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Analytical limits

ICP is used to analyze samples of water and waste water, and also solid samples after suitable maceration processes. The detection limits and [Pg.114]

It is clear that the detection limits lie in the same range as for flame A AS. The advantages over flame A AS lie in the possibility of determining [Pg.114]


The formation of hydrogen is accompanied with VFAs or solvent production during an anaerobic digestion process. Therefore, the distribution of VFA concentrations and their finctions is a usefiil indicator for monitoring hydrogen production. Fig. 3 shows the variations in alcohol and VFAs. Most of the VFAs were analyzed as acetate and butyrate, and most of the alcohols were analyzed as ethanol. The propionate concentration was below the analytical limit. It indicates that the anaerobic pathway in the reactor is not propionic-type fermentation but but5nrate-type fermentation. Clostridium butyricum is considered to be the dominant... [Pg.151]

An attempt to estimate human daily impact of N nitroso compounds is shown in Table I. The apparent intake from food of preformed nitrosamines is comparatively low, at least in these surveys of a Western diet in England (3). The Intake directly to the respiratory tract from smoking could be somewhat larger. However, if the blood levels reported are confirmed as correct, then inputs of up to 700 meg per day of at least N nitrosodimethylamine (NDMA) may be calculated, based on pharmacokinetic considerations of data obtained in animals and extrapolated to man. It should be emphasized that no information is available at present on nitrosamide intake or in vivo formation, largely because of analytical limitations. [Pg.196]

No specific information was found on the releases of diisopropyl methylphosphonate to soil. However, diisopropyl methylphosphonate has been detected in soils at the RMA (Williams et al. 1989). Concentrations of diisopropyl methylphosphonate in live surface soil samples at the RMA ranged from <0.05 to 0.24 mg/kg (Williams et al. 1989). Concentrations of diisopropyl methylphosphonate in surface soil samples measured during the Remedial Investigation/Feasibility Study (RI/FS) at RMA ranged from less than the analytical limit of 0.114 mg/kg to 11 mg/kg (Ebasco Services 1991). The most recent sampling conducted in 1995 indicated the concentrations of diisopropyl methylphosphonate in the onpost surface soil samples were less than the analytical reporting limit of 0.342 mg/kg (D.P. Associates 1995). [Pg.121]

Table 7.5. Analytical limits within the signal and sample domain the most meaningful of which are emphasized... [Pg.227]

Sample Matrix Sample Preparation Analytical Limit (% Recovery) Reference... [Pg.92]

Oxford Instruments, 2006. INCAEnergy EDS X-ray Microanalysis System. Oxford Instruments Analytical Limited, Oxfordshire,... [Pg.214]

The Process. Toxicologists have least to offer here. In fact, only their intellectual analysis and review of the literature should be required to asses the manufacturing process and any residues of its chemicals and so to set analytical limits on purity and residues in the final preparation. [Pg.435]

Compound Water Sludge3 Analytical limit of detection (hg g1 sample)... [Pg.518]

Archean and Himalayan (Tertiary). The coherence of these samples suggests that Mo isotope fractionation during igneous processing is small compared to current analytical limits (Siebert et al. 2003). [Pg.439]

The synthetic pigment CuPc was obtained by serendipity in 1927 but not identified as such by the authors probably due to analytical limitations and/or because attention was focused on other compounds (de Diesbach von der Weid, 1927). Upon reaction of o-C6H4Br2 with cuprous cyanide and C5H5N a blue insoluble compound was obtained, which undoubtedly was CuPc. Basically there are two commercially important processes to produce CuPc. One is based on phthaloni-trile and the other one uses phthalic anhydride. The phthalonitrile process often yields a product with fewer impurities and using metallic copper gives CuPc by cyclotetramerization. [Pg.95]

Figure 17. Representation of the analytical limits to be kept for defect-free REM-or Ca-treated steel. The shaded areas (deep shade only for calcium) are considered safe by the Kawasaki team. Figure 17. Representation of the analytical limits to be kept for defect-free REM-or Ca-treated steel. The shaded areas (deep shade only for calcium) are considered safe by the Kawasaki team.
Figure 8.5 Schematic of intelligent gravimetric analyzer (Hiden Analytical Limited, England). Figure 8.5 Schematic of intelligent gravimetric analyzer (Hiden Analytical Limited, England).
The main analytical limitations of DC polarography and the methods of overcoming them are as follows ... [Pg.125]

