Organic solutes adsorption onto surfaces

Adsorption — An important physico-chemical phenomenon used in treatment of hazardous wastes or in predicting the behavior of hazardous materials in natural systems is adsorption. Adsorption is the concentration or accumulation of substances at a surface or interface between media. Hazardous materials are often removed from water or air by adsorption onto activated carbon. Adsorption of organic hazardous materials onto soils or sediments is an important factor affecting their mobility in the environment. Adsorption may be predicted by use of a number of equations most commonly relating the concentration of a chemical at the surface or interface to the concentration in air or in solution, at equilibrium. These equations may be solved graphically using laboratory data to plot "isotherms." The most common application of adsorption is for the removal of organic compounds from water by activated carbon. 

The mechanisms of adsorption of organic solutes—including hydro-phobic, polar, and ionic species—onto surfaces have been summarized previously (2 5). Assuming that the various adsorptive mechanisms act independently, the free energy of adsorption (AGa[Pg.192]

These examples show that adsorption of water molecules on platinum electrodes depends on the solution components. If the energy of the solute adsorption is higher than that of water molecules, water tends to adsorb on the top of the primary solute layer, which is directly bound to the platinum adsorption sites. If the interaction of organic molecules with platinum is weak, water adsorbs directly onto the electrode surface. In the... 

These monolayers form themselves spontaneously by adsorption of suitable components from a diluted solution directly onto a surface. The formation of ordered and orientated monomolecular layers by spontaneous adsorption from a diluted solution is called self-assembling, the respective layers are called self-assembled monolayers (SAM) or self-organized monolayers. In the first part of this review, the coating of surfaces with functionalized SAMs will be examined. After that, some aspects of the attachment of the biomolecules onto these SAM-modified surfaces will be discussed. 

The link between colloids and surfaces follows naturally from the fact that particulate matter has a high surface area to mass ratio. The surface area of a 1cm diameter sphere (4jtr ) is 3.14 cm, whereas the surface area of the same amount of material but in the form of 0.1 pm diameter spheres (i.e. the size of the particles in latex paint) is 314 000 cm. The enormous difference in surface area is one of the reasons why the properties of the surface become very important for colloidal solutions. One everyday example is that organic dye molecules or pollutants can be effectively removed from water by adsorption onto particulate activated charcoal because of its high surface area. This process is widely used for water purification and in the oral treatment of poison victims. 

In conclusion, for low-dose dmg products, it is important to be aware of the possibility that adsorption of the dmg from the sample solutions onto surfaces can lead to low or variable assay results. These surfaces include filters, volumetric flasks, and sample vials. Evaluation of the components that come in direct contact with the sample solutions for potential dmg adsorption should be conducted as part of method development. This is especially true for compounds containing active sites such as amino groups, as described in this case study. While, most potency analyses involve the use of some organic solvents in the dissolving solvent, dissolution analyses could be problematic since the compendial media are aqueous buffers. For components such as HPLC vials, it is important to examine not only the type... 

The reversal of the direction of the electro-osmotic flow by the adsorption onto the capillary wall of alky-lammonium surfactants and polymeric ion-pair agents incorporated into the electrolyte solution is widely employed in capillary zone electrophoresis (CZE) of organic acids, amino acids, and metal ions. The dependence of the electro-osmotic mobility on the concentration of these additives has been interpreted on the basis of the model proposed by Fuerstenau [6] to explain the adsorption of alkylammonium salts on quartz. According to this model, the adsorption in the Stern layer as individual ions of surfactant molecules in dilute solution results from the electrostatic attraction between the head groups of the surfactant and the ionized silanol groups at the surface of the capillary wall. As the concentration of the surfactant in the solution is increased, the concentration of the adsorbed alkylammonium ions increases too and reaches a critical concentration at which the van der Waals attraction forces between the hydrocarbon chains of adsorbed and free-surfactant molecules in solution cause their association into hemimicelles (i.e., pairs of surfactant molecules with one cationic group directed toward the capillary wall and the other directed out into the solution). 

This relationship resulted from the spontaneous tendency for the analyte, initially solubilized in an aqueous matrix, to partition into the surface monolayer of hydrophobic octadecyl- or octyl-bonded silica. Organic compounds as analytes will have a unique value for the thermodynamic distribution constant. One fundamental difference between LEE and SPE stands out Partition or adsorption of solute molecules onto a solid surface follows the principles of the Eangmuir adsorption isotherm, whereas EEE does not. We will briefly develop the principles below. This model assumes that an analyte A combines with a site of adsorption, S, in which there is a finite number of such sites according to... 

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