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Estimation of distribution

The line the data supports on a hazard plot determines engineering information relating to the distribution of time to failure. Fan failure data and simulated data are illustrated here to explain how the information is obtained. The methods provide estimates of distribution parameters, percentiles, and probabilities of failure. The methods that give estimates of distribution parameters differ slightly from the hazard paper of one theoretical distribution to another and are given separately for each distribution. The methods that give estimates of distribution percentiles and failure probabilities are the same for all papers and are given first. [Pg.1050]

When a set of data does not plot as a straight line on any of the available papers, then one may wish to draw a smooth curve through the data points on one of the plotting papers, and use the curve to obtain estimates of distribution percentiles and probabilities of failure for various given times. With such a nonparametric fit to the data, it is usually unsatisfactory to extrapolate beyond the data because it is difficult to determine how to extend how to extend the curve. Nonparametric fitting is best used only if the data contain a reasonably large number of failures. [Pg.1053]

If estimated of distribution parameters are desired from data plotted on a hazard paper, then the straight line drawn through the data should be based primarily on a fit to the data points near the center of the distribution the sample is from and not be influenced overly by data points in the tails of the distribution. This is suggested because the smallest and largest times to failure in a sample tend to vary considerably from the true cumulative hazard function, and the middle times tend to lie close to it. Similar comments apply to the probability plotting. [Pg.1053]

It does not contain a probabilistic modeling component that simulates variability therefore, it is not used to predict PbB probability distributions in exposed populations. Accordingly, the current version will not predict the probability that children exposed to lead in environmental media will have PbB concentrations exceeding a health-based level of concern (e.g., 10 pg/dL). Efforts are currently underway to explore applications of stochastic modeling methodologies to investigate variability in both exposure and biokinetic variables that will yield estimates of distributions of lead concentrations in blood, bone, and other tissues. [Pg.243]

The plasma concentration at when divided by the dose gives an estimate of distribution volume that can be used to calculate dosing for fast equilibrating drug, in particular, such as anesthetics. This distribution volume term often proves more useful than the traditional central volume of distribution or the steady-state distribution volume. [Pg.367]

In Section 3.3, the background material developed in Section 3.2 is used in a discussion of practical issues involved in the selection of distributions, particularly for models of pesticide ecological risk. The topics discussed include data representativeness, preliminary data exploration, selection of distribution type, estimation of distribution parameters (distribution fitting), and evaluation of distribution fit. [Pg.33]

Gilliom RJ, Helsel DR. 1986. Estimation of distributional parameters for censored trace level water quality data 1. Estimation techniques. Water Resour Res 22 135-146. [Pg.51]

Implement hierarchical approaches, along with professional judgment, and reference to other cases, to account for uncertainty in the estimation of distribution parameters. [Pg.170]

Koontz, M.D. and H.E. Rector (1995). Estimation of Distributions for Residential Air Exchange Rates, USEPA Contract No. 68-D9-0166, United States Environmental Protection Agency, Washington, DC, USA. [Pg.240]

The value of in this equation is not V g xtrap) instead it represents a second estimate of distribution volume, referred to as Vii area) or d(ft) that generally is estimated from measured elimination half-life and clearance. The similarity of these two estimates of distribution volume reflects the extent to which drug distribution is accurately described by a singlecompartment model, and obviously varies from drug to drug (15). [Pg.16]

The three estimates of distribution volume that we have encountered have slightly different properties (24). Of the three, Vd(ss) has the strongest physiologic rationale for multicompartment systems of drug distribution. It is independent of the rate of both drug distribution and elimination, and is the volume that is referred to in Equations 3.1 and 3.2. On the other hand, estimates of V ( area) most useful in clinical pharmacokinetics, since it is this volume that links elimination clearance to elimination half-life in the equation... [Pg.34]

A further OECD Council Decision in 1991 focused on HPV chemicals. These decisions prompted the development of a minimum hazard data set to describe an HPV chemical - the Screening Information Data Set, or SIDS. This includes physicochemical properties (melting point, boiling point, vapor pressure, water solubility, and octanol-water partition coefficient) environmental fate (stability in water, photodegradation, biodegradation, and an estimate of distribution/transport in the environment) environmental effects (acute toxicity to aquatic vertebrates, invertebrates, and plants) and human health effects (acute toxicity, repeated-dose toxicity, toxicity to the gene and the chromosome, and reproductive and developmental toxicity). [Pg.1337]

Ideally, the group of reference individuals should be a random sample of all the individuals fulfilling the defined inclusion criteria in the parent population. Statistical estimation of distribution parameters (and their confidence intervals) and statistical hypothesis testing require this assumption. [Pg.429]

The nonparametric method makes no assumptions concerning the type of distribution and does not use estimates of distribution parameters. The percentiles may simply be determined by cutting off the required percentage of values in each tail of the subset reference distribution. [Pg.435]

Gilliom RJ, Helsel DR (1986) Estimation of distributional parameters for censored trace level water quality data. 1. Estimation techniques. Water Resour Res 22 135-146 Goldoni M, Caglieri A, Poli D, Vettori M, Corradi M, Apostoli P, Mutti A (2006) Determination of hexavalent chromium in exhaled breath condensate and environmental air among chrome... [Pg.36]

E. Dabek-Zlotorzynska, M. Kelly, H. Chen and C.L. Chakrabarti, Application of capillary electrophoresis combined with a modified BCR sequential extraction for estimating of distribution of selected trace metals in PM2.5 fractions of urban air particulate matter, Chemosphere, 58,1365-1376, 2005. [Pg.973]

An alternative to maintaining a population of solutions is to build a model of some aspect of the fitness function and use that to guide the search. One well studied method is to model the probability of each variable taking each of its possible values in a good solution. As the model evolves, new candidate solutions are drawn from the model s distribution, which in turn cause the model to be updated. This approach is known as an Estimation of Distribution Algorithm (EDA) and is described in more detail in Sect. 2. [Pg.249]

Santana, R. Estimation of distribution algorithms from available implementations to potential developments. In Proceedings of the 13th Annual Conference Companion on Genetic and Evolutionary Computation, pp. 679-686. ACM (2011)... [Pg.271]

A thermodynamic equilibrium method is used to determine the equilibrium ratio of concentrations of the low-molecular-mass substances in materials in contact. The equilibrium state is usually determined with the help of kinetic curves of mass change in bodies in contact versus time. The analysis of this data permits estimation of distribution coefficients between the studied materials. A long experiment duration (usually a few months at room temperature) is a serious hindrance. If data must be collected at sub-zero temperatures, the experiment may take several years. [Pg.161]

Figure 7.18 depicts the particle distribution in a twin-screw element after a certain flow time, after having been initially inserted in the gap between the screws. A quantitative estimation of distributive mixing could be applied to this data. [Pg.348]

Monte Carlo Estimates of Distribution with Improved Electrostatic Potentials. [Pg.371]

Samii, S., Rafiliu, S., Eles, P. Peng, Z. (2008). A Simulation Methodology for Worst-Case Response Time Estimation of Distributed Real-Time Systems, Proceedings of Design, Automation, and Test in Europe (DATE 08), pp. 556-561. [Pg.29]

Larranaga, P. and Lozano, J.A. (2002). Estimation of Distribution Algorithms, Kluwer, Boston, 382 p. [Pg.39]


See other pages where Estimation of distribution is mentioned: [Pg.1041]    [Pg.1050]    [Pg.1050]    [Pg.1051]    [Pg.1053]    [Pg.332]    [Pg.85]    [Pg.89]    [Pg.532]    [Pg.43]    [Pg.481]    [Pg.640]    [Pg.354]    [Pg.248]    [Pg.251]    [Pg.251]    [Pg.40]    [Pg.488]    [Pg.93]    [Pg.258]    [Pg.295]    [Pg.301]    [Pg.27]    [Pg.171]   
See also in sourсe #XX -- [ Pg.9 , Pg.89 , Pg.91 ]




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