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Polymers, trace analysis

Iron, thickness measurement, 150-152 trace analysis by x-ray emission spectrography, 163, 225-232 Iron-55, as x-ray source for sulfur determination, 130, 133-135 Iron oxides, analysis, 182, 184 Irradiance, definition, 6 Irradiation, equipment for, 177 of polymers, 177... [Pg.347]

Some typical applications in SFE of polymer/additive analysis are illustrated below. Hunt et al. [333] found that supercritical extraction of DIOP and Topanol CA from ground PVC increased with temperature up to 90 °C at 45 MPa, then levelled off, presumably as solubility became the limiting factor. The extraction of DOP and DBP plasticisers from PVC by scC02 at 52 MPa increased from 50 to 80 °C, when extraction was almost complete in 25 min [336]. At 70 °C the amount extracted increased from 79 to 95 % for pressures from 22 to 60 MPa. SFE has the potential to shorten extraction times for traces (<20ppm) of additives (DBP and DOP) in flexible PVC formulations with similar or even better extraction efficiencies compared with traditional LSE techniques [384]. Marin et al. [336] have used off-line SFE-GC to determine the detection limits for DBP and DOP in flexible PVC. The method developed was compared with Soxhlet liquid extraction. At such low additive concentrations a maximum efficiency in the extractive process and an adequate separative system are needed to avoid interferences with other components that are present at high concentrations in the PVC formulations, such as DINP. Results obtained... [Pg.96]

Extraction or dissolution almost invariably will cause low-MW material in a polymer to be present to some extent in the solution to be chromatographed. Solvent peaks interfere especially in trace analysis solvent impurities also may interfere. For identification or determination of residual solvents in polymers it is mandatory to use solventless methods of analysis so as not to confuse solvents in which the sample is dissolved for analysis with residual solvents in the sample. Gas chromatographic methods for the analysis of some low-boiling substances in the manufacture of polyester polymers have been reviewed [129]. The contents of residual solvents (CH2C12, CgHsCI) and monomers (bisphenol A, dichlorodiphenyl sulfone) in commercial polycarbonates and polysulfones were determined. Also residual monomers in PVAc latices were analysed by GC methods [130]. GC was also... [Pg.195]

Applications SFE-SFC solves problems in such diverse areas as polymers/monomers, oils/lubricants, foods, pharmaceuticals, natural products, specialty chemicals, coatings, surfactants and others. Off-line SFE-SFC survives alongside on-line determinations of additives, because of the need for representative sample sizes. Off-line SFE-SFC was used for extraction of AOs from PP [102]. In cases where the analyst wishes to perform further analysis on the extracted species, it is useful to be able to isolate the extract from the solvent. The ability to remove the solvent easily is particularly important when SFE is coupled on-line to chromatographic techniques, but is equally important for trace analysis when it is useful to concentrate... [Pg.441]

HPLC-QFAAS is also problematical. Most development of atomic plasma emission in HPLC detection has been with the ICP and to some extent the DCP, in contrast with the dominance of the microwave-induced plasmas as element-selective GC detectors. An integrated GC-MIP system has been introduced commercially. Significant polymer/additive analysis applications are not abundant for GC and SFC hyphenations. Wider adoption of plasma spectral chromatographic detection for trace analysis and elemental speciation will depend on the introduction of standardised commercial instrumentation to permit interlaboratory comparison of data and the development of standard methods of analysis which can be widely used. [Pg.456]

There is a need for increased chromatography-FTIR sensitivity to extend IR analysis to trace mixture components. GC-FTIR-MS was prospected as the method of choice for volatile complex mixture analysis [167]. HPLC-FT1R, SFC-FTIR and TLC-FTIR are not as sensitive as GC-FTIR, but are more appropriate for analyses involving nonvolatile mixture components. Although GC-FTIR is one of the most developed and practised techniques which combine chromatography (GC, SFC, HPLC, SEC, TLC) and FUR, it does not find wide use for polymer/additive analysis, in contrast to HPLC-FTIR. [Pg.458]

Trends in element analysis are multi-element (survey) analysis, lower concentration levels, micro/local element analysis and speciation (coupling with chromatography). An overview of the determination of elements in polymeric materials is available [7], Reviews on sample preparation for trace analysis are given in refs [8-10]. Quality assurance of analytical data in routine elemental analysis has been discussed [11], Organic analysis is obviously much more requested in relation to polymer/additive matrices than elemental analysis. [Pg.591]

Applications ICP-MS has become the technique of choice for the determination of elements in a wide range of liquid samples at concentrations in the ng L 1 to [igL-1 range. Typical applications of ICP-MS are multi-element analysis of liquids (even with high solid contents) element speciation by hyphenation to chromatographic techniques continuous on-line gas analysis multi-element trace analysis of polymers and trace analysis in high-purity materials. ICP-MS is routinely used for quality control purposes. [Pg.658]

