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Fitting data compound

The Antoine equation does not fit data accurately much above the normal boiling point. Thus, as regression by computer is now standard, more accurate expressions applicable to the critical point have become usable. The entire DIPPR Compilation" is regressed with the modified RiedeP equation (2-28) with constants available for over 1500 compounds. [Pg.389]

Table III lists the material balances for the preparative separations. These are the percent weight recoveries for either asphaltene or maltene defined, using the sulfur balance for an example, as the sum of the amount of sulfur in each cut times the cut weight percent divided by the total sulfur. In general, the balances are in the 80-120% range, which is reasonable considering the amount of sample handling involved. The recoveries are out of line only in a few cases, most notably the Prudhoe Bay maltene nickel balance. In addition, a comparison of the calculated elemental values for the total residua differ somewhat from the raw total values for several residua. These discrepancies are probably attributable to the small samples, multiple sample manipulations, and compounding of individual errors when the asphaltene and maltene data are summed. The data-fitting routine described in the next section was used to obtain a set of best fit data, which were used in the subsequent size calculations. Table III lists the material balances for the preparative separations. These are the percent weight recoveries for either asphaltene or maltene defined, using the sulfur balance for an example, as the sum of the amount of sulfur in each cut times the cut weight percent divided by the total sulfur. In general, the balances are in the 80-120% range, which is reasonable considering the amount of sample handling involved. The recoveries are out of line only in a few cases, most notably the Prudhoe Bay maltene nickel balance. In addition, a comparison of the calculated elemental values for the total residua differ somewhat from the raw total values for several residua. These discrepancies are probably attributable to the small samples, multiple sample manipulations, and compounding of individual errors when the asphaltene and maltene data are summed. The data-fitting routine described in the next section was used to obtain a set of best fit data, which were used in the subsequent size calculations.
It is difficult to fit data with the local composition models due to their complex logarithmic forms. However, they are readily generalizable to multicomponent systems. Smith, van Ness, and Abbott and Prausnitz, Lichtenthaler, and Gomes de Azevedo present the Wilson and UNIQUAC models extended for multi-component solutions. They both employ the constants from binary data. However, the constants are not unique in the sense that valid, but different constants may be obtained from different sets of data. Wilson s equations cannot be employed for immiscible solutions, but the UNIQUAC model may be used to describe such solutions. However, Wilson s equations are good for polar or associating compounds. A compilation of Wilson parameters can be found by Hirata, Ohe, and Nagahama. ... [Pg.2005]

Although the two-period crossover design has certain intrinsic weaknesses, intra-individual variation is usually smaller than variation between subjects, and bioequivalence can usually be established using a smaller number of subjects in a crossover study. The order in which subjects receive single doses of the different formulations must be randomised and an adequate interval allowed between doses to ensure washout. The number of subjects will depend on the variability of the kinetics of the compound. A power calculation should be performed using historical data, if possible. In practice, the minimum number of volunteers needed is 12 and the maximum usually about 24 but is occasionally more. The number and times of blood samples is a critical a sufficient number of samples is required around the to permit and to be identified with adequate accuracy. Sampling should continue for at least 3-4 half-lives and later samples should be spaced so that no more than about 15% (or ideally 10%) of the AUC has to be determined by extrapolation or interpolation between points. Model-fitted data are usually not acceptable should be obtained directly from the observed concentration data and... [Pg.229]

The absence of specific guidelines, or legal requirements for toxicity data submission on specified studies places the Health Protection Branch in the position that it can require any type of study prior to establishing maximum residue limits, or recommending registration to Agriculture Canada. This provides the advantage that each compound can be considered individually, and the data requirements can be tailored to fit the compound. [Pg.540]

In order to assess how the Maier and Goritz model meets experimental data, we used a nonlinear algorithm (i.e., Marquart-Levensberg) to fit data obtained by Gerspacher et al7 on a series of SBR filled compounds (see Appendix 5.6), with Equations 5.59a and b (Figure 5.50). [Pg.170]

Fitting data on 0.049 silica weight fraction compound... [Pg.311]

