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Limits of Confidence

Considering Fig. 5.6, we observe that, if we have a very high confidence level, then 1 — a l and the domain for the existence of parameters (p, o ) is high. As far as our scope is to produce the relations between the population and the selection characteristics, i.e. between the couples (p, o ) and (x, s ), we can write Eq. (5.17) in a state that introduces the mean value (x) and volume (n) of the selection. In relation (5.34) the population mean value has been divided into n parts. Now, if for each interval aj i — a , the population mean value is compared with the mean [Pg.342]

Now if we consider the population variance (dispersion), each identical interval a i — a presents a dispersion which depends on the global ct, thus, we can write  [Pg.343]

The above relation shows that each of the n divisions of the population has the CT /n dispersion. Now, considering that a division x — p is a normal random variable and that the mean value of this variable is zero, we can transform relation (5.22) into relation (5.37) where u keeps its initial properties (mean value is zero and dispersion equal to unity)  [Pg.343]

The intersection of the expressions contained in Eq. (5.38) gives the expression for the confidence interval I =  [Pg.343]

When the selection contains a small number of measurements (for example n 25), the confidence interval for the mean value will be obtained by the use of the dimensionless Student variable given here by the current value (5.39)  [Pg.344]


Software tools for computational chemistry are often based on empirical information. To use these tools, you need to understand how the technique is implemented and the nature of the database used to parameterize the method. You use this knowledge to determine the most appropriate tools for specific investigations and to define the limits of confidence in results. [Pg.7]

Since detailed chemical kinetic mechanisms involve the participation of a large number of species in a large number of elementary reactions, sensitivity and reaction path analyses are also essential elements of DCKM. Sensitivity analysis provides a means to assess the limits of confidence we must put on our model predictions in view of uncertainties that exist in reaction rate parameters and thermochemical and thermophysical data utilized, as well as the initial and boundary conditions used in the modeling work. Through... [Pg.98]

Heemken et al. [90] compared ASE and SFE with Soxhlet, sonication, and methanolic saponificaion extraction (MSE) for the extraction of PAHs, aliphatic and chlorinated hydrocarbons from a certified marine sediment samples, and four suspended particulate matter (SPM) samples. Average PAH recovery in three different samples using SFE was between 96 and 105% of that by Soxhlet, sonication, and MSE for ASE the recovery was between 97 and 108%. Compared to the certified values of sediment HS-6, the average recoveries of SFE and ASE were 87 and 88% for most compounds the results were within the limits of confidence. For alkanes, SFE recovery was between 93 and 115%, and ASE recovery was between 94 and 107% of that by Soxhlet, sonication, and MSE. While the natural water content of the SPM sample (56%) led to insufficient recovery by ASE and SFE, quantitative extractions were achieved in SFE after addition of anhydrous sodium sulfate to the sample. [Pg.177]

Fig. 27. Boundaries separating the regions of steady-state and auto-oscillation regimes of binary copolymerization in CSTR. Curve 2 is calculated for kinetic parameters resulting in the best approximation of experimental data reported in Ref. [345] curves 1 and 3 are calculated at the limits of confidence interval of the values of these parameters [17, 6]... Fig. 27. Boundaries separating the regions of steady-state and auto-oscillation regimes of binary copolymerization in CSTR. Curve 2 is calculated for kinetic parameters resulting in the best approximation of experimental data reported in Ref. [345] curves 1 and 3 are calculated at the limits of confidence interval of the values of these parameters [17, 6]...
A more common method for medical devices is to run the life test until failure occurs. Then an exponential model can be used to calculate the percentage survivability. Using a chi-square distribution, limits of confidence on this calculation can be established. These calculations assume that a failure is equally likely to occur at any time. If this assumption is unreasonable (e.g., if there are a number of early failures), it may be necessary to use a Weibull model to calculate the mean time to failure. This statistical model requires the determination of two parameters and is much more difficult to apply to a test that some devices survived. In the heart-valve industry, lifetime prediction based on S-N (stress versus number of cycles) or damage-tolerant approaches is required. These methods require fatigue testing and ability to predict crack growth. " ... [Pg.336]

The features to be determined to validate a procedure are repeatability (within-run) and intermediate (between-run) precision, limit of detection, limit of quantification, linearity of the response of the assay, specificity of the assay and whether there are any interferences, its trueness, the vmcertainty associated with an individual result with a stated limit of confidence, and appropriate reference ranges. While examining these topics further information relevant to reagent stability, necessary frequency of recalibration, suitable IQC protocol, and overall assay weakness will be obtained. [Pg.4083]

The conventional MO methods show substantial improvement with increase in basis size. The mean absolute error is reduced by a factor of 3-4 for the MP4 and F4 methods. The improvement is not as great for the MP2 method which still shows significant deviations and several systems where the error in the calculated acidity exceeds 10 kJ mol". The G2 methods all perform extremely well. Mean absolute deviations range from 4.5 to 4,6 kJ mol". Only for one system, CFI2NH for which there is a large quoted limit of confidence (22 kJ mol" ) in its determination, does the calculated acidity exceed the acceptable range. Acidities predicted by the three G2 methods seldom differ by more than 3 kJ mol" from one another, and show mean absolute deviations of just 1.3 kJ mol". ... [Pg.2275]

In Section 4D.2 we introduced two probability distributions commonly encountered when studying populations. The construction of confidence intervals for a normally distributed population was the subject of Section 4D.3. We have yet to address, however, how we can identify the probability distribution for a given population. In Examples 4.11-4.14 we assumed that the amount of aspirin in analgesic tablets is normally distributed. We are justified in asking how this can be determined without analyzing every member of the population. When we cannot study the whole population, or when we cannot predict the mathematical form of a population s probability distribution, we must deduce the distribution from a limited sampling of its members. [Pg.77]

