To our knowledge, no study exists that uses more than one set of empirical age– concentration CSD collected in different years to estimate intrinsic elimination half-lives.
Most empirical studies on concentration choose (alpha =2) (Davis 1998; Storper et al. 2002; Aiginger and Pfaffermayr 2004; Beine and Coulombe 2007), and we follow this approach.
Analysis of the applicability of different electronegativity scales (XAllen, XPauling, and XMulliken) as a replacement for the empirical valence electron concentration (VEC) parameter to determine High Entropy Alloy (HEA) solid-solution stability is performed, using statistical methods (via cluster analysis and probability density function).
In order to develop a model description that can predict the extent of the protective effect exerted by FXa against APC proteolysis of FVa over a range of reactant concentrations, empirical experiments were performed at saturating and non-saturating concentrations of FXa.
Although six model groups did not closely predict empirical methyl mercury concentrations, four of these entities were pooled groups (other toothed cetaceans, other deepwater fishes, benthos, and zooplankton).
Our results are based on statistical methodologies designed to separate the natural and anthropogenic contributions in monitored concentrations by modeling the empirical distribution of the detected concentration with a mixture of probability density functions.
Using these data, we have developed an empirical model for nanoparticle concentration reduction using recirculation air filtration and evaluated the model against experimental data of nanoparticle concentration reductions while generating airborne silver nanoparticles in an enclosed area.
The use of empirical equations for stress concentration factor calculation, however, gave clearly erroneous results.
We searched for empirical studies addressing the concentration of victimization in journal articles, academic institutions, and government reports.
