Internalisation mechanisms

Drin, G., et al. 2003. Studies on the internalisation mechanism of cationic cell-penetrating peptides. J Biol Chem 278 31192. 

Depending upon the mechanism that is employed by the organism to accumulate the solute, internalisation fluxes can vary both in direction and order of magnitude. The kinetics of passive transport will be examined in Section 6.1.1. Trace element internalisation via ion channels or carrier-mediated transport, subsequent to the specific binding of a solute to a transport site, will be addressed in Section 6.1.2. Finally, since several substances (e.g. Na+, Ca2+, Zn2+, some sugars and amino acids) can be concentrated in the cell against their electrochemical gradient (active transport systems), the kinetic implications of an active transport mechanism will be examined in Section 6.1.3. Further explanations of the mechanisms themselves can be obtained in Chapters 6 and 7 of this volume [24,245]. 

Determination of the exact mechanism leading to cellular internalisation of CNTs is considered very important in their development as components of biomedical devices and therapeutics intended for implantation or administration to patients. One of the most important parameters in all such studies is the type of nanotubes used, determined by the process by which they are made biocompatible. Interactions with cells have to be performed using biocompatible CNTs, achieved by either covalent or noncovalent surface functionalisation that results in water-dispersible CNTs. A variety of different functionalisation strategies for CNTs have been reported by different groups, therefore direct comparisons are often hampered by the inability to correlate experimental conditions. 

Fig. 6 Diverse mechanisms of a-LTX action. Right, Ca2+ is present in the medium. The pathways shown are described in the text. CC Ca2+ channels DAG, diacyl glycerol LTX 4x, a-LTX tetramers MC, mitochondria. Left, Ca2+-free conditions. For main comments, see text. The possible pathways for Ca2+-independent exocytosis shown include (1) high concentrations of Na+ mimicking Ca2+ (2) the internalised domains of a-LTX interacting with components of the exo-cytotic machinery (E) (3) a-LTX exerting direct fusogenic action.

Fig. 7-2. Summary of environmental pathways by which terrestrial plants may become contaminated with radionuclides. In the case of an input from atmosphere, or as a result of the process of resuspension , any external radionuclide burden may be reduced by field loss mechanisms conversely, an initially external radionuclide deposit (Rat) may become internalised (i int) following foliar absorption and translocation. Radioactive contaminants of soils may be derived either from atmospheric inputs or from seepage in ground waters. Partitioning of radionuclides in soil—soil water systems controls their availability for root absorption, which normally occurs exclusively from the liquid phase. The chemical speciation of the nuclide in this phase, however, provides a further control on bioavailability which is highly radionuclide specific.

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