Because exceeds the confidence interval s upper limit of 0.346, there is reason to believe that a 2 factorial design and a first-order empirical model are inappropriate for this system. A complete empirical model for this system is presented in problem 10 in the end-of-chapter problem set. [Pg.682]

Measurement Method Selection. A measurement method should meet sampling strategy requirements to the degree that the data can be used for decision making. This does not mean that it must be the optimum method with respect to all requirements. The range of methods available is limited and it is often necessary to select a method deficient in one or more attributes but which can yield data from which conclusions can be drawn with the desired degree of confidence. Some of the attributes to be considered in selecting a method foUow. [Pg.107]

In defining acute level toxicity foi the purposes of comparing different materials, the LD q itself is not sufficient but the LD q and the 95% confidence limits should be quoted as a minimum. For example, and as demonstrated in Figure 8, two materials (A and B) with different LD q values, but overlapping 95% confidence limits, ate to be considered not statistically significantly different with respect to mortahty at the 50% level this it based on the fact that there is a statistical probabiUty that the LD q of one material could He in the 95% confidence limits of the other, and vice versa. Conversely, when there is no overlap in 95% confidence limits, as shown with material C, it may be concluded that the LD q values ate statistically significantly different. [Pg.234]

Confidence The accuracy of the conclusions drawn from any unit test depends upon the accuracy of the laboratory analyses. Plant-performance analysts must have confidence in these analyses including understanding the methodology and the limitations. This confidence is established through discussion, analyses of known mixtures, and analysis of past laboratory results. This confidence is established during the preparation stage. [Pg.2558]

If there is a lack of specific, appropriate data for a process facility, there can be considerable uncertainty in a frequency estimate like the one above. When study objectives require absolute risk estimates, it is customary for engineers to want to express their lack of confidence in an estimate by reporting a range estimate (e.g., 90% confidence limits of 8 X 10 per year to 1 X 10 per year) rather than a single-point estimate (e.g., 2 X 10per year). For this reason alone it may be necessary for you to require that an uncertainty analysis be performed. [Pg.39]

Further statistical procedures can be applied to determine the confidence limits of the results. Generally, only the values for the mean and standard deviation would be reported. The reader is referred to any good statistical text to expand on the brief analysis presented here. [Pg.536]

Uncertainty - displays distribution and confidence limits of a system, sequence, or end state for both base and current data values. [Pg.139]

The confidence limits of a measurement are the limits between which the measurement error is with a probability P. The probability P is the confidence level and a = 1 - P is the risk level related to the confidence limits. The confidence level is chosen according to the application. A normal value in ventilation would be P = 95%, which means that there is a risk of a = 5 /o for the measurement error to be larger than the confidence limits. In applications such as nuclear power plants, where security is of prime importance, the risk level selected should be much lower. The confidence limits contain the random errors plus the re.sidual of the systematic error after calibration, but not the actual systematic errors, which are assumed to have been eliminated. [Pg.1129]

Since the confidence limits of a repeated measurement are based on the dispersion of the measurement result, they usually are presented as symmetrical limits ... [Pg.1129]

Frequently the value of the quantity of interest has to be determined indirectly. For example, the determination of the efficiency of any system is based on the measurement of several quantities and some equation relating the measured quantities X, and the final quantity Y under consideration. When the confidence limits of the different measured quantities are known, and the relationship y = f(X,) is known, an estimate for the cumulated confidence limits dy of the final quantity can be determined from... [Pg.1130]

The bias error is a quantity that gives the total systematic error of a measuring instrument under defined conditions. As mentioned earlier, the bias should be minimized by calibration. The repeatability error consists of the confidence limits of a single measurement under certain conditions. The mac-curacy or error of indication is the total error of the instrument, including the... [Pg.1130]

Figure 12.12 demonstrates that the larger the confidence limits of measurement are, the closer to the target value the measurement result must be for symmetrical tolerances. A consequence of this is that if the confidence limits of... [Pg.1131]

It should be noted that data were not rejected through consideration of upper or lower bounds. These limits for the input data included a variety of assumed and calculated limits using various levels of confidence. [Pg.128]

To.xicity values for carcinogenic effects can be e.xprcsscd in several ways. The slope factor is usually, but not always, the upper 95th percent confidence limit of the slope of the dose-response curve and is e.xprcsscd as (mg/kg-day). If the extrapolation model selected is the linearized multistage model, this value is also known as the ql. That is ... [Pg.337]


See other pages where Limits of Confidence is mentioned: [Pg.342]    [Pg.169]    [Pg.280]    [Pg.45]    [Pg.342]    [Pg.169]    [Pg.280]    [Pg.45]    [Pg.17]    [Pg.211]    [Pg.108]    [Pg.232]    [Pg.235]    [Pg.293]    [Pg.426]    [Pg.232]    [Pg.324]    [Pg.2548]    [Pg.454]    [Pg.58]    [Pg.145]    [Pg.350]    [Pg.143]    [Pg.1130]    [Pg.1130]    [Pg.1130]    [Pg.180]    [Pg.266]    [Pg.405]    [Pg.15]    [Pg.319]    [Pg.336]   


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Analysis of Statistical Confidence Limits

Confidence

Confidence Limits of the Distribution

Confidence limits

Confidence limits of the geometric mean for a log-normal distribution

Confidence limits of the mean

Confidence limits of the mean for large samples

Confidence limits of the mean for small samples

Distribution of Errors and Confidence Limits

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