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Real world samples

For new analytical techniques to prosper, they must have demonstrated applications to real-world samples, with outstanding figures of merit relative to competing approaches. Table 10.24 opposes the prospects of conventional separation procedures and advanced in situ analyses by the currently most qualifying techniques. Lab-on-a-chip (LOC) devices are unlikely to be robust enough to cope with the moderately complex (i.e. dirty ) matrices that are real-life samples. Industrial chemists need to avoid a lot of work for every analyte and every matrix. Obstacles to solid analysis are relatively poor sensitivities, narrow linear dynamic ranges and unavailability of solid standards. The trend... [Pg.730]

Remember that real-world samples are frequently very complex and will require you to separate and then identify or quantify ... [Pg.847]

Research in analytical chemistry is clearly an area where automation has a significant role to play. It is important that research data is fuUy validated and as accurate as possible. While it is not always possible to automate entire processes, the use of automated carousels to feed samples into a reaction system is an obvious area to improve the quality and rate of generation of data. It wiU also allow the researchers to quickly validate their proposed methodology on real-world samples and optimize the performance characteristics. This naturally requires a very close relationship between the researchers and the ultimate end-users of the analytical product. Given a good return for the investment, I am sure that the initial investment to automate the research activity will be justified and forthcoming. [Pg.235]

Real-world samples are usually characterized by a variety of chemical groups and, consequentially, by random peak distribution, therefore requiring a high separating power. A practical method for enhancing the peak capacity, as mentioned before, can be achieved by using multidimensional separations. In MD systems, the peak capacity is the sum of the peak capacities of the ID processes ... [Pg.104]

In the real world samples generally contain more than one constituent, and their spectra usually overlap. If we had a 2-component sample with individual and composite spectra like those in Figure 8, and if we wanted to determine the concentration of J, we would need to make measurements at two wavelengths, j and k. The tail (leading edge) of K overlaps the peak of J, giving rise to a composite absorbance (the solid line) which is higher than J s contribution. [Pg.99]

Several complexities must be addressed in order to fully understand the mode(s) of binding and the effects of the linker and dye on the stability of the duplex. The fact that the greatest stability was observed with an alkyl chain linker may be somewhat problematic in a dirty sample, as might be encountered in the analysis of crudely prepared real-world samples. In such cases, the alkyl chain could provide sites at which proteins and lipids might adsorb. Quantum yields are sufficient such that polyethylene glycol tethers could be used in real-world sensor configurations. [Pg.247]

Primary methods of measurement can, to some extent, be utilised for the preparation of synthetic RMs. In many situations these cannot be used in analytical chemistry as it is imperative that real world samples are used for standardisation purposes (Examples 3 and 4). [Pg.42]

NARL studies are designed to test the proficiency of laboratories by using test samples that resemble real world samples. Homogeneity of the test samples is established at a level that is sufficient for the purpose of the study taking into consideration the degree of interlaboratory variability appropriate for the particular analysis. [Pg.119]

Effective use of evaluation samples depends on matching the standards with the real-world samples, especially in terms of their matrix. Take the example of extraction of pesticides from fish liver. In a real sample, the pesticide is embedded in the liver cells (intracellular matter). If the calibration standards are made by spiking livers, it is possible that the pesticides will be absorbed on the outside of the cells (extracellular). The extraction of... [Pg.28]

Often, the matrix spike cannot be carried out at the same time as the analysis. The spiking is carried out separately on either the same matrix or on one that resembles the samples. In the example above, clean soil can be spiked with regular chlorophenol and then the recovery is measured. However, one should be careful in choosing the matrix to be spiked. For instance, it is easy to extract different analytes from sand, but not so if the analytes have been sitting in clay soil for many years. The organics in the soil may provide additional binding for the analytes. Consequently, a matrix spike may be extracted more easily than the analytes in real-world samples. The extraction spike may produce quantitative recovery, whereas the extraction efficiency for real samples may be significantly lower. This is especially true for matrix-sensitive techniques, such as supercritical extraction. [Pg.32]

