permit their separation in the solvent-extraction operation. Practical solvents are C, C, and alcohols. For industrial process, alcohols are the best choice (see Amyl alcohols). Small quantities of potassium nitrate continue to be produced from natural sources, eg, the caUche deposits in Chile. [Pg.536]

Burger and coworkers (5) in 1952 reported that some distribution coefficients for Pu022+ in organic-aqueous systems at lighted conditions were different from those observed for dark conditions, and those authors believed that some Pu022+ had been photochemically reduced. That reduction was confirmed by others (6) in 1965, and in 1969 a report suggested that most aqueous plutonium reactions were affected by light (7 ). [Pg.264]

Guerin TF, IR Kennedy (1992) Distribution and dissipation of endosulfan and related cyclodienes in sterile aqueous systems implication for studies on biodegradation. J Agric Eood Client 40 2315-2323. [Pg.272]

Any fundamental study of the rheology of concentrated suspensions necessitates the use of simple systems of well-defined geometry and where the surface characteristics of the particles are well established. For that purpose well-characterized polymer particles of narrow size distribution are used in aqueous or non-aqueous systems. For interpretation of the rheological results, the inter-particle pair-potential must be well-defined and theories must be available for its calculation. The simplest system to consider is that where the pair potential may be represented by a hard sphere model. This, for example, is the case for polystyrene latex dispersions in organic solvents such as benzyl alcohol or cresol, whereby electrostatic interactions are well screened (1). Concentrated dispersions in non-polar media in which the particles are stabilized by a "built-in" stabilizer layer, may also be used, since the pair-potential can be represented by a hard-sphere interaction, where the hard sphere radius is given by the particles radius plus the adsorbed layer thickness. Systems of this type have been recently studied by Croucher and coworkers. (10,11) and Strivens (12). [Pg.412]

The presence of colloids in natural aqueous systems acts to influence the distribution and behavior of organic pollutants [24,88 - 94]. Colloids are formed by some physical and chemical processes. These physical and chemical processes... [Pg.125]

MINTEQA2 http //www.epa.gov/ceampubl/mmedia/minteq/index.htm MINTEQA2 is an equilibrium speciation model that can be used to calculate the equilibrium composition of dilute aqueous solutions in the laboratory or in natural aqueous systems. The model is useful for calculating the equilibrium mass distribution among dissolved species, adsorbed species, and multiple solid phases under a variety of conditions including a gas phase with constant partial pressures. [Pg.125]

Sharom, M.S. and Solomon, K.R. Adsorption-desorption, degradation, and distribution of permethrin in aqueous systems, J. Agric. FoodChem., 29(6) 1122-1125, 1981. [Pg.1723]

The first part of the book contains basic solution theory and thermodynamics (Chapter 2) a survey of the effects on the distribution ratio of changes in parameter values, such as concentration of metals, complex formers and other reactants, pH, temperature, etc., (Chapter 3) measurement techniques, data collection, evaluation, and interpretation (Chapter 4) and kinetics (Chapter 5). The ionic strength is an essential factor in all aqueous systems, and how to cope... [Pg.30]

Aqueous systems are favourable for the degradation of PVA. Kinetic monitoring of the molecular weight distribution in liquid cultures of mixed microbial... [Pg.150]

However, reactions of PAHs in ambient air to form more polar species (e.g., nitro-PAHs, ketones, quinones, lactones, and dicarboxylic acids) greatly enhance their solubilities in aqueous systems. This has major implications when one considers the distribution of PAHs, and their atmospherically formed PAC derivatives, through the air, water, and soil environments. These increases in solubility upon reaction are important not only from an environmental chemistry perspective but also in terms of possible impacts on public health and ecosystems, e.g., in both the exposure and the health effect... [Pg.451]

The effect of halide, cyanate, cyanide, and thiocyanate ions on the partitioning of Hg in [BMIM][PF6]/aqueous systems (Figure 3.3-2) has been studied [8]. The results indicate that the metal ion transfer to the IL phase depends on the relative hydrophobicity of the metal complex. Hg-I complexes have the highest formation constants, decreasing to those of Hg-F [42]. Results from pseudohalides, however, suggest a more complex partitioning mechanism, since Hg-CN complexes have even higher formation constants [42], but display the lowest distribution ratios. [Pg.73]

Figure 3.3-3 Distribution ratios for (closed symbol) and Cs (open symbol) with dibenzo-18-crown-6 (0.1 m) as extractant in IL/aqueous systems ([BMIM][PF6] ( ), [HMIM][PFd ( ), [OMIM][PFe] ( )) as a function of increasing aqueous phase concentrations of [AI(N03)3] (m). From reference [7]. Figure 3.3-3 Distribution ratios for (closed symbol) and Cs (open symbol) with dibenzo-18-crown-6 (0.1 m) as extractant in IL/aqueous systems ([BMIM][PF6] ( ), [HMIM][PFd ( ), [OMIM][PFe] ( )) as a function of increasing aqueous phase concentrations of [AI(N03)3] (m). From reference [7].
Figure 3.3-8 Distribution ratios for aniline (pKj, = 9.42) and benzoic acid (pKj = 4.19) in [BMIM][PF6]/aqueous systems as a function of the pH of the aqueous phase. Figure 3.3-8 Distribution ratios for aniline (pKj, = 9.42) and benzoic acid (pKj = 4.19) in [BMIM][PF6]/aqueous systems as a function of the pH of the aqueous phase.
The most popular method for measuring the polarity of a solute entails determination of the distribution constant between water and a water-immiscible solvent, e.g., octanol. However, because there is difficulty in dissolving proteins in the solvent, a two-phase aqueous system was developed (Shanbhag and Axelson, 1975). Albertson (1986) reported the construction of various aqueous phase systems for partitioning proteins, other macromolecules, and even cells. Recently, simpler aqueous biphase systems were selected for hydrophobic partitioning of proteins (Hachem et al., 1996). However, because of restrictions similar to those for HIC, as discussed above, it may be premature to replace the method used in Basic Protocol 5. The definition of hydrophobicity is based on the polarity of chemical compounds, which is closely related to the distribution between solvents of different polarities. This theory is similar to the elution mechanism of phase distribution chromatography as well as phase partition. However, complexity in the partition system and procedure hampers the broad use of the phase partition approaches. [Pg.310]

Edwards, D. A., Z. Adeel, and R.G. Luthy. 1994. Distribution of nonionic surfactant and phenanthrene in a sediment/aqueous system. Environ. Sci. Technol. 28, 1550-1560. [Pg.465]


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See also in sourсe #XX -- [ Pg.150 , Pg.151 ]




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