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Non-reactive species

Chapter 1) that its concentration in the reservoir can be modified only by processes taking place at the boundaries. Species i can be added to or subtracted from the system by solid, liquid or gaseous input and output, not by chemical reaction or radioactive decay inside the reservoir. For the sake of illustration, we will consider a water reservoir, whose properties will be labeled liq . Mass balance requires [Pg.346]

This is the simplest of autonomous systems with no force acting on it (pure relaxation). At t = 0, the concentration is [Pg.346]

Between t and t + dt, the outlet of the reservoir loses a quantity d M (t) of species i that has resided for a time t in the reservoir and given by [Pg.347]

The residence time t of the species i is the mean age of each mass fraction, i.e.  [Pg.347]

The relaxation time V/Q is therefore the mean residence time of the species i in the reservoir. This parameter does not depend on the nature of the species as long as the species is non-reacting In particular, V/Q is also the water residence (or renewal or flushing) time. For this reason, it will be denoted th. [Pg.347]


If only partial screening is present, the fractal dimension takes a value somewhere between df and df. According to this model, a crosslinker deficiency, which leads to a more open structure and therefore a lower value of du increases the value of n. Dilution of the precursor with a non-reactive species has the same effect on the relaxation exponent. [Pg.186]

Steady-state is established more rapidly for a reactive than for a non-reactive species and the steady-state concentration will be smaller (Figure 7.3). [Pg.350]

Figure 7.3 Comparative evolution of the concentration for a non-reactive species and a reactive species when the input concentration is doubled at t=0. In this particular case, th = 0.2 is the water residence time in time units, a,- = 4 the reactivity coefficient, equation (7.2.8), of the reactive species. Figure 7.3 Comparative evolution of the concentration for a non-reactive species and a reactive species when the input concentration is doubled at t=0. In this particular case, th = 0.2 is the water residence time in time units, a,- = 4 the reactivity coefficient, equation (7.2.8), of the reactive species.
The criteria for the thermally decomposable coblock include the synthesis of well-defined functional oligomers, compared with the synthesis of polyimide. This block must also decompose quantitatively into non-reactive species that can easily diffuse through a glassy polyimide matrix. The temperature at which decomposi-... [Pg.88]

Studies of CO oxidation over Pt/Al203 [72-74] showed that oscillations are observed only in the presence of admixed hydrocarbons or water. If the reaction mixture is thoroughly purified, self-oscillations vanish. These data are evidently an argument in favour of the fact that reversible formation steps of non-reactive species play a special role in the appearance of selfoscillations. In accordance with the assertions of Marshneva et al. [163,164],... [Pg.262]

The possible reactions of a radical species impinging upon a surface can be classified in the following way The particle can either become reflected without reacting with a probability r, it can react with the surface to form a volatile, non-reactive species that desorbs with a probability 7, or it can effectively stick to the surface with a probability s. In principle, one might also consider reactions in which a different reactive species is formed, however it is assumed that this reaction channel is negligible. [Pg.254]

These catalytic cycles are largely responsible for the depletion of ozone. One chlorine atom may destroy more than 100,000 ozone molecules before it is transformed into a non-reactive species. Despite the substantial reduction of chlorine and bromine compounds released into the atmosphere as a result of the Montreal Protocol, this has not shown any significant impact on the reduction of the size of the ozone hole. If such a trend continues, it may still take some half a century for the recovery of ozone to the levels it had prior to 1984. [Pg.178]

For relatively non-reactive species such as chlorides, will approximate zero for reactive materials, such as some actinides, the coefficient may exceed 10, Note that this coefficient is kinetic in nature, with the time required to reach equilibrium dependent on many factors. For example, work by Rhodes(2) indicated that for a polymeric form of 239pu> over 852 of the adsorption occurred in the first 5 minutes, with continued adsorption over a period of several hundred hours. He observed that the approach to equilibrium was approximately proportional to the log of time. [Pg.23]

The dashed lines in Fig. 6.51 indicate the intrinsic Arrhenius curve of the transfer, whereas the solid line indicates the one including the pre-equilibrium. The reduction of the rate constants as compared to the di-tert-butyl radical is explained by the formation of a non-reactive species at low temperatures, which is hydrogen bonded to the added dioxane. Thus, for the reaction to occur, the intramolecular H-bonded species has first to be formed, which exhibits a higher energy but also a... [Pg.208]

Based on the strong dilution trends of non-reactive species, such as chloride and sulfate, the extent of interaction of fracture condensate water with matrix pore water must have been very limited. However, reactive species, such as silica, show increasing concentrations owing to reaction with predominantly fracture-lining silica polymorphs and feldspars at higher temperatures. A precipitation zone of secondary mineral phases such as amorphous silica, calcite, and gypsum in... [Pg.351]

Deactivation pathways arise from the decomposition of any of the intermediates and lead to non-reactive species (i.e., species that cannot readily re-enter the catalytic cycle). Moreover, the reaction intermediate can also lead to the formation of by-products, which may or may not be connected to deactivation processes. Computational studies of such reactions are challenging because they can involve many intermediates and reaction pathways. In addition, there is often a lack of information about such processes in terms of their nature and the spectroscopic signatures of the chemical species containing the metal center and/or of the by-products, as well as kinetic data of their mode of formation. For these reasons, studies of deactivation and by-product formation are rarely carried out, even if they are probably indispensable for a full understanding of the efficiency of a catalytic process and the rational design of better catalysts. [Pg.173]

In selectivity problems, it may be interesting to control the location of the FERMI level, and, to this purpose, to introduce small amounts of a non-reactive species, which is adsorbed with N ... [Pg.68]

In vitro methods Tissue binding assays. If no in vivo models are available, in vitro methods combined with in vivo testing in a pharmacologically non-reactive species may suffice. [Pg.14]


See other pages where Non-reactive species is mentioned: [Pg.418]    [Pg.345]    [Pg.349]    [Pg.58]    [Pg.52]    [Pg.12]    [Pg.40]    [Pg.146]    [Pg.216]    [Pg.178]    [Pg.1099]    [Pg.8]    [Pg.370]    [Pg.40]    [Pg.116]    [Pg.180]    [Pg.59]    [Pg.144]    [Pg.476]    [Pg.575]    [Pg.94]    [Pg.429]    [Pg.280]    [Pg.293]   


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