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Test mixture components

Table 5 Number of Theoretical Plates (N) for the Test Mixture Component in Microemulsions Containing Different Organic Solvents with TTAB... Table 5 Number of Theoretical Plates (N) for the Test Mixture Component in Microemulsions Containing Different Organic Solvents with TTAB...
Test Mixture Components and Quantitation Mass Ions ... [Pg.355]

A list of danger categories is given in Table 14.2. Note that chemicals may possess several hazards, e.g. nitric acid is classed as both an oxidizer and a conosive. If a chemical is not in one of these categories it is not generally considered to be dangerous. If the hazards of a new chemical have not been established it should be labelled Caution - substance not yet fully tested . Mixtures can be classified either from results from tests on the preparation, or by calculation to predict the healtli effects of the product based on the properties of individual components and tlieu concentration in the mixture. Preparations need to be classified for both physico-chemical and health effects but, to date, not for environmental effects. [Pg.443]

Their reaction was tested on the individual components of the test mixture indole, ergotamine tartrate, ergotaminine and ergobasine [ergometrine) [3]. The results obtained were as follows ... [Pg.228]

In practice, it is more difficult to optimize resolution as a function of the relative retentlvity than to optimize retention. Thus, unless the mixture is very complex or contains components that are particularly difficult to separate it may be possible to optimize a particular separation using the linear equation (1.72) as demonstrated by Bttre [177]. Figure 1.13 illustrates the relative change in peak position for a polarity test mixture with two identical, serially coupled open tubular columns, coated with a poly(dimethylslloxane) and Carbowax 20 M stationary phases, as a function of their relative retentlvity on the second column. The linear relationship predicted by equation (1.72) effectively predicts the relative peak positions and indicates that a nearly... [Pg.35]

Test mixture should contain components that correctly characterize the column in terms of both kinetic and thermodynamic performance. [Pg.184]

At least two components of the test mixture should have k values between 2 and 10. [Pg.184]

Having chosen the test mixture and mobile diase composition, the chromatogram is run, usually at a fairly fast chart speed to reduce errors associated with the measurement of peak widths, etc.. Figure 4.10. The parameters calculated from the chromatogram are the retention volume and capacity factor of each component, the plate count for the unretained peak and at least one of the retained peaks, the peak asymmetry factor for each component, and the separation factor for at least one pair of solutes. The pressure drop for the column at the optimum test flow rate should also be noted. This data is then used to determine two types of performance criteria. These are kinetic parameters, which indicate how well the column is physically packed, and thermodynamic parameters, which indicate whether the column packing material meets the manufacturer s specifications. Examples of such thermodynamic parameters are whether the percentage oi bonded... [Pg.184]

Figura 2.9 Dse of th Grob test Mixture to compare tbe activity of various glass surfaces coated with ov-ioi. Surface types A > Untreated pyrex glass, B pyrex glass deactivated by thermal degradation of Ceurbowax 20M, C < SCOT column, prepared with Silanox 101, D pyrex glass column coated with a layer of barium carbonate and deactivated as in (B), and E - untreated fused silica. Components are identified in Table 2.7 with ac - 2-ethylhexanoic acid. (Reproduced with permission from ref. 152. Copyright Elsevier Scientific Publishing Co.)... Figura 2.9 Dse of th Grob test Mixture to compare tbe activity of various glass surfaces coated with ov-ioi. Surface types A > Untreated pyrex glass, B pyrex glass deactivated by thermal degradation of Ceurbowax 20M, C < SCOT column, prepared with Silanox 101, D pyrex glass column coated with a layer of barium carbonate and deactivated as in (B), and E - untreated fused silica. Components are identified in Table 2.7 with ac - 2-ethylhexanoic acid. (Reproduced with permission from ref. 152. Copyright Elsevier Scientific Publishing Co.)...
Whereas the components of (known) test mixtures can be attributed on the basis of APCI+/, spectra, it is quite doubtful that this is equally feasible for unknown (real-life) extracts. Data acquisition conditions of LC-APCI-MS need to be optimised for existing universal LC separation protocols. User-specific databases of reference spectra need to be generated, and knowledge about the fragmentation rules of APCI-MS needs to be developed for the identification of unknown additives in polymers. Method development requires validation by comparison with established analytical tools. Extension to a quantitative method appears feasible. Despite the current wide spread of LC-API-MS equipment, relatively few industrial users, such as ICI, Sumitomo, Ford, GE, Solvay and DSM, appear to be somehow committed to this technique for (routine) polymer/additive analysis. [Pg.519]

