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Flames atomic spectroscopy

Burners Sources of heat for laboratory operations or for flame atomic spectroscopy. [Pg.1104]

C.M.P.V. Lopes, A.A. Almeida, J.L.M. Santos, J.L.F.C. Lima, Automated multi-commutated flow system for flame atomic spectroscopy determination of rubidium at high concentrations, At. Spectrosc. 27 (2006) 13. [Pg.291]

The most common approach taken in utilizing the hydrides for analysis is to permit the reaction to proceed for some time, holding the volatile species in a balloon attached to the system. When the reaction is complete, the hydride is analyzed by flame atomic spectroscopy. This general method has been used to determine parts-per-billion levels of arsenic and selenium in water 165-170) and to determine antimony, arsenic, and selenium using an automated system (777). Thompson and Thomerson (772) have used a sodium borohydride solution to convert various ionic forms of arsenic, bismuth, antimony, selenium, tin. [Pg.26]

The section on Spectroscopy has been retained but with some revisions and expansion. The section includes ultraviolet-visible spectroscopy, fluorescence, infrared and Raman spectroscopy, and X-ray spectrometry. Detection limits are listed for the elements when using flame emission, flame atomic absorption, electrothermal atomic absorption, argon induction coupled plasma, and flame atomic fluorescence. Nuclear magnetic resonance embraces tables for the nuclear properties of the elements, proton chemical shifts and coupling constants, and similar material for carbon-13, boron-11, nitrogen-15, fluorine-19, silicon-19, and phosphoms-31. [Pg.1284]

Absorbance profile for Ag and Cr in flame atomic absorption spectroscopy. [Pg.414]

Small concentrations of iron can also be deterrnined by flame atomic absorption and inductively coupled plasma emission spectroscopies (see... [Pg.444]

Chemical Analysis. The presence of siUcones in a sample can be ascertained quaUtatively by burning a small amount of the sample on the tip of a spatula. SiUcones bum with a characteristic sparkly flame and emit a white sooty smoke on combustion. A white ashen residue is often deposited as well. If this residue dissolves and becomes volatile when heated with hydrofluoric acid, it is most likely a siUceous residue (437). Quantitative measurement of total sihcon in a sample is often accompHshed indirectly, by converting the species to siUca or siUcate, followed by deterrnination of the heteropoly blue sihcomolybdate, which absorbs at 800 nm, using atomic spectroscopy or uv spectroscopy (438—443). Pyrolysis gc followed by mass spectroscopic detection of the pyrolysate is a particularly sensitive tool for identifying siUcones (442,443). This technique rehes on the pyrolytic conversion of siUcones to cycHcs, predominantly to [541-05-9] which is readily detected and quantified (eq. 37). [Pg.59]

Barium can also be deterruined by x-ray fluorescence (XRF) spectroscopy, atomic absorption spectroscopy, and flame emission spectroscopy. Prior separation is not necessary. XRF can be appHed directly to samples of ore or products to yield analysis for barium and contaminants. AH crystalline barium compounds can be analy2ed by x-ray diffraction. [Pg.484]

The capacity factors of SN-SiO, for metal ions were determined under a range of different conditions of pH, metal ions concentrations and time of interaction. Preconcentration of Cd ", Pb ", Zn " and CvS were used for their preliminary determination by flame atomic absorption spectroscopy. The optimum pH values for quantitative soi ption ai e 5.8, 6.2, 6.5, 7.0 for Pb, Cu, Cd and Zn, respectively. The sorption ability of SN-SiO, to metal ions decrease in line Pb>Cu> >Zn>Cd. The soi ption capacity of the sorbent is 2.7,7.19,11.12,28.49 mg-g Hor Cd, Zn, Pb, andCu, respectively. The sorbent distribution coefficient calculated from soi ption isotherms was 10 ml-g for studied cations. All these metal ions can be desorbed with 5 ml of O.lmole-k HCl (sorbent recovery average out 96-100%). [Pg.274]

The possibility of preconcentration of selenium (IV) by coprecipitation with iron (III) hydroxide and lanthanum (III) hydroxide with subsequent determination by flame atomic absorption spectroscopy has been investigated also. The effect of nature and concentration of collector and interfering ions on precision accuracy and reproducibility of analytical signal A has been studied. Application of FefOH) as copreconcentrant leads to small relative error (less than 5%). S, is 0.1-0.2 for 5-100 p.g Se in the sample. Concentration factor is 6. The effect of concentration of hydrochloric acid on precision and accuracy of AAS determination of Se has been studied. The best results were obtained with HCl (1 1). [Pg.293]

A schematic diagram showing the disposition of these essential components for the different techniques is given in Fig. 21.3. The components included within the frame drawn in broken lines represent the apparatus required for flame emission spectroscopy. For atomic absorption spectroscopy and for atomic fluorescence spectroscopy there is the additional requirement of a resonance line source, In atomic absorption spectroscopy this source is placed in line with the detector, but in atomic fluorescence spectroscopy it is placed in a position at right angles to the detector as shown in the diagram. The essential components of the apparatus required for flame spectrophotometric techniques will be considered in detail in the following sections. [Pg.783]

With flame emission spectroscopy, there is greater likelihood of spectral interferences when the line emission of the element to be determined and those due to interfering substances are of similar wavelength, than with atomic absorption spectroscopy. Obviously some of such interferences may be eliminated by improved resolution of the instrument, e.g. by use of a prism rather than a filter, but in certain cases it may be necessary to select other, non-interfering, lines for the determination. In some cases it may even be necessary to separate the element to be determined from interfering elements by a separation process such as ion exchange or solvent extraction (see Chapters 6, 7). [Pg.792]

CHAPTER 21 ATOMIC ABSORPTION AND FLAME EMISSION SPECTROSCOPY... [Pg.898]

Klrkbrlght, G. F. "The Application of Non-Flame Atom Cells In Atomic Absorption and Atomic Fluorescence Spectroscopy. [Pg.267]


See other pages where Flames atomic spectroscopy is mentioned: [Pg.399]    [Pg.405]    [Pg.399]    [Pg.405]    [Pg.176]    [Pg.226]    [Pg.435]    [Pg.524]    [Pg.177]    [Pg.232]    [Pg.773]    [Pg.779]    [Pg.779]    [Pg.780]    [Pg.781]    [Pg.782]    [Pg.783]    [Pg.783]    [Pg.784]    [Pg.786]    [Pg.788]    [Pg.793]    [Pg.794]    [Pg.796]    [Pg.798]    [Pg.799]    [Pg.800]    [Pg.802]    [Pg.804]    [Pg.806]    [Pg.808]    [Pg.810]    [Pg.814]    [Pg.857]   
See also in sourсe #XX -- [ Pg.405 ]




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Atomic absorption and flame emission spectroscopy

Atomic emission spectroscopy flame sources

Atomic spectroscopy

Flame atomic fluorescence spectroscopy

Flame atomization Flames

Flame atomizers

Flame temperatures, atomic spectroscopy

Flame-atomic absorption spectroscopy

Flames atomic emission spectroscopy

Flames atoms

Flames in atomic absorption spectroscopy

Hydride generation-flame atomic absorption spectroscopy

Interferences flame atomic absorption spectroscopy

Metals flame atomic absorption spectroscopy

Metals flame atomic emission spectroscopy

Nebulizers flame atomic absorption spectroscopy

Temperatures flame atomic absorption spectroscopy

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