ATOMIC ABSORPTION SPECTROSCOPY (AAS)
ATOMIC ABSORPTION SPECTROSCOPY (AAS)
Atomic absorption spectroscopy (AAS) and atomic
emission spectroscopy (AES) is a spectroanalytical procedure for
the quantitative determination of chemical elements using the absorption of
optical radiation (light) by free atoms in the gaseous state. Atomic absorption
spectroscopy is based on absorption of light by free metallic ions.
In analytical chemistry the technique is used for
determining the concentration of a particular element (the analyte) in a sample
to be analyzed. AAS can be used to determine over 70 different elements in
solution, or directly in solid samples via electrothermal vaporization, and is used
in pharmacology, biophysics, archaeology and toxicology research.
Atomic emission spectroscopy was first used as an
analytical technique, and the underlying principles were established in the
second half of the 19th century by Robert Wilhelm
Bunsen and Gustav Robert Kirchhoff, both professors at
the University of Heidelberg, Germany.
The modern form of AAS was largely developed during
the 1950s by a team of Australian chemists. They were led by Sir Alan
Walsh at the Commonwealth Scientific and Industrial Research
Organisation (CSIRO), Division of Chemical Physics,
in Melbourne, Australia.
Atomic absorption spectrometry has many uses in
different areas of chemistry such as clinical analysis of metals in biological
fluids and tissues such as whole blood, plasma, urine, saliva, brain tissue,
liver, hair, muscle tissue, semen, in some pharmaceutical manufacturing
processes, minute quantities of a catalyst that remain in the final drug
product, and analyzing water for its metal content.
In order to analyze a sample for its atomic
constituents, it has to be atomized. The atomizers most commonly used nowadays
are flames and electrothermal (graphite tube) atomizers. The atoms should
then be irradiated by optical radiation, and the radiation source could be an
element-specific line radiation source or a continuum radiation source.
SCHEMATIC
FLOW OF AAS MEASUREMENT
The atomizers most commonly used
nowadays are (spectroscopic)
i.
Flames
ii. electrothermal
(graphite tube) atomizers. Other atomizers, such as glow-discharge atomization,
hydride atomization, or cold-vapor atomization might be used for special
purposes.
• Flame
atomizers
The oldest and most
commonly used atomizers in AAS are flames, principally the air-acetylene flame
with a temperature of about 2300 °C and the nitrous oxide system
(N2O)-acetylene flame with a temperature of about 2700 °C. The
latter flame, in addition, offers a more reducing environment, being ideally
suited for analytes with high affinity to oxygen.
• Electrothermal
atomizers/GFAA method development
Electrothermal
AAS (ET AAS) using graphite tube atomizers was pioneered by Boris V. L’vov
at the Saint Petersburg Polytechnical Institute, Russia, since the
late 1950s, and investigated in parallel by Hans Massmann at the Institute of
Spectrochemistry and Applied Spectroscopy (ISAS) in Dortmund, Germany
With this technique
liquid/dissolved, solid and gaseous samples may be analyzed directly. A
measured volume (typically 10–50 μL) or a weighed mass (typically around
1 mg) of a solid sample are introduced into the graphite tube and subject
to a temperature program. This typically consists of stages, such as
i. Drying – the solvent
is evaporated
ii. Pyrolysis –
the majority of the matrix constituents are removed;
iii. Atomization – the
analyte element is released to the gaseous phase; and
iv. Cleaning – eventual
residues in the graphite tube are removed at high temperature.
• The
graphite tubes are heated via their ohmic resistance using a low-voltage
high-current power supply;
iii. Cold-vapor
atomization
• The
cold-vapor technique is an atomization method limited to only the determination
of mercury, due to it being the only metallic element to have a large enough
vapor pressure at ambient temperature. Because of this, it has an
important use in determining organic mercury compounds in samples and their
distribution in the environment.
OTHER INSTRUMENTS MEASURE HEAVY
METALS.
Gas chromatography–mass
spectrometry (GC-MS) is
an analytical method that combines the features
of gas-chromatography and mass spectrometry to identify
different substances within a test sample. Applications of GC-MS
include drug detection, fire investigation, environmental
analysis, explosives investigation, and identification of unknown
samples, including that of material samples obtained from planet Mars during
probe missions as early as the 1970s.
GC-MS can also be used
in airport security to detect substances in luggage or on human beings.
Additionally, it can identify trace elements in materials that were
previously thought to have disintegrated beyond identification.