Note Some original target compounds (see Table I) are not included because of inconsistent or incomplete data. a All rejections indicated by greater than (>) were obtained by using the analytical limit of rejection in eq 1. Actual rejection may approach 1002. — means cannot be determined from available data neg means negative value. [Pg.439]

In old contaminated soil sites, CPs are less accessible to biodegradation than CPs in more recently contaminated sites (Salkinoja-Salonen et al., 1989) inaccessibility correlates with unavailability of CPs to extraction by nonpolar solvents (diethyl ether, hexane). Remediation studies with artificially contaminated soil are likely to give lower residual CP concentrations than obtained in actual remediation. Decreased CP concentrations due to analytical limitations should not be interpreted as biodegradation. [Pg.264]

While catalytic HDM results in a desirable, nearly metal-free product, the catalyst in the reactor is laden with metal sulfide deposits that eventually result in deactivation. Loss of catalyst activity is attributed to both the physical obstruction of the catalyst pellets pores by deposits and to the chemical contamination of the active catalytic sites by deposits. The radial metal deposit distribution in catalyst pellets is easily observed and understood in terms of the classic theory of diffusion and reaction in porous media. Application of the theory for the design and development of HDM and HDS catalysts has proved useful. Novel concepts and approaches to upgrading metal-laden heavy residua will require more information. However, detailed examination of the chemical and physical structure of the metal deposits is not possible because of current analytical limitations for microscopically complex and heterogeneous materials. Similarly, experimental methods that reveal the complexities of the fine structure of porous materials and theoretical methods to describe them are not yet... [Pg.250]

Variation in sample height on a non contact optical unit can be a major analytical limitation. There are at least three American and three European near-infrared moisture monitoring systems which use water absorption at 1940 nm with one or more reference wavelengths. These are designed to be mounted above a conveyor belt with clearance between the optical window and the sample surface. Since water is a strong absorber the coefficients used in the analytical expression are small and the uncertainty associated by multiplying the sampling noise may be acceptable. For analytes where absorbance differences are less, the precision may not be sufficient. [Pg.277]

Under experimental conditions of 50 °C and pH 1.5, 5, 7, 9, or 11, no hydrolytic loss of PFOS was observed in a 49-day study [42]. Based on mean values and precision measures, the half-life of PFOS was estimated as > 41 years at 25 °C. However, it is important to note that this estimate was influenced by the analytical limit of quantitation and that no loss of PFOS was detected in the study. Likewise, under experimental conditions of 50 °C and pH 1.5, 5, 7, 9, or 11, the hydrolytic loss of PFOA was observed for 109 days. Results showed that the degradation rate of PFOA was not dependent upon pH levels. The hydrolytic rate constant for PFOA at 50 °C was determined to be 8.1E-5/d, and the minimum calculated half-life was estimated as 92 years [43]. [Pg.404]

In ideal situations in which erosion rate is well constrained, cosmogenic-nuclide paleoaltimetry currently will be exact to no more than 200 m at best, given current uncertainty in scaling functions and long-term atmospheric conditions, analytical limitations, as well as... [Pg.275]

Macadamia nuts, guava, refined sugar, and molasses are the only raw agricultural commodities treated with atrazine that are consumed as foods. There are no known residue concentrations of atrazine or its chloro-metabolites above their analytical limits of detection (LODs) in any of these four foods. In evaluating Equation (31.2), the residue concentration in each of these four foods is assumed to be equally likely to be any value between zero and its LOD (i.e., uniformly distributed between zero and the LOD). [Pg.485]

The sensitivity and detection limits of an analytical technique are determined by the SNR of the measurement, an important metric for assessing both the instrumental performance and analytic limits of the spectral measurement. Following typical analytical practices, 3 and 10 times the noise have been suggested as limits of detection and of quantification for IR spectroscopy, respectively. The performance of interferometers in the continuous-scan mode, which is simpler compared with that of the step-scan mode, has been analyzed well. The SNR of a spectrum measured using a Michelson interferometer is given by12... [Pg.7]


See other pages where Analytical limits is mentioned: [Pg.709]    [Pg.117]    [Pg.891]    [Pg.220]    [Pg.559]    [Pg.730]    [Pg.89]    [Pg.1283]    [Pg.238]    [Pg.291]    [Pg.109]    [Pg.235]    [Pg.25]    [Pg.196]    [Pg.175]    [Pg.272]    [Pg.358]    [Pg.183]    [Pg.1283]    [Pg.851]    [Pg.134]    [Pg.172]    [Pg.440]    [Pg.456]    [Pg.472]    [Pg.303]    [Pg.231]   


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