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Spectral identification

As outlined in Section 5.1.1.1, secondary ion emissions can be collected in the form of mass spectra. This is useful in cases where the optimal signals of interest are not known before analysis, and/or an understanding of all neighboring signals is needed. The former serves to aid in the collection of spatial or volumetric images or depth profiles, i.e. allows for the identification of the most effective signal/s to be followed, whereas the latter allows for the understanding of isobaric interferences that may be present. [Pg.249]

In the case of atomic and simple molecular ion emissions (unfragmented ions or those displaying minimal fragmentation), identification tends to be a relatively straightforward procedure of matching their masses. This is covered in Section 5.4.1.1. [Pg.249]


Chemical Gas Detection. Spectral identification of gases in industrial processing and atmospheric contamination is becoming an important tool for process control and monitoring of air quaUty. The present optical method uses the ftir (Fourier transform infrared) interference spectrometer having high resolution (<1 cm ) capabiUty and excellent sensitivity (few ppb) with the use of cooled MCT (mercury—cadmium—teUuride) (2) detectors. [Pg.295]

Monobasic acids are determined by gas chromatographic analysis of the free acids dibasic acids usually are derivatized by one of several methods prior to chromatographing (176,177). Methyl esters are prepared by treatment of the sample with BF.—methanol, H2SO4—methanol, or tetramethylammonium hydroxide. Gas chromatographic analysis of silylation products also has been used extensively. Liquid chromatographic analysis of free acids or of derivatives also has been used (178). More sophisticated hplc methods have been developed recentiy to meet the needs for trace analyses ia the environment, ia biological fluids, and other sources (179,180). Mass spectral identification of both dibasic and monobasic acids usually is done on gas chromatographicaHy resolved derivatives. [Pg.246]

Everett, T. S. Multinuclear NMR Spectral Identification of Organofiuor-ine Compounds unpublished data. [Pg.1080]

In an acetone extract from a neoprene/SBR hose compound, Lattimer et al. [92] distinguished dioctylph-thalate (m/z 390), di(r-octyl)diphenylamine (m/z 393), 1,3,5-tris(3,5-di-f-butyl-4-hydroxybenzyl)-isocyanurate m/z 783), hydrocarbon oil and a paraffin wax (numerous molecular ions in the m/z range of 200-500) by means of FD-MS. Since cross-linked rubbers are insoluble, more complex extraction procedures must be carried out (Chapter 2). The method of Dinsmore and Smith [257], or a modification thereof, is normally used. Mass spectrometry (and other analytical techniques) is then used to characterise the various rubber fractions. The mass-spectral identification of numerous antioxidants (hindered phenols and aromatic amines, e.g. phenyl-/ -naphthyl-amine, 6-dodecyl-2,2,4-trimethyl-l,2-dihydroquinoline, butylated bisphenol-A, HPPD, poly-TMDQ, di-(t-octyl)diphenylamine) in rubber extracts by means of direct probe EI-MS with programmed heating, has been reported [252]. The main problem reported consisted of the numerous ions arising from hydrocarbon oil in the recipe. In older work, mass spectrometry has been used to qualitatively identify volatile AOs in sheet samples of SBR and rubber-type vulcanisates after extraction of the polymer with acetone [51,246]. [Pg.411]

The success of spectral identification depends on the appropriate reference spectra for comparison. IR measurement of eluates that are at slightly subambient temperature is advantageous considering that the large databases of condensed-state spectra may be searched. Spectra measured by matrix-isolation GC-FTIR have characteristically narrow bandwidths compared with the spectra of samples in the condensed phase near ambient temperature or in the gas phase. In addition, the relative intensities of bands in the spectra of matrix-isolated samples often change compared with either gas- or condensed-phase spectra [195]. GC-FTIR spectra obtained by direct deposition match well with the corresponding reference spectra in standard phase... [Pg.457]

In spectral identification, the first step is a comparison of the observed losses with vibrational frequencies measured by IRS in the gas phase, to see if any correlations exist. When a molecule is attached to a surface it is fettered by forces due to the chemical bonds to the surface, and there will be stretching modes of vibration... [Pg.198]

The scope and mechanism of carboxylic acid homologation is examined here in relation to the structure of the carboxylic acid substrate, the concentrations and composition of the ruthenium catalyst precursor and iodide promoter, synthesis gas ratios, as well as 13C labelling studies and the spectral identification of ruthenium iodocarbonyl intermediates. [Pg.224]

In ultrapure polymer samples, all chains are terminated in the same way. The MALDI spectrum of an ultrapure polymer resembles a comb and the spacing between the comb s teeths equals the mass, Mrepeat, of the repeat unit. This quantity is often diagnostic and it suggests an almost trivial use of MALDI is the spectral identification of polymers. The reason is that, if one computes the M,.c x.at value for common polymers, most values are different, the number of superpositions being very low [4—6]. The Mrepeat value is not an integer, due to the fact that various isotopes are present. [Pg.301]

Studies involving mass spectral identifications were carried out using a VG 7035 coupled to a Dani gas chromatograph (VG Analytical, Manchester). Modifications were made to the analytical system as the high vacuum of the mass spectrometer was incompatible with the air vent system normally employed between the cold trap and the analytical column. Consequently, the flow of gas through the Tenax during thermal desorption was reduced... [Pg.314]

Not every PRM is suitable for constructing spectral identification libraries. These are usually compiled by using supervised modeling methods, and unknown samples are identified with those classes they resemble most. [Pg.468]