Retention time data by itself are never sufficient to identify mixture components unless it is known that the standards tested were the only possibilities. [Pg.535]

For the derivation of the PNEC several approaches have been proposed. Generally these can be categorised into three distinct assessments a conservative, a distributional, and a mixture toxicity approach. In conservative approaches, usually the most (realistic) sensitive endpoint such as LC50 or the known no observed effect concentration (NOEC) is taken and divided by an uncertainty factor (10-100). The selected uncertainty factor value depends on the type of endpoint and the number of available data, and is applied to account for laboratory to field extrapolations, species differences in sensitivities, and similar uncertainties. In distributional approaches, a series of, or all available, literature data are taken and a selected cut-off value is applied to the distribution of these data. The cut-off value may be, e.g., the concentration value that will protect 95% of the species (tested). In general, again an uncertainty factor (usually of 10) is then applied to take into account species differences. In the mixture toxicity approach, a similar mode of action is assumed for the assessment of the combined (additive) effect of the mixture. All relevant mixture components are scaled relative to the most potent one. This results in relative potencies for each component. The total effect of the mixture is then evaluated by... [Pg.942]

Reversed-phase liquid chromatography shape-recognition processes are distinctly limited to describe the enhanced separation of geometric isomers or structurally related compounds that result primarily from the differences between molecular shapes rather than from additional interactions within the stationary-phase and/or silica support. For example, residual silanol activity of the base silica on nonend-capped polymeric Cis phases was found to enhance the separation of the polar carotenoids lutein and zeaxanthin [29]. In contrast, the separations of both the nonpolar carotenoid probes (a- and P-carotene and lycopene) and the SRM 869 column test mixture on endcapped and nonendcapped polymeric Cig phases exhibited no appreciable difference in retention. The nonpolar probes are subject to shape-selective interactions with the alkyl component of the stationary-phase (irrespective of endcapping), whereas the polar carotenoids containing hydroxyl moieties are subject to an additional level of retentive interactions via H-bonding with the surface silanols. Therefore, a direct comparison between the retention behavior of nonpolar and polar carotenoid solutes of similar shape and size that vary by the addition of polar substituents (e.g., dl-trans P-carotene vs. dll-trans P-cryptoxanthin) may not always be appropriate in the context of shape selectivity. [Pg.244]

Mobile phases in chromatography and buffer systems in electrophoresis are examples of frequently used solvent mixtures. In a mixture of p components, only p— can be varied independently, which means that maximally p— mixture-related variables can be examined in the type of experimental designs typically used in robusmess testing. The value of the pth variable is determined by those of the other and used as adjusting component to complete the mixture. If one of the mixture components has an important effect on a response, then the composition of the whole mixture is important and should be strictly controlled. ... [Pg.190]

To determine the correction factors, an internal standard is generally added to each of the mixtures and the detector response measured relative to the internal standard. If the ratio of a monosaccharide to the internal standard decreases after hydrolysis of a test mixture of monosaccharides, decomposition has occurred and a recovery factor should be determined. The internal standard must either be resistant to decomposition during hydrolysis or should be added after hydrolysis it is usually better to add the internal standard after hydrolysis, to be on the safe side. The internal standard must not appear in the samples and must be resolved from other components in the sample, as with any internal standard. [Pg.254]

Anti-adhesive effect. Green and roasted coffee, used in a treatment mixture and as a pretreatment on beads, inhibited the Strep tococcus mutans sucrose-independent adsorption to saliva-coated hydroxyapatite beads. The inhibition of Salmonelb mutans adsorption indicated that coffee-active molecules may adsorb to a host surface, preventing the tooth receptor from interacting with any bacterial adhesions. Among the known tested coffee components, trigonelline and nicotinic and chlorogenic acids are very... [Pg.163]