Like liquid chromatography–mass spectrometry, it allows analysis and
detection even of tiny amounts of a substance.
High-performance liquid
chromatography (HPLC) is an analytical technique to
separate, identify, and quantify components in a mixture. It is the single
biggest chromatography technique essential to most laboratories worldwide.
• How
Does HPLC Work?
In column
chromatography a solvent drips through a column filled with an adsorbent under
gravity. HPLC is a highly improved form of column chromatography. A pump forces
a solvent through a column under high pressures of up to 400 atmospheres. The
column packing material or adsorbent or stationary phase is typically a
granular material made of solid particles such as silica or polymers.
The pressure makes the
technique much faster compared to column chromatography. This allows using much
smaller particles for the column packing material. The smaller particles have a
much greater surface area for interactions between the stationary phase and the
molecules flowing past it. This results in a much better separation of the
components of the mixture.
Installation
requirements
The condition for
installation can be categorized into the following areas for laboratory
Environment.
i.
Suitability
ii.
Environmental conditions
iii.
Noise levels
iv.
Suitability
Equipment
class
An instrument is designed for indoor use only
and is classified suitable under Equipment Class category Example Agilent is I.
Installation
category
The installation
category implies the regulation for impulse withstand voltage. It is also
called the ‘Over voltage category’. ‘II’ applies to electrical equipment with a
nominal supply voltage up to 300 V. But in Tanzania normal voltage supply is
240V
Pollution
level
Pollution level
describes the degree to which a solid, liquid, or gas that deteriorates dielectric
strength is adhering. ‘2’ applies to a normal indoor atmosphere, where only
nonconductive pollution occurs.
Environmental
conditions
Operating your
instrument within the recommended cleanliness and temperature and humidity
ranges ensures optimum instrument performance and lifetime.
Cleanliness
The area selected for
operation of an AAS system must be free from drafts, corrosive atmospheres and
vibration. Sample preparation areas and materials storage facilities should be
located in a separate room. The area should have a dust-free, low-humidity
atmosphere. Air conditioning is strongly recommended for control of the
environment. The instrument should not be located near a window, door or any
other area where drafts may cause unstable thermal conditions.
Noise
levels
The sound pressure
level (SPL) of a flame AA in a ‘normal’ laboratory environment (≈60 dBA)
ambient noise measured at normal operator position is ≈65 dBA. At a distance of
1 meter from the instrument, the SPL is reduced to ≈62 dBA. The likely maximum
SPL at a customer location will be greatly influenced by the extraction system.
For laboratory
facilities
i.
Exhaust system
ii.
Electrical power supplies
iii.
Water cooling system
iv.
Waste fluids
v.
i. Exhaust system
vi.
Exhaust system Heat, vapors and fumes generated
by flame, furnace and vapor generation methods can be toxic or corrosive and
may be hazardous to personnel and must be extracted from the instrument by an
exhaust system.
vii.
ii. Electrical power supplies
viii.
The installation of electrical power supplies
must comply with the rules and/or regulations imposed by the local authorities
responsible for the use of electrical energy in the workplace. Many AASs are
supplied with a 2-meter (6 ft, 6 in) mains power cord terminated . All power
supplies should be: Single phase AC, 3-wire system (active, neutral and ground,
or two actives and ground) Terminated at an appropriate connection receptacle
that is within reach of the system power cable assembly. In areas where
208/220/240 volt supplies are not normally available in a single phase
configuration, supplies may be taken from two phases and ground of a three
phase system.
Other
power requirements
I.
A separate connection receptacle should
be provided for each unit in the system. Do not use double adapters or
extension cords. For Furnace instruments, a separate mains circuit individually
protected by fuses or circuit breakers must be used for the GTA accessory. It
is preferable for the GTA and the instrument to share the same phase.
II.
iii. Water cooling system
III.
The Graphite Tube Atomizer must have a
supply of cooling water to remove heat from the furnace workhead.
IV.
iv. Waste fluids
V.
The AA flame instrument atomizes only a
small percentage of the sample taken up. The excess liquids from the spray
chamber must be drained into a waste vessel. Suitable tubing is supplied with
the spectrometer for use with inorganic solvents. If you use organic solvents,
you will need different tubing, suitable for the solvent(s) of choice. The AA
instrument also needs a drain or a sump for disposal of waste liquid during
rinse cycles when flame or furnace autosamplers are used.
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