Chlorotrifluoromethyl aniline (no. 73.) was found in the sediment samples. This compound is used as a reactant with chloro-aniline (no. 72) in the preparation of 4,4 -dichloro-3-(trifluoromethyl)-carbanilide, a disinfectant. Two other related compounds also found in some of the sediments were chlorophenyl isocyanate (no. 74) and chloro(-trifluoromethyl)phenyl isocyanate (no. 75). This suggests that some of the 4,4 -dichloro-3-(trifluoromethyl)-carbanilide may, in fact, exist in the sediment extracts but is decomposed in the injection port of the gas chromatograph, since it is very doubtful that the easily hydrolyzable isocyanates exist as such in the sediments. To strengthen this hypothesis some 3,4,4 -trichlorocarbanilide [none of the 4,4 -dichloro-3-(trifluorome-thyl)-carbanilide was available] was analyzed by GCMS. The injection port temperature was 300°C. As expected, none of the parent compound eluted from the column. However, mass spectra were obtained for chlorophenyl isocyanate, dichlorophenyl isocyanate, chloroaniline, and dichloroaniline. The presence of the carbanilides themselves (no. 76, 77, 78) was confirmed with the help of HPLC and mass spectral identification. [Pg.72]

The NIOSH RTECS is the first non-spectroscopic CIS data base and has proven to be a very valuable addition to the CIS. Interest in the data base has been shown by many groups within EPA involved in the implementation of TSCA. For example, work is now underway to link spectral data with the NIOSH toxicity data so that as a result of a mass spectral identification, the EPA lab can quickly be informed if the chemical identified is toxic and hence requires immediate action. [Pg.267]

Biologically active isobutylamides have been isolated from plants of the Compositae and the Rutaceae. Some of the isohutyla-mides were found to have paralytic and toxic activities against insects, especially when applied topically to several species of Coleopterans and Dipterans.The present work describes the isolation, spectral identification, synthesis, and insect and snail bioassays of five isobutylamides from the Rutaceae plant, Fagara macrophylla. In addition, the synthesis and bioassay of four analogs of the isbbutylamide natural products are described. [Pg.163]

Day EA, Anderson DF. 1965. Gas chromatographic and mass spectral identification of natural components of the aroma fraction of blue cheese. J Agric Food Chem 13 2-4. [Pg.77]

Structure/property relationships Physical tests Spectral identification Stepwise polymerizations and 10 5... [Pg.689]

Kaye, W. (1 954) Near infrared spectroscopy I. Spectral identification and analytical applications. Spectrochimica Acta 6,... [Pg.213]

How can this enigma be answered Put away a sample of pure harmaline, with its spectral identification, onto the shelf for 50 or 100 years, and then re-analyze it Who knows, but what might be needed for this conversion is heat, or a bit of iron catalyst, or some unknown species of South American mold. Acid is certainly known to promote this oxidation. It would be very much worth while to answer this question because some, perhaps much, of the results of human pharmacological studies that involve harmaline as a metabolic poison, may be influenced by the independent action of harmine as a harmaline contaminant. [Pg.99]

For qualitative analysis, two detectors that can identify compounds are the mass spectrometer (Section 22-4) and the Fourier transform infrared spectrometer (Section 20-5). A peak can be identified by comparing its spectrum with a library of spectra recorded in a computer. For mass spectral identification, sometimes two prominent peaks are selected in the electron ionization spectrum. The quantitation ion is used for quantitative analysis. The confinnation ion is used for qualitative identification. For example, the confirmation ion might be expected to be 65% as abundant as the quantitation ion. If the observed abundance is not close to 65%, then we suspect that the compound is misidentified. [Pg.541]

Infrared spectral identification of adduct formation involving carbon dioxide and a transition metal complex has often been in error because of subsequent reactions of C02 with concomitant production of carbonato-, hydrogen-carbonato-, or carboxylato-metal complexes. Indeed Mason and Ibers (9) have suggested that the only acceptable structural characterization forjudging the authenticity of a class of transition metal-C02 complexes should be diffraction methods. X-ray structural studies have verified at least six C02 adducts which display all three types of bonding modes of... [Pg.131]


See other pages where Spectral identification is mentioned: [Pg.253]    [Pg.258]    [Pg.226]    [Pg.312]    [Pg.1010]    [Pg.1012]    [Pg.239]    [Pg.373]    [Pg.413]    [Pg.135]    [Pg.119]    [Pg.365]    [Pg.50]    [Pg.39]    [Pg.341]    [Pg.272]    [Pg.274]    [Pg.669]    [Pg.333]    [Pg.433]    [Pg.56]    [Pg.108]    [Pg.138]    [Pg.170]    [Pg.297]    [Pg.834]    [Pg.23]    [Pg.90]   
See also in sourсe #XX -- [ Pg.249 ]




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Automated Mass Spectral Deconvolution and Identification System

Automated Mass Spectral Deconvolution and Identification System, AMDI

Automated mass spectral deconvolution and identification

Identification by means of a spectral library

Identification spectral libraries

Identification with the Spectral Density Approach

Mass spectral fragmentation identification

Peak identification spectral properties

Spectral Identification of Short-Lived Molecules

Spectral Peak Identification

Spectral Properties and Structure Identification

Spectral analysis and identification

Spectral line identifications

Spectral scanning for source identification

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