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Physico-chemical model

In this work the development of mathematical model is done assuming simplifications of physico-chemical model of peroxide oxidation of the model system with the chemiluminesce intensity as the analytical signal. The mathematical model allows to describe basic stages of chemiluminescence process in vitro, namely spontaneous luminescence, slow and fast flashes due to initiating by chemical substances e.g. Fe +ions, chemiluminescent reaction at different stages of chain reactions evolution. [Pg.54]

E. Buzaneva, A. Karlash, K. Yakovkin, Y. Shtogun, S. Putselyk, D. Zherebetskiy, A. Gorchinskiy, G. Popova, S. Prilutska, O. Matyshevska, Y. Prilutskyy, P. Lytvyn, P. Scharff, and P. Eklund, DNA nanotechnology of carbon nanotube cells physico-chemical models of self-organization and properties. Mat. Sci. Eng. C-Bio. S. 19, 41 15 (2002). [Pg.596]

Maes, A. Cremers, A. In "Soil Chemistry B. Physico-Chemical Models" Bolt, G.H. Ed. Elsevier Sci. Publ. Amsterdam, 1979, Chap. 6. [Pg.18]

Buzaneva E, Karlash A, Yakovkin K, Shtogun Y, Putselyk S, Zherebetskiy D, Gorchinskiy A, Popova G, Prilutska S, Matyshevska O, Prilutskyy Y, Lytvyn P, Scharff P, Eklund P (2002) DNA nanotechnology of carbon nanotube cells Physico-chemical models of self-organization and properties. Mater. Sci. Eng. C 19 41 15. [Pg.44]

Laffort, P. and Dravnieks, A. An approach to a physico-chemical model of olfactory stimulation in vertebrates by single compounds, J. Theor. Biol, 38 335-345, 1973. [Pg.1683]

This transformation of a physico-chemical model into an empirical model was previously discussed by Weyland et al. [27]. A ternary nonlinear blending term is often added to improve the descriptive power of this equation. Then, a special cubic mixture model is obtained ... [Pg.268]

QSAR, (frequently derived by regression analysis based on physico-chemical models which refer to the respective biological property.)... [Pg.15]

The behaviour we are expecting to emerge from this physico-chemical model is that of a steady wave of reaction moving from left to right in Fig. 11.2 into the region of unreacted A. By steady, we really mean that the wavefront should maintain its shape as it moves with a constant speed. It is this shape and speed which we seek to determine (and express in terms of the rate constant, diffusion coefficient, etc.). [Pg.296]

The measured uptake coefficient y is a convolution of the processes which affect the rate of gas uptake. Uptake coefficients have been measured for various PSC surfaces and sulfuric acid solutions using a variety of experimental methods, and have been interpreted in tenns of physico-chemical models to yield reactivities and solubilities of gaseous species. More most cases the total experimental uptake coefficient ym can be represented in tenns of a resistance model, whereby the resistances l/ym and 1/y are associated with reaction and liquid solubility [42] Quantitative values for y will be discussed later in section 2.3.4. [Pg.270]

We have introduced many practical software based numerical procedures to solve physico-chemical models for simulation and design purposes. Therefore, we hope that our readers now feel comfortable and ready to handle more complex industrial problems from the modeling stage through the numerical solution and model validation stages on her/his own. [Pg.425]

Van Genuchten, M. Th. Cleary, R. W. "Movement of Solutes in Soil Computer-Simulated and Laboratory Results, in "Soil Chemistry, B. Physico-Chemical Models, Bolt, G. H., Ed., Elsevier Scientific Publishing Company, New York, 1979. [Pg.28]

Bolt, G.H. (1982) Transport and accumulation of soluble soil components. In G. H. Bolt, editor, Soil chemistry. B. Physico-chemical models 143, Elsevier, Amsterdam, pp. 285-346... [Pg.205]

See, for example, Chap. 5 in G. H. Bolt, Soil Chemistry. B. Physico-Chemical Models, Elsevier, Amsterdam, 1982, for a compilation of binary cation exchange data. [Pg.214]

Extensive DFT and PP calculations have permitted the establishment of important trends in chemical bonding, stabilities of oxidation states, crystal-field and SO effects, complexing ability and other properties of the heaviest elements, as well as the role and magnitude of relativistic effects. It was shown that relativistic effects play a dominant role in the electronic structures of the elements of the 7 row and heavier, so that relativistic calculations in the region of the heaviest elements are indispensable. Straight-forward extrapolations of properties from lighter congeners may result in erroneous predictions. The molecular DFT calculations in combination with some physico-chemical models were successful in the application to systems and processes studied experimentally such as adsorption and extraction. For theoretical studies of adsorption processes on the quantum-mechanical level, embedded cluster calculations are under way. RECP were mostly applied to open-shell compounds at the end of the 6d series and the 7p series. Very accurate fully relativistic DFB ab initio methods were used for calculations of the electronic structures of model systems to study relativistic and correlation effects. These methods still need further development, as well as powerful supercomputers to be applied to heavy element systems in a routine manner. Presently, the RECP and DFT methods and their combination are the best way to study the theoretical chemistry of the heaviest elements. [Pg.86]

