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2021-02-02 17:45
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2021年2月2日发(作者:roxanne)


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


2

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