Expt 6 AAS Presentation

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    Experiment 6:

    Determination of TraceLevels of Copper inVegetable Samples Using

    the Atomic AbsorptionSpectrophotometerArgamino.Buenaseda.Gajigan

    Chem 127.1 Maam Cruz

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    INTRODUCTION

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    AAS

    one of the mostcommoninstrumental

    methods foranalyzing formetals and somemetalloids

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    PARTS

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    Hollow Cathode Lamp

    Provide the analytical light line for theelement of interest

    Provide a constant yet intense beam ofthat analytical line

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    Nebulizer

    Suck up liquid sample at a controlledrate

    Create a fine aerosol for introductioninto the flame

    Mix the aerosol and fuel and oxidant

    thoroughly for introduction into theflame

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    Flame

    Destroy any analyte ions and

    breakdown complexes Create atoms (the elemental form) of

    the element of interest

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    Monochromator Isolate analytical lines' photons passing

    through the flame

    Remove scattered light of otherwavelengths from the flame

    In doing this, only a narrow spectral line

    impinges on the PMT.

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    Photomultiplier Tube (PMT)

    As the detector, the PMT determinesthe intensity of photons of the analytical

    line exiting the monochromator.

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    KANGKONG

    Ipomoea aquatica

    A smooth, widely spreading vine,

    with the stems trailing on mud orfloating on water.

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    KAMOTE Ipomoea batatas

    A herbaceous vine with alternateheart-shaped or palmately lobedleaves and sympetalous flowers.

    The edible root is long and taperedwith a smooth skin of varying colorsfrom red, purple, brown and white.

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    Copper Content Standards

    Kangkong

    37.68 mg/kg (dry weight) (Wang, 2010)

    3.34-3.95 mg/100g (Umar, 2007) Kamote

    0 mg/100g (Antia, 2006)

    Root: 0.34 mg/100g (www.whfoods.org)

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    METHODOLOGY

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    Preparation of StockSolutions

    0.5 g of coppermetal weredissolved in 20 mL

    of 1:1 nitric acid diluted to mark in

    250-mL volumetricflasks

    5 mL aliquot wereobtained from theprepared solution

    diluted to a 100-mL

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    Preparation of Standard

    Five clean, 50-mLvolumetric flaskswere prepared and

    labeled withnumbers 1 to 5.

    0.50, 1.25, 2.50,5.00 mL of the

    stock solution wereplaced to flasks 1,2, 3, and 4respectively

    to re are 1.00,

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    Preparation of Sample

    The leaves fromthe vegetablesamples were

    rinsed and dried inthe oven

    The temperature ofthe oven was

    maintained at 100to 150C for 45minutes.

    Two (2) grams of

    the dried sample

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    Preparation of Sample

    The mixture wasboiled slowly atlow setting for 20

    minutes. 10 mL distilled

    water was addedto the cooled set-

    up.

    It was thenfiltered to a 50-

    mL volumetric

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    Analysis of theVegetable Sample

    The absorbanceof the standardsolutions and the

    sample weremeasured usingthe requiredinstrumental

    parameters (forCu) of the atomicabsorptionspectrophotomet

    er.

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    Standard AdditionMethod

    Five clean 50-mLvolumetric flaskswere prepared and

    labeled withnumbers 1 to 5.

    To each flask,10 mLof the digested

    sample were added.

    0.00, 0.50, 1.25,2.50, 5.00 mL of the

    stock copper

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    Standard AdditionMethod

    The absorbancesof the solutions

    were measuredusing the requiredinstrumentalparameters for

    Cu.

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    RESULTS

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    DIRECT CALIBRATION

    StandardConcentration

    (ppm)Absorbance

    CorrectedAbsorbance

    Blank 0.00 0.0123 0

    1 1.00 0.1937 0.1814

    2 2.50 0.3685 0.3562

    3 5.00 0.6789 0.6666

    4 10.00 1.1751 1.1628

    0 2 4 6 8 10 12

    0

    2

    4

    6

    8

    10

    12f(x) = 1.#NANxR = 1.#NAN

    Concentration (ppm)

    Corrected Absorbance

    Kangkong 0.036 = 0.1089

    [Cu] + 0.088

    [Cu] = -0.4775ppm

    Accounting for

    dilution:

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    STANDARD ADDITIONMETHOD

    Kangkong

    Set-upVolume ofStandard

    (mL)

    Absorbance

    Trial 1 Trial 1 Trial 3

    1 0.00 0.0119 0.0127 0.01332 0.50 0.1619 0.1632 0.16123 1.25 0.3350 0.3311 0.32824 2.50 0.6165 0.6147 0.61485 5.00 1.0855 1.0820 1.0820

    Set-up

    A/Ao

    (Vx+Vs/Cs)

    (A/Ao) (Vx +Vs/Cs)

    Trial 1 Trial 1 Trial 3 Trial 1 Trial 1 Trial 3

    1 0 0 0 0 0 0 02 14 13 12 0.105 1.4285 1.3493 1.27263 28 26 25 0.1125 3.1670 2.9330 2.77614 52 48 46 0.125 6.4758 6.0502 5.77825 91 85 81 0.15 13.683 12.780 12.203

    A/Ao= 0.1619/0.0119

    =14

    (Vx +Vs)/Cs=(10+0.50)/100= 0.105

    (A/Ao )(Vx+Vs)/Cs= 14 X 0.105= 1.4285

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    Kangkong

    0 2 4 6 8 10 12

    0

    2

    4

    6

    8

    10

    12f(x) = 1.#NANxR = 1.#NANf(x) = 1.#NANxR = 1.#NANf(x) = 1.#NANxR = 1.#NAN

    LinearRegressionfor

    LinearRegressionfor

    LinearRegressionfor

    Volume of Standard (mL)

    (A/Ao) (Vx +Vs/Cs)

    Cx = (1/m)Linear Equations:

    y = 2.7261x + 0.0018Cx=0.3668y = 2.5459x + 0.0019Cx=0.3928y = 2.4333x + 0.0021Cx=0.4110

    Average of Cx = 0.3902ppmAccounting for dilution:(0.3902mg/L)(50mL/10mL)

    (50mL)(1L/1000mL)/2g= 0.0488 mg/g

    STANDARD ADDITIONMETHOD

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    Kamote

    Set-upVolume ofSolution

    (mL)

    Absorbance

    Trial 1 Trial 1 Trial 3

    1 0.00 0.0272 0.0261 0.02762 0.50 0.1696 0.1679 0.17333 1.25 0.3308 0.3315 0.33174 2.50 0.6200 0.6191 0.62025 5.00 1.1073 1.1078 1.1088

    Set-up

    A/Ao(Vx

    +