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Lab 1
Determination of heavy
metals in soil by
atomic absorption spectrometry(AAS)
Name: XuFei
Group: The 3rd group
Date:
Sep.
20
th
2012
Part 1
The
introduction
1.1The purposes
(1)Learn how to operate the atomic
absorption spectrometry;
(2)Learn how
to do the pretreatment of soil samples;
(3)Get familiar with the application of
atomic absorption spectrometry.
1.2The
principles
Atomic Absorption
Spectrometry (AAS) is a technique for measuring
quantities
of
chemical
elements
present
in
environmental
samples
by
measuring
the
absorbed
radiation
by
the
chemical
element
of
interest.
This
is
done
by
reading
the
spectra
produced
when
the
sample
is
excited
by
radiation.
The
atoms
absorb
ultraviolet
or
visible light and make transitions to
higher energy levels .
Atomic
absorption
methods
measure
the
amount
of
energy
in
the
form
of
photons
of light that are absorbed by the sample. A
detector measures the wavelengths
of
light
transmitted
by
the
sample,
and
compares
them
to
the
wavelengths
which
originally passed through the sample. A
signal processor then integrates the changes
in wavelength absorbed, which appear in
the readout as peaks of energy absorption at
discrete wavelengths. The energy
required for an electron to leave an atom is known
as
ionization
energy
and
is
specific
to
each
chemical
element.
When
an
electron
moves
from
one
energy
level
to
another
within
the
atom,
a
photon
is
emitted
with
energy E. Atoms of an
element emit a characteristic spectral line. Every
atom has its
own distinct pattern of
wavelengths at which it will absorb energy, due to
the unique
configuration of electrons
in its outer shell. This enables the qualitative
analysis of a
sample.
The concentration is
calculated based on the
Beer-Lambert law.
Absorbance
is
directly proportional to the
concentration of the analyte absorbed for the
existing set
of
conditions.
The
concentration
is
usually
determined
from
a
calibration
curve,
obtained
using
standards
of
known
concentration.
Calibration
Curve
Method:
Prepare
standard
solutions
of
at
least
three
different
concentrations,
measure
the
absorbance
of
these
standard
solutions,
and
prepare
a
calibration
curve
from
the
values
obtained.
Then
measure
the
absorbance
of
the
test
solution
adjusted
in
concentration to a measurable range,
and determine the concentration of the element
from the calibration curve.
1
Lab 1
Part 2
The materials and apparatus
Atomic absorption spectrometry; Cu
hollow cathode lamp; AC voltage stabilizer;
oil-free gas compressor; acetylene
cylinder; oscillator; sample boat; Erlenmeyer
flask
with stopper (100 ml); beaker;
graduate cylinder; pipette.
Part 3
The procedure
3.1 operating procedure for
AAS
(1) inspect major
components to ensure operating normal.
(2) Install required hollow cathode
lamp. Sele
ct “T” before
turning to the power and
hollow cathode lamp. Then select
appropriate la mp current and preheat for 30min.
(3) Make sure electrical meter to point
to zero and then turn on high-voltage power.
(4) Select appropriate slit width.
(5) Rotate monochromator and select
required wavelength. If the power meter is too
high or low, adjust negative high
voltage until the meter reads full scale.
(6) Adjust light point and wavelength
so that the meter represents the maximum value.
(7) Turn on air compressor and
acetylene gas and ignite flame. Adjust the flame
appropriately and preheat the burner.
(8) Inject distilled water into the
flame and continue to preheat the burner. Inject
distilled water into the flame after
each sample.
(9) Select “E”, inject
blank solution into the flame and
adjust
the meter to zero.
(10) Optimize analysis conditions and
measure standard solution and samples.
(11) After completion of measurement,
turn off acetylene gas valve and then air
compressor, cut off gas supply a moment
later.
(12) Select
“T”
before turning o
ff high voltage power,
decrease lamp current and then
turn off
the lamp. At the same time, all buttons should be
on original positions.
(13) Check the
equipment before leaving the laboratory.
3.2 Determination of soil samples
(1) Preparation of extracting solution
(0.05 mol/l EDTA solution)
18.6 g of
EDTA is dissolved with water in a beaker (500 ml).
The PH is adjusted
to
7.0
using
dilute
ammonia.
The
mixture
is
transferred
into
a
volumetric
flask
(1000ml), dilute to
the mark and mixed well.
(2) Treatment
of soil samples
2.50
g
of
air-dried
soil
(60-
100
mesh)
is
put
into
an
Erlenmeyer
flask
with
stopper (100 ml). 12.5 ml of EDTA
solution is added. The mixture is shaken for 1h
and then filtered. The filtrate is
preserved for analysis.
(3) Preparation
of Cu standard stock solution
0.10 g of
Cu is dissolved in 15 ml of (1:1) nitric acid
solution. The mixture is
transferred
into a volumetric flask (1000 ml) and diluted to
the mark with re-distilled
water. The
concentration of the stock standard solution is
100g/ml. (The concentration
should be
calculated according to the mass of Cu).The
working Cu standard solution
(10?
g/ml) is obtained by
diluting 10 ml of Cu standard stock solution to
100 ml with
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