The first step in developing a QSPR equation is to compile a list of compounds for which the experimentally determined property is known. Ideally, this list should be very large. Often, thousands of compounds are used in a QSPR study. If there are fewer compounds on the list than parameters to be fitted in the equation, then the curve fit will fail. If the same number exists for both, then an exact fit will be obtained. This exact fit is misleading because it fits the equation to all the anomalies in the data, it does not necessarily reflect all the correct trends necessary for a predictive method. In order to ensure that the method will be predictive, there should ideally be 10 times as many test compounds as fitted parameters. The choice of compounds is also important. For... [Pg.243]

The field points must then be fitted to predict the activity. There are generally far more field points than known compound activities to be fitted. The least-squares algorithms used in QSAR studies do not function for such an underdetermined system. A partial least squares (PLS) algorithm is used for this type of fitting. This method starts with matrices of field data and activity data. These matrices are then used to derive two new matrices containing a description of the system and the residual noise in the data. Earlier studies used a similar technique, called principal component analysis (PCA). PLS is generally considered to be superior. [Pg.248]

Revised material in Section 5 includes an extensive tabulation of binary and ternary azeotropes comprising approximately 850 entries. Over 975 compounds have values listed for viscosity, dielectric constant, dipole moment, and surface tension. Whenever possible, data for viscosity and dielectric constant are provided at two temperatures to permit interpolation for intermediate temperatures and also to permit limited extrapolation of the data. The dipole moments are often listed for different physical states. Values for surface tension can be calculated over a range of temperatures from two constants that can be fitted into a linear equation. Also extensively revised and expanded are the properties of combustible mixtures in air. A table of triple points has been added. [Pg.1287]

Hctivity Coefficients. Most activity coefficient property estimation methods are generally appHcable only to pure substances. Methods for properties of multicomponent systems are more complex and parameter fits usually rely on less experimental data. The primary group contribution methods of activity coefficient estimation are ASOG and UNIEAC. Of the two, UNIEAC has been fit to more combinations of groups and therefore can be appHed to a wider variety of compounds. Both methods are restricted to organic compounds and water. [Pg.253]

The regression constants A, B, and D are determined from the nonlinear regression of available data, while C is usually taken as the critical temperature. The hquid density decreases approximately linearly from the triple point to the normal boiling point and then nonhnearly to the critical density (the reciprocal of the critical volume). A few compounds such as water cannot be fit with this equation over the entire range of temperature. Liquid density data to be regressed should be at atmospheric pressure up to the normal boihng point, above which saturated liquid data should be used. Constants for 1500 compounds are given in the DIPPR compilation. [Pg.399]

Table 15 [S 19 56, 59 93 107 108 109, 110, 111, 112 113, 114] contams NMR data for a vanety of tnfluoromethyl compounds that do not fit into the more common categones already covered Most carbon-attached tnfluoromethyl (CF3-C) F-NMR signals fall in the 25 ppm range from -60 to -85 ppm, a notable exception being trifluoromethylacetylenes, with signals at approximately -50 ppm Trifluoromethylated compounds in which the CFj is directly bonded to an atom orlier carton are considered in Table 16 [57 59,95 109,115,116 117 118,119,120 121 122, 123 124, 125] These heteroatom contaming compounds are of interest to both organic and morganic chemists and have been studied by NMR for numerous reasons... Table 15 [S 19 56, 59 93 107 108 109, 110, 111, 112 113, 114] contams NMR data for a vanety of tnfluoromethyl compounds that do not fit into the more common categones already covered Most carbon-attached tnfluoromethyl (CF3-C) F-NMR signals fall in the 25 ppm range from -60 to -85 ppm, a notable exception being trifluoromethylacetylenes, with signals at approximately -50 ppm Trifluoromethylated compounds in which the CFj is directly bonded to an atom orlier carton are considered in Table 16 [57 59,95 109,115,116 117 118,119,120 121 122, 123 124, 125] These heteroatom contaming compounds are of interest to both organic and morganic chemists and have been studied by NMR for numerous reasons...
Considering that the parameters for the MNDO/d method for all first row elements (which are present in most of the training set of compounds) are identical to MNDO, the improvement by addition of d-functions is quite impressive. It should also be noted that MNDO/d only contains 15 parameters, compared to 18 for PM3, and that some of the 15 parameters are taken from atomic data (analogously to the MNDO/AMl parameterization), and not used in the molecular data fitting as in PM3. [Pg.92]


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