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Long-term decay parameters

Figure 4. Long-term decay parameters (r2, equation 1) for d33 of (PS)O-NPP films simultaneously corona poled and cross-linked with the indicated equivalents of 1,4-butanediol diglycidyl ether/equiv-alents available phenol OH groups. Figure 4. Long-term decay parameters (r2, equation 1) for d33 of (PS)O-NPP films simultaneously corona poled and cross-linked with the indicated equivalents of 1,4-butanediol diglycidyl ether/equiv-alents available phenol OH groups.
It seems that water absorption serves as one of the key parameters in microbial growth in WPC materials. When a whole cross section of a composite deck board is tested by immersion in water, water absorption after 24 hr is typically between 1 and 3% by weight, after 7 days between 3 and 10%, after 20 days about 8 to 15% (see Chapter 12). These values depend on temperature, and the lower the the temperature, the lower the water absorption [1]. However, water absorption by the top layer of a composite board (1 mm in depth, 50 50 mix of woodiplastic) was in excess of 15% after 24 hr [2]. On other data, water absorption by the 5-mm top layer of Trex deck board in the temperature range from 5 to 25°C was 45 and 60%, respectively. This level of moisture content is well in excess of that necessary to support fungal decay. In fact, authors [1] noticed that when the 25°C trial was run for 30 days using Trex samples, a thick microbial film was developed on the surface of the material. This is a rather common observation in the course of long-term water absorption studies. [Pg.414]

Table 8.4 contains the deactivation parameters estimated from the long-term catalyst stability test and the feedstock evaluation with HCO. d and d are the parameters of the hyperbolic function that describes the initial activity decay caused by coke formation, whereas 3 is the exponent of the power-type function that represents the slow deactivation process by metal deposition (see Equation 8.21). Each set of... [Pg.291]

One of the simplest and therefore computationally less expensive potential functions for ion-water consists of the sum of long-range Coulorabic electrostatic interactions plus short-range dispersion interactions usually represented by the Lennard-Jones potential. This last term is a combination of 6 and 12 powers of the inverse separation between a pair of sites. Two parameters characterize the interaction an energetic parameter e, given by the minimum of the potential energy well, and a size parameter a, that corresponds to the value of the pair separation where the potential energy vanishes. The 6-th power provides the contribution of the attractive forces, while repulsive forces decay with the 12-th power of the inverse separation between atoms or sites. [Pg.444]

It is not unusual for PK research articles to report model parameters for three-, four-, or five-compartment models for some drugs. If the multicompartment model parameters are known for a drug, then the plasma concentration at any time can be predicted by the equations in Table 10.2. Determining the time at which the plasma concentration reaches a particular value is generally a very laborious trial-and-error calculation, since the concentration equation contains multiple exponential decay terms. An exception occurs for plasma concentration Cf) values at long enough times to be located on the terminal line. For this special case, the time at which a particular plasma concentration is reached is given by... [Pg.261]

Curves without E decay rapidly at larger times, while curves with the E term are constant at long time as indicated. Parameters in Table 1. [Pg.244]

Fluorescence decays I(t) of the N groups in N2 and NIO are non-exponra-tial. In the previous discussion we focussed only on the long-lived ccmiponent ii. These decay curves actually fit quite well to a sum of two exponential terms (xsh is the short-lived component), although the magnitude of the individual parameters is probably without significance. [Pg.621]

One of the most fundamental assumptions of the method is the requircment that natural C concentrations in materials of zero " C age in a particular carbon reservoir are equivalent to that which has been characteristic of living oi nisms in that same reservoir over the entire time scale. Generally this assumption is seen to require an eqnilibrinm or steady-state relationship in which the prodnction and decay rates have been in approximate balance. Since the decay rate of " C is constant, the principal variables affecting equilibrium conditions would be changes in the atmospheric prodnction rate of " C, long-and short-term climatic perturbations arrd effects related to variations in the parameters of the carbon cycle such as reservoir sizes and rates of trarrsfer of between differ-... [Pg.171]


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Decay parameter

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