In this study, a factorial experiment was set up to evaluate the effects of four variables at two levels on extraction efficiencies by using bonded-phase isolation techniques and a 27-component synthetic test mixture. The compounds studied and the respective mass ions used for quantitation are given in the box. The compounds in the mix vary greatly in water solubility and volatility and, in general, represent a wide class of organic compounds typical of those present in environmental samples. To maximize solute recoveries, the procedure was... [Pg.354]

Individual stock solutions of the test compounds were prepared in methanol at a concentration of 50 mg/mL. A standard test mixture was prepared by adding 100-/iL aliquots of each of the individual stock solutions to 500 mL of ultrapure water to give a concentration of 10 ppm per component. Samples requiring the addition of 500 ppm of methanol (conditioning solvent) were prepared by adding 6.3 /uL of methanol to 10-mL aliquots of the aqueous standard mix just prior to extraction. The pH of the samples was adjusted with either 6 M HC1 (for pH 2 samples) or 6 M NaOH (for pH 8 samples). To separate ionic strength effects from pH effects, the ionic strength of the samples was held constant. [Pg.357]

The separation of protein test mixtures on very short C 8 columns yielded surprising results (Fig. 18). The resolution obtained with a 6.3 x 4.6 mm column was about 2.25 or 2.22 times better than with a 45 x 4.6 mm column when the flow rate was low (0.25 or 0.5 ml/min, respectively) and the volumetric gradient rate large (16% B/ml). The gradient components were A water and B 2-propanol, both with 0.1% trifluoro-acetic acid (TFA)73). Even a column (better to say, a disk) 1.6 mm in length and 4.1 mm in diameter was effective in separating ribonuclease A, cytochrome C, and ovalbumin. Of course, the sample capacity of such a short column was very low 73). [Pg.189]

Purge line A with water and line B with MeOH. Dial-a-mix 70% MeOH and equilibrate the C18 column at l.OmL/min. When stable, inject 15pL of the seven-component test mixture and annotate the chromatogram s start. Run an isocratic chromatogram. [Pg.231]

Inject 15j L of the seven-component standards test mixture. Annotate and run an isocratic chromatogram. [Pg.231]

Put acetonitrile in the B reservoir. Purge the pump inlet line with acetonitrile. Dial-a-mix 60% acetonitrile/water. Reconnect the C18 column at O.lmL/min. Increase the flow to l.OmL/min and equilibrate the column. Inject 15 pL of the seven-component test mixture. Annotate and run the chromatogram. [Pg.232]

Testing the component and mixture melting points was done by the ASTM-D-127 method. Vaseline penetration testing was done by ASTM-D-937, and that of ozocerite, paraffin and the mixture by ASTM-D-1321 method. Calculations by Eq. (3.29) offered these values of regression coefficients ... [Pg.494]

It has been explained that when testing mixture diagrams, factor space is usually a regular simplex with q-vertices in a q-1 dimension space. In such a case, the task of mathematical theory of experiments consists of determining in the given simplex the minimum possible number of points where the design points will be done and based on which coefficients of the polynomial that adequately describes system behavior will be determined. This problem, for the case when there are no limitations on ratios of individual components, as presented in the previous chapter, was solved by Scheffe in 1958 [5], However, a researcher may in practice often be faced with multicomponent mixtures where definite limitations are imposed on ratios of individual components ... [Pg.506]

Multi-component hydrocarbon standards to provide accurate calibration of instruments (generally gas chromatographs) used to monitor the concentrations of a wide range of volatile organic hydrocarbon compounds (VOCs) in ambient air. These standards currently contain 30 different hydrocarbon species that are important to photochemical ozone formation, with concentrations ranging down to a few parts per billion by molar value. They are disseminated widely in the United Kingdom and the rest of Europe as calibration standards, and as test mixtures for assessment of the quality of international ambient hydrocarbon measurements (often under the auspices of the European Commission - EC). [Pg.215]


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