Isolation of DNA from Small Real-World Samples for PCR... [Pg.294]

The literature reviewed shows that GC/TEA methods can be extremely sensitive and respond to a few picograms of common explosives. Fine et al. [14] using GC/TEA (capillary columns) found that the minimum detectable level at a signal-to-noise ratio of 3 1 is estimated to be 4 pg for TNT and RDX 5 pg for EGDN, NG and DNT and 25 pg for tetryl when they determined explosives in real world samples without previous clean-up. [Pg.12]

Interfacing the TEA to both a gas and a HPLC has been shown to be selective to nitro-based explosives (NG, PETN, EGDN, 2,4-DNT, TNT, RDX and HMX) determined in real world samples, such as pieces of explosives, post-blast debris, post-blast air samples, hand swabs and human blood, at picogram level sensitivity [14], The minimum detectable amount for most explosives reported was 4-5 pg injected into column. A pyrolyser temperature of 550°C for HPLC-TEA and 900°C for GC/TEA was selected. As the authors pointed out, GC uses differences in vapour pressure and solubility in the liquid phase of the column to separate compounds, whereas in HPLC polarity, physical size and shape characteristics determine the chromatographic selectivity. So, the authors reported that the use of parallel HPLC-TEA and GC-TEA techniques provides a novel self-confirmatory capability, and because of the selectivity of the technique, there was no need for sample clean-up before analysis. The detector proved to be linear over six orders of magnitude. In the determination of explosives dissolved in acetone and diluted in methanol to obtain a 10-ppm (weight/volume) solution, the authors reported that no extraneous peaks were observed even when the samples were not previously cleaned up. Neither were they observed in the analysis of post-blast debris. Controlled experiments with handswabs spiked with known amounts of explosives indicated a lower detection limit of about 10 pg injected into column. [Pg.24]

After sampling, storage, and sample preparation, species are to be identified and quantified. Direct speciation approaches can provide full information about the species in a sample without any additional (separation) method, and quantify the species directly. Such methods, for example, chemical sensors, biosensors, and nuclear magnetic resonance (NMR), however, have many limitations in sensitivity and/or selectivity when applied to real-world samples as human milk. [Pg.541]

Consistency with other observations on "real-world" samples ... [Pg.225]

In Table 1, the principle features of ICP-OES and ICP-MS techniques are presented. As can be observed, each technique presents specific capabilities and limitations, which determine their applications in the analysis of real-world samples. In the following sections, the basic principles of ICP-OES and ICP-MS are described with a special focus on the recent technological and methodological developments. An overview of their applications in inorganic and organometallic analysis is also presented. [Pg.6084]

Research on the pyrolysis of thermoset plastics is less common than thermoplastic pyrolysis research. Thermosets are most often used in composite materials which contain many different components, mainly fibre reinforcement, fillers and the thermoset or polymer, which is the matrix or continuous phase. There has been interest in the application of the technology of pyrolysis to recycle composite plastics [25, 26]. Product yields of gas, oil/wax and char are complicated and misleading because of the wide variety of formulations used in the production of the composite. For example, a high amount of filler and fibre reinforcement results in a high solid residue and inevitably a reduced gas and oiFwax yield. Similarly, in many cases, the polymeric resin is a mixture of different thermosets and thermoplastics and for real-world samples, the formulation is proprietary information. Table 11.4 shows the product yield for the pyrolysis of polyurethane, polyester, polyamide and polycarbonate in a fluidized-bed pyrolysis reactor [9]. [Pg.291]


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See also in sourсe #XX -- [ Pg.119 , Pg.157 , Pg.245 , Pg.305 , Pg.336 , Pg.425 , Pg.489 ]

See also in sourсe #XX -- [ Pg.119 , Pg.157 , Pg.245 , Pg.308 , Pg.340 , Pg.429 , Pg.493 ]




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