Upon approach, organisms will be attracted or repelled by the biomaterial surface, depending on the resultant of the various interaction forces. Thus, the physico-chemical surface properties of the biomaterial, with or without conditioning film, and those of the microorganisms play a decisive role in this process. Because the size of microorganisms is in the im range, adhesion can be described in terms of colloid science. Indeed, for several strains and species physico-chemical models like the Deijaguin-... [Pg.139]

G.H. Bolt, In Soil Science, Volume B, Physico-Chemical Models. G.H. Bolt, Ed., Elsevier (1979), chapter 1. [Pg.276]

Adsorption of Inorganics at SoUd-Uquid Interfaces, M.A. Anderson, A.J. Rubin, Eds., Ann Arbor Science (1981) T.W. Healy, L.R. White, Ado. CdUoid Intetface Set 9 (2978) 303 G.H. Bolt, W.H. van Riemsdljk, in Sod Chemistry, B. Physico-chemical Models, G.H. Bolt, Ed.. 2nd part, 2nd ed., Elsevier (1982). chapter 13 P.W. Schindler, W. Stunun In Aquatic Surface Chemistry, Wiley (1978), chapter 4. [Pg.327]

Another possibility is to obtain physico-chemical models. Consider for instance the optimization of pH and solvent strength. The subject was studied among others by Marques and Schoenmakers [66], Schoenmakers et al. [67,68] and Bourguignon et al. [62] for the optimization of the separation of a mixture of chlorophenols. Marques and Schoenmakers proposed the following model based on a quadratic relationship between log k and the solvent composition () and on dissociation equilibria ... [Pg.206]

M. E. Orazem, P. Agarwal, A. N. Jansen, P. T. Wojcik, and L. H. Garcia-Rubio, "Development of Physico-Chemical Models for Electrochemical Impedance Spectroscopy," Electrochimica Acta, 38 (1993) 1903-1911. [Pg.513]

Putikov, O.F. and Wen, B., 1997. Mathematical and physico-chemical modelling of concentration distribution of heavy metals in "stream" halos of dispersion. Abstracts of International Geophysical Conference, Moscow 97, G.2-8,1 p. [Pg.499]

Wen, B., 1997a. Physico-chemical modelling of the natural ionic flotation of metals by gas bubbles in porous rocks. In Abstracts of the All-Russian Scientific-Practical Conference of Young Scientists and Specialists, "Geophysics-97". VIRG Rudgeofizika, St.Petersburg, pp. 44-45 (in Russian). [Pg.510]

Wen, B., 1997b. Solution of the physico-mathematical model of the "stream" halo of dispersion and comparison with results of physico-chemical modelling. In Abstracts of the Annual Scientific Conference of Young Scientists, "Mineral Resources of Russia and their Exploitation". St.Petersburg State Mining Institute, St. Petersburg, p. 4 (in Russian). [Pg.510]

De Vries DJ. IMPAQT, a physico-chemical model for simulation of the fate and distribution of micro pollutants in aquatic systems.The Netherlands and TOW-IW T250, Delft Hydraulics, 1987. [Pg.646]

Soil Chemistry. Vol. B, Physico-Chemical Models Bolt, G. H., Ed. Elsevier Amsterdam, The Netherlands, 1982. [Pg.92]

G. H. Bolt and V.H. van Riemsdijk, in G.H.Bolt (ed.), Physico-Chemical Models, Soil Chemistry, Elsevier, Amsterdam,1982. [Pg.875]

Bolt, G. H., and Van Riemsdijk, W. H. (1982). Ion adsorption on inorganic variable charge constituents. In Soil Chemistry, Part B, Physico-Chemical Models, 2nd ed., ed. Bolt, G. H., Elsevier, Amsterdam, The Netherlands, 495-502. [Pg.452]


See other pages where Physico-chemical model is mentioned: [Pg.3]    [Pg.18]    [Pg.197]    [Pg.293]    [Pg.406]    [Pg.3]    [Pg.575]    [Pg.1422]    [Pg.21]    [Pg.31]    [Pg.380]    [Pg.92]    [Pg.93]    [Pg.792]    [Pg.792]    [Pg.705]   
See also in sourсe #XX -- [ Pg.384 , Pg.386 ]




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