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Organic complexes hydrophobic

Neutral carriers are organic complexing agents which are capable of sequestering and transporting ionic species in a hydrophobic organic phase. The antibiotics, valino-mycin and nonactin were the first neutral carriers to be incorporated in an ISE These macrocyclic neutral carriers contain a polar internal cavity and an outer hydro-phobic shell. The excellent selectivity exhibited by valinomycin for potassium ions is... [Pg.58]

Morel, F.M.M. 1983. Principles of aquatic chemistry, p. 427. Wiley-Interscience, NY. Mortland, M.M. 1970. Clay-organic complexes and interactions, Advan. Agron. 22 75-117. Namba, S., N. Hosonuma, and T. Yashima. 1981. Catalytic application of hydrophobic properties... [Pg.252]

Unlike the oxalato-complex, this complex is insoluble in water but it is soluble in organic solvents. This contrast is due to the organic ligands surrounding Al which makes the complex hydrophobic. On the other hand, the polar oxalate ligands surrounding Al in the oxalato-complex explain the hydrophilic nature of the solid. [Pg.265]

Interactions between nonpolar compounds are generally stronger in water than in organic solvents. At concentrations where no aggregation or phase separation takes place, pairwise hydrophobic interactions can occur. Under these conditions, the lowest energy state for a solute molecule is the one in which it is completely surrounded by water molecules. However, occasionally, it will also meet other solute molecules, and form short-lived encounter complexes. In water, the lifetime of these complexes exceeds that in organic solvents, since the partial desolvation that accompanies the formation of these complexes is less unfavourable in water than in organic solvents. [Pg.167]

Absorption, metaboHsm, and biological activities of organic compounds are influenced by molecular interactions with asymmetric biomolecules. These interactions, which involve hydrophobic, electrostatic, inductive, dipole—dipole, hydrogen bonding, van der Waals forces, steric hindrance, and inclusion complex formation give rise to enantioselective differentiation (1,2). Within a series of similar stmctures, substantial differences in biological effects, molecular mechanism of action, distribution, or metaboHc events may be observed. Eor example, (R)-carvone [6485-40-1] (1) has the odor of spearrnint whereas (5)-carvone [2244-16-8] (2) has the odor of caraway (3,4). [Pg.237]

Although most nonionic organic chemicals are subject to low energy bonding mechanisms, sorption of phenyl- and other substituted-urea pesticides such as diuron to sod or sod components has been attributed to a variety of mechanisms, depending on the sorbent. The mechanisms include hydrophobic interactions, cation bridging, van der Waals forces, and charge-transfer complexes. [Pg.221]

It is established, that the natural and synthetic polymers influence on spectrophotometrical, protolytical and complex-formating properties of azodyes in different degree. The result of interaction between anions of organic dyes and polymers is formation of specifical hydrophobic-hydrated adducts. Express spectrophotometrical methods of polymer content determination in water solutions with the help of polymer adducts have been elaborated. [Pg.110]

Contaminant transfer to bed sediments represents another significant transfer mechanism, especially in cases where contaminants are in the form of suspended solids or are dissolved hydrophobic substances that can become adsorbed by organic matter in bed sediments. For the purposes of this chapter, sediments and water are considered part of a single system because of their complex interassociation. Surface water-bed sediment transfer is reversible bed sediments often act as temporary repositories for contaminants and gradually rerelease contaminants to surface waters. Sorbed or settled contaminants are frequently transported with bed sediment migration or flow. Transfer of sorbed contaminants to bottomdwelling, edible biota represents a fate pathway potentially resulting in human exposure. Where this transfer mechanism appears likely, the biotic fate of contaminants should be assessed. [Pg.237]


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