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Non limitation

If water losses from the surrounding area are a major component of the total evaporative losses of the pond, then soil moisture conditions will be expected to be high. Under non-limiting soil moisture conditions vegetative moisture losses are often defined as "potential" losses. Evaporative losses in this case would not be expected to differ greatly from free water evaporation. The literature recommends... [Pg.549]

Trivial Names for Carbohydrates and Derivatives with their Systematic Equivalents and Symbols (non-limiting list)... [Pg.172]

The maximum amount of water used by a unit is determined using constraints (6.10). This amount is used as the limit in constraints (6.8) and (6.9). In a multiple contaminant system there exists a limiting component for each operation in each unit. The limiting component is the component that requires the largest amount of water to remove the required mass load and still comply with the maximum inlet and outlet concentrations. For a certain operation in a certain unit there could exist multiple limiting components, however, the amount of water required by each will be the same. It is important to note that when the maximum amount of water is used, the concentration of the non-limiting components will be below their respective maxima. [Pg.125]

FIGURE 8.9 Mitochondrial 02 and H2S consumption from non-limiting 02 to anoxic conditions, (a) Isolated mitochondria were exposed to repeated bouts of 12.5 pM H2S until anoxia was achieved, (b) At higher 02 levels, both 02 and H2S consumption events are coincident, but as the 02 levels decline the events become uncoupled and 02 consumption is limited first. The multiphasic kinetics of 02 consumption may result from transient inhibition of cytochrome c oxidase by H2S. Under anoxia, H2S consumption continues at a low level (after [36] reproduced with permission of the Company of Biologists). [Pg.253]

To appreciate that deviation from the Levich equation is likely to stem from non-limiting currents (the overpotential rj is not extreme enough), breakdown of mass transport ( j is too extreme) and turbulent flow. [Pg.196]

The value of = 0 in a Koutecky-Levich plot implies that the rotation speed is infinite. We should appreciate that any current obtained at o) — 00 would automatically represent a mass-transport-limited quantity. So let us now look at what the non-limiting currents along the y-cpcis really mean when x is 0. [Pg.233]

Different simple correlations between biomass and fluorescence data showed that on-line estimation is possible under strictly defined culture conditions. Even a strictly finear relation between biomass and culture fluorescence was found for the growth of Zymomonas mobilis, Methylomonas mucosa, and Pseudomonas putida under non-limited conditions [47]. [Pg.26]

Figure 4. Comparison between BAF(nP) data from non-limited-growth experiments and values estimated from Figures 2 and 3. Data points represent the average BAF(np)from three time points (t = 8, 16, and 30 days). The solid line is based on data from Connolly and Pedersen (27), and the dashed line is based on data from Gobas et al. (40). Figure 4. Comparison between BAF(nP) data from non-limited-growth experiments and values estimated from Figures 2 and 3. Data points represent the average BAF(np)from three time points (t = 8, 16, and 30 days). The solid line is based on data from Connolly and Pedersen (27), and the dashed line is based on data from Gobas et al. (40).
A variety of responses can be initiated by the direct interaction of metals with cellular components. Membrane damage and enzyme inhibition are examples of such a metal effect. Above a certain threshold concentration of metals in the cell, its physiological state is irreversibly changed (Van Assche et al., 1988). This response is reflected by an increase in capacity (activity under non-limiting substrate and coenzyme concentrations) of certain enzymes. This increase in capacity is generally called enzyme induction. These secondary, indirect effects of metals are considered to play an important role in the stress metabolism induced by toxic metal concentrations. [Pg.161]

The expected change in Bronsted exponent with change in reactivity is illustrated by the results [49] shown in Table 9 for the hydrolysis of vinyl ethers (mono alkoxy-activated olefins) which occurs by initial slow protonation of olefinic carbon as in mechanism (28). The value of R which is the catalytic coefficient for an acid of pK 4.0 calculated from results for carboxylic acids with pK around 4.0 is taken as a measure of the reactivity of the system. The correlation of a with reactivity is scattered but the trend is in the expected direction. The results are quite similar to those shown for the ionization of ketones in Table 2. For the proton transfers shown in Table 9 the Bronsted exponent has not reached the limiting value of zero or unity even when reaction in one direction is very strongly thermodynamically favourable. The rate coefficient in the favourable direction is probably well below the diffusion limit, although this cannot be checked for the vinyl ethers. Non-limiting values for the Bronsted exponent have also been measured in the hydrolysis of other vinyl ethers [176]. [Pg.162]

From the measured or simulated time variations of the concentrations of the three different species, one estimates the values of the three different factors they are equal to zero when the considered substrate or product is non-limiting and they increase when the substrate level becomes too low or the byproduct concentration too high. [Pg.175]

We note in passing, that there is no particle size effect on the H2-oxidation rate over Pt, although the Volmer reaction, the non-limiting step, is faster on the larger crystallites. [Pg.276]

Non-limited EPR entanglement in time-modulated quantum dissipative dynamics... [Pg.115]

Of the eight classes of samples introduced in the preceding section, comparison of the loop-gap resonator with the TE102 cavity resonator leads to the following conclusions. The loop gap is markedly superior for the four classes of limited samples, and for the two unlimited classes that are additionally nonsaturable . A more careful comparison is required for the two categories non-limited, high loss, saturable and non-limited, low loss, saturable . [Pg.136]

This last category, non-limited, low loss, saturable , is suitable for gas phase ESR or for liquid phase experiments in very low loss solvents such as heptane or benzene. In principle, best performance is obtained by filling the resonator with sample and employing a resonator of the highest possible Q, such as one oscillating in the cylindrical TEqh mode. [Pg.136]

The category of non-limited, high loss, saturable is problematical. The present experience is that the sensitivity is about the same expressed on a molarity basis when comparing the TE102 and loop-gap resonator, even though 20 times less material is required in the latter. This perspective may shift to favor the loop-gap resonator in the future by increased use of the dispersion mode at high powers, as mentioned in the preceding section and described in Ref. 53. [Pg.136]

The parameters are maximum growth rate z, and minimum or subsistence quota k(Q. The variable /> is a luxury coefficient (/ 1 for non-limiting nutrient), empirically defined for a given species by ... [Pg.349]

The results of this biodegradation analysis, which was carried out under non-limiting conditions (nutrients, nitrogen sources, oxygen) are summarized in Table 3. [Pg.81]

There were three sites (7, 8 and 13) where no degradation of ETBE was observed, even after a long period of incubation (about one year). Two of these sites were in the USA and showed efficient degradation of MTBE (sites 7 and 8). Four sites, all of which were in Europe, showed efficient degradation of ETBE (2, 3, 5 and 6). There were seven intermediate cases with a very low biodegradation of ETBE, even under non-limiting conditions, suggesting these were poor candidates for natural attenuation (sites 1,4, 9, 11,8,14). [Pg.85]

The oxidation reactions are catalyzed in the sample by the action of microorganisms already present in natural water. If you suspect that the sample will have a high BOD, you have to dilute the water sample with pure oxygen-saturated water. This is necessary to be sure that oxygen is non-limiting to oxidize all the organic matter. The results are corrected for this dilution. [Pg.194]


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See also in sourсe #XX -- [ Pg.325 ]




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Limitations on non-steady-state kinetic behaviour imposed by the reaction mechanism

Non-Gaussian Behavior Related to Limited Chain Extensibility

Non-adiabatic limit

Non-draining limit

Non-relativistic limit

Spin-Interactions and the Non-relativistic Limit of Electrodynamics

The Non-Relativistic Limit

The non-relativistic limit of electrodynamics

Thermodynamic limitations on non-steady-state kinetic behaviour

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