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While arc/spark emission techniques enjoyed widespread popularity for the determinationof metals, flame emission spectrometry, also known as flame photometry,was used extensively for determination of the alkalis and other easily excitedelements. A Swedishagronomist named Lundegårdh is credited with beginningthe modern era of
flame photometry in the late 1920’s. His apparatus for
elemental analyses of plants, shown in Figure 1-4,used pneumatic nebulizationand a premixed airacetylene flame and is remarkably
similar to equipment used today.While the atomic spectra emitted from flames had the advantage of being simpler than those emitted from arcs
and sparks, the main limitation of the technique was that the flames were not hot enough to cause emission for many elements. Despite
that limitation, several successful commercial instruments
were based on the technique, many of which are still in use today. The
most widespread use of the technique is in clinical labs for determining sodium and potassium levels in blood and other biological materials.In the 1960’s and 1970’s both flame and arc/spark optical emission spectrometry declined in popularity. Many of the analyses that had been performed using optical emission were increasingly performed using atomic absorption spectrophotometry (AAS). While advances in flame emission spectrometry allowed the determination
of about half of the elements in the periodic table, the technique could no longer
compete well with AAS. Since absorption of light by ground state atoms was used as the mode of detection, the need for very high temperatures to populate excited states of atoms was no longer a limitation. The instabilities and spectral interferences
which plagued arc/spark emission techniques were also greatly reduced by atomic absorption techniques.Spray chamber, nebulizer and burner
such as those used by Lundegårdh for flame emissionspectrography. (Used with permission from the
Division of Analytical Chemistry of the American
Chemical Society.)
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At the time of its greatest popularity, flame atomic absorption was used primarily in
the analysis of solutions for trace metals. For solid samples, the technique requires
that samples be dissolved. With the exception of a few well-documented interferences,
samples and standards need not be made very similar. Flame atomic
absorption offers the analyst high precision (0.2 to 0.5% RSD) determinations and
moderate detection limits. Electrothermal atomization (graphite furnace) atomic
absorption spectrometry, on the other hand, offers high sensitivity and low detection
limits. Graphite furnace AAS (GFAAS) does provide poorer precision and a higher
level of matrix interferences than are experienced with the flame-based technique.
However, advances such as the use of stabilized temperature platform furnace
(STPF) technology and Zeeman background correction have reduced or eliminated
most of the interferences previously associated with GFAAS.
Both the flame and graphite furnace AAS techniques are used widely today and
both provide excellent means of trace elemental analysis. Most atomic absorption
instruments are limited, however, in that they typically measure only one element
at a time. The instrumental setup or operating conditions may require changing
hollow cathode lamps or using different furnace parameters for each element to be
determined. Because of the different operating conditions and furnace parameters
required for each element, conventional atomic absorption techniques do not lend
themselves readily to multi-element simultaneous analysis.
Also, despite advances in nonlinear calibration, the need for sample dilution is
greater than for present-day OES techniques, due to the limited working (calibration)
range for the AAS techniques. Consequently, devices for automatic sample dilution
when a sample concentration exceeds the calibration range are available. For those
samples that require element preconcentration for lower detection limits, flow-injection
techniques coupled with cold vapor mercury or hydride generation equipment
and GFAAS can not only provide significant improvements in detection limits, over
100 times better as compared to conventional hydride generation AA, but also may
reduce potential interferences by the complete removal of matrix components.
Stanley Greenfield of Birmingham, England is credited with the first published report
(1964) on the use of an atmospheric pressure inductively coupled plasma (ICP) for
elemental analysis via optical emission spectrometry (OES) [1]. The conclusions
from this landmark paper summarize what Greenfield identified as the advantages
of plasma emission sources over flames, ac sparks and dc arcs:
The plasma source has a high degree of stability, has the ability to
overcome depressive interference effects caused by formation of
stable compounds, is capable of exciting several elements that are
not excited in orthodox chemical flames, and gives increased sensitivity
of detection [over flame photometry].
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The plasma source is far simpler to operate than the conventional
arc and spark methods, especially in solution and liquid analysis,
and gives the high degree of stability associated with the a.c. spark
combined with the sensitivity of the d.c. arc. Particular advantages
of the high-frequency plasma torch are the lack of electrodes, which
gives freedom from contamination, and the extremely low background
produced.
As with most new techniques, the original optical emission results using ICP sources
were not spectacular. The technique was better than flame atomic absorption for
only a few of the most refractory elements. Along with Greenfield, Velmer Fassel
and his colleagues at Iowa State University are generally credited with the early
refinements in the ICP that made it practical for analysis of nebulized solutions by
OES. The technique continued to be refined as sources of noise were tracked down
and eliminated, and gas flows, torch designs and plasma settings were optimized.
By 1973, the low detection limits, freedom from interferences and long linear working
ranges obtained with the ICP proved that it was clearly an emission source superior
to those used previously in analytical optical emission spectrometry. Since that time,
an ever-increasing number of academic, governmental and industrial researchers
have joined in the development of the ICP.
It has been mentioned that an affiliated technique to atomic spectroscopy for
elemental analysis is ICP-MS. Though ICP-MS is not the subject of this handbook
on the concepts, instrumentation and techniques in optical emission spectrometry,
ICP-MS has become an important tool for the analyst since its commercial introduction
in 1983. ICP-MS was pioneered by just a few prominent laboratories: Iowa State
University, Ames, Iowa; Sciex, a manufacturer’s laboratory in Toronto, Canada; and
several facilities in the U.K. including the University of Surrey, the British Geological
Survey and a U.K. manufacturer. The technique features high sensitivity and
excellent detection limits, equal to or better than GFAAS for most elements. The
mass spectra are considerably simpler than the atomic emission spectra from the
ICP but the mass spectra are complicated by mass interferences from molecular
ions originating in the ICP. However, ICP-MS allows for the routine use of isotopic
ratio and isotopic dilution measurements to assist in the solution of analytical
problems. Furthermore, qualitative analysis can be rapidly performed by ICP-MS
techniques.