Integration of sample preparation and chromatography by on-line coupling aims at reduction of analysis time. It is apparent from Section 7.1 that these hyphenated techniques are not yet contributing heavily to the overall efficiency of polymer/additive analysis in industry. On-line SFE-SFC requires considerable method development, and MAE-HPLC is off-line. Enhancement of sensitivity for trace analysis requires appropriate sample preparation and preconcentration schemes, as well as improved detection systems. [Pg.732]

For the analysis of organic additives in polymeric materials, in most cases, prior extraction will be necessary. Depending on the nature of the additive, many different approaches are employed. These include soxhlet extraction with organic solvent or aqueous media, total sample dissolution followed by selective precipitation of the polymer leaving the additive in solution, assisted extraction using pressurised systems, ultrasonic agitation and the use of supercritical fluids. In trace analysis, solid phase extraction (SPME) from solution or solvent partition may be required to increase the analyte concentration. [Pg.562]

For trace analysis in fluids, some Raman sensors (try to) make use of the SERS effect to increase their sensitivity. While the basic sensor layout for SERS sensors is similar to non-enhanced Raman sensors, somehow the metal particles have to be added. Other than in the laboratory, where the necessary metal particles can be added as colloidal solution to the sample, for sensor applications the particles must be suitably immobilised. In most cases, this is achieved by depositing the metal particles onto the surfaces of the excitation waveguide or the interface window and covering them with a suitable protection layer. The additional layer is required as otherwise washout effects or chemical reactions between e.g. sulphur-compounds and the particles reduce the enhancement effect. Alternatively, it is also possible to disperse the metal particles in the layer material before coating and apply them in one step with the coating. Suitable protection or matrix materials for SERS substrates could be e.g. sol-gel layers or polymer coatings. In either... [Pg.148]

J.M.P. Douse, Trace analysis of explosives at the low nanogram level in handswab extracts using columns of Amberlite XAD-7 porous polymer beads and sdica capillary column gas chromatography with thermal energy analysis and electron capture detection , J. Chromatogr., 328 (1985) 155-165. [Pg.243]

Attempts to optimize polymer-based electrodes for trace analysis have started very recently. Ceresa et al. have reported an ion-selective electrode optimized for the determination of Pb2+ in drinking water. The detection limit was 0.7 ppb (3 x 10 9M) which is somewhat poorer than the best LOD reported so far for Pb2+-selective electrodes [10] but the former was optimized for ruggedness and response time rather than LOD. Nevertheless, the obtained LOD was still adequate for the targeted application since it was about 20-fold lower than the 15 ppb action limit for Pb2+ in drinking water imposed by the USA EPA [79]. The authors used ICPMS as a reference method and obtained excellent correlation for samples of concentration 3nM. It was shown that the calibration procedure required ca. 10 min for stable readings in micromolar to nanomolar concentration levels. Moreover, the authors... [Pg.45]

Zhu, Q. Z., P. Degelmann, R. Niessner, and D. Knopp. 2002. Selective trace analysis of sulfonylurea herbicides in water and soil samples based on solid-phase extraction using a molecularly imprinted polymer. Environ. Sci. Technol. 36 5411-5420. [Pg.471]

Columns lengths of 10-25 m with a 0.32-mm ID and 10-/tm film thickness are available commercially. These phases are ideal for the separation of analytes in aqueous solutions or trace analysis of residual water, because the hydrophobic nature of the polymer allows water to be eluted as a sharp peak. The upper operational temperature of 250°C makes these phases a good choice for the separation of polar light hydrocarbons and alcohols. At subambient temperatures oxygenated gases such as CO and C02 are separated without tailing. [Pg.47]

J. M. F. Douse, Trace Analysis of Explosives in Handswab Extracts Using Amberlite XAD-7 Porous Polymer Beads, Silica Capillary Column Gas Chromatography with Electron Capture Detection and Thin Layer Chromatography, Journal of Chromatography 234 (1982) 415. [Pg.120]

The reaction products are separated and ignited the tritium content of the polymer, as determined by radiation trace analysis, is proportional to the number of metal—polymer bonds. A part of these bonds was generated by transfer to organometal (see Chap. 7, Sect. 5.1). The measurement is therefore repeated several times at various conversions. The number of active... [Pg.428]


See other pages where Polymers, trace analysis is mentioned: [Pg.671]    [Pg.400]    [Pg.94]    [Pg.242]    [Pg.306]    [Pg.313]    [Pg.508]    [Pg.513]    [Pg.548]    [Pg.651]    [Pg.669]    [Pg.732]    [Pg.735]    [Pg.223]    [Pg.93]    [Pg.408]    [Pg.343]    [Pg.73]    [Pg.165]    [Pg.198]    [Pg.179]    [Pg.31]    [Pg.115]   
See also in sourсe #XX -- [ Pg.274 ]

See also in sourсe #XX -- [ Pg.274 ]




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