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Maximum model

Figure 12. Efficiency, lifetime, and intensity of single-maximum model. Figure 12. Efficiency, lifetime, and intensity of single-maximum model.
The NOSV gives a better estimate of the detectability of marine oil pollution, independently of the local wind conditions of this particular study. These results show that higher wind speeds cause lower detectability of oil pollution, and the maximum (model) wind speed where oil spill detection in European coastal waters can be inferred. In particular, at wind speeds below 7 m s 1 oil spills are well detectable, whereas above 10 m s 1 wind speed the definite detection of marine oil pollution seems to be almost impossible. At wind speeds between 7 and 10 m s 1 the detectability of oil spills is rather low. These results can explain why less oil pollution was detected in the northern test areas during winter time. E.g., the mean wind speed in the central North Sea during winter time lies above 10 ms"1 (Figure 5), thus making it unlikely that every oil spill in that area was detectable by SAR sensors. [Pg.199]

The 3D Systems Thermojet Printer [38] also uses a demand mode piezoelectric array printhead dispensing a thermoplastic material to build solid models. Printing resolutions (actually addressability) of 300, 400, and 600 dot per inch (drop spacings of 85 pm, 63 pm, and 42 pm) are claimed. The maximum model size is 25 cm x 19 cm x 20 cm. [Pg.232]

The Objet Quadra, recently developed by Objet Geometries Ltd., prints a photopolymer at 600 dots per inch in X and T, and uses a 20-pm layer thickness. The photopolymer is cured during printing so not postprocessing is required. A support material is also printed where required. The maximum model size is 27 cm x 30 cm x 20 cm. [Pg.232]

With their natural logarithm, the data in Table 2 and Table 3 were input to the Eq. (1) to build early-warning models in R environment (Wold, et al., 2001, Mevik Wehrens, 2007), respectively. The model parameters in Chongqing City and Ningbo City were shown in Table 5. One was called Chongqing Model, the other was named Ningbo model. All the models were assessed by Leave-One-Out Cross Validation method (LOOCV), and the maximum model error was less than 15%. [Pg.1275]

If this criterion is based on the maximum-likelihood principle, it leads to those parameter values that make the experimental observations appear most likely when taken as a whole. The likelihood function is defined as the joint probability of the observed values of the variables for any set of true values of the variables, model parameters, and error variances. The best estimates of the model parameters and of the true values of the measured variables are those which maximize this likelihood function with a normal distribution assumed for the experimental errors. [Pg.98]

In the maximum-likelihood method used here, the "true" value of each measured variable is also found in the course of parameter estimation. The differences between these "true" values and the corresponding experimentally measured values are the residuals (also called deviations). When there are many data points, the residuals can be analyzed by standard statistical methods (Draper and Smith, 1966). If, however, there are only a few data points, examination of the residuals for trends, when plotted versus other system variables, may provide valuable information. Often these plots can indicate at a glance excessive experimental error, systematic error, or "lack of fit." Data points which are obviously bad can also be readily detected. If the model is suitable and if there are no systematic errors, such a plot shows the residuals randomly distributed with zero means. This behavior is shown in Figure 3 for the ethyl-acetate-n-propanol data of Murti and Van Winkle (1958), fitted with the van Laar equation. [Pg.105]

The maximum-likelihood method is not limited to phase equilibrium data. It is applicable to any type of data for which a model can be postulated and for which there are known random measurement errors in the variables. P-V-T data, enthalpy data, solid-liquid adsorption data, etc., can all be reduced by this method. The advantages indicated here for vapor-liquid equilibrium data apply also to other data. [Pg.108]

The importance of distinct a priori knowledge account becomes more perceptible if noisy data are under restoration. The noise / ( shifts the solution of (1) from the Maximum Likelihood (ML) to the so called Default Model for which the function of the image constraint becomes more significant. [Pg.117]

To verify the modelling of the data eolleetion process, calculations of SAT 4, in the entrance window of the XRII was compared to measurements of RNR p oj in stored data as function of tube potential. The images object was a steel cylinder 5-mm) with a glass rod 1-mm) as defect. X-ray spectra were filtered with 0.6-mm copper. Tube current and exposure time were varied so that the signal beside the object. So, was kept constant for all tube potentials. Figure 8 shows measured and simulated SNR oproj, where both point out 100 kV as the tube potential that gives a maximum. Due to overestimation of the noise in calculations the maximum in the simulated values are normalised to the maximum in the measured values. Once the model was verified it was used to calculate optimal choice of filter materials and tube potentials, see figure 9. [Pg.212]

The GammaMat M isotope pipeline crawlers previously have been used with exposure cameras for iridium the models M6 and Ml 8 used exposure units designed for a maximum loading of 2.2 TBq (60Ci) and 3.7 TBq (lOOCi), respectively. [Pg.427]

Introducing the Selenium for gammagraphic weld inspection at significantly improved quality levels of the radiographs we have also designed an exposure unit for Selenium. This unit is fuUy compatible with both models, M6 and Ml8. Different from the exposure units for iridium, which are Type B(U) containers, the Source Projector M-SE for Selenium is a Type A container with a maximum loading of 3 TBq (80Ci) Selenium. [Pg.427]

It has been pointed out [138] that algebraically equivalent expressions can be derived without invoking a surface solution model. Instead, surface excess as defined by the procedure of Gibbs is used, the dividing surface always being located so that the sum of the surface excess quantities equals a given constant value. This last is conveniently taken to be the maximum value of F. A somewhat related treatment was made by Handa and Mukeijee for the surface tension of mixtures of fluorocarbons and hydrocarbons [139]. [Pg.89]

Bianco and Marmur [143] have developed a means to measure the surface elasticity of soap bubbles. Their results are well modeled by the von Szyszkowski equation (Eq. III-57) and Eq. Ill-118. They find that the elasticity increases with the size of the bubble for small bubbles but that it may go through a maximum for larger bubbles. Li and Neumann [144] have shown the effects of surface elasticity on wetting and capillary rise phenomena, with important implications for measurement of surface tension. [Pg.90]

The solution flow is nomially maintained under laminar conditions and the velocity profile across the chaimel is therefore parabolic with a maximum velocity occurring at the chaimel centre. Thanks to the well defined hydrodynamic flow regime and to the accurately detemiinable dimensions of the cell, the system lends itself well to theoretical modelling. The convective-diffiision equation for mass transport within the rectangular duct may be described by... [Pg.1937]


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See also in sourсe #XX -- [ Pg.149 ]

See also in sourсe #XX -- [ Pg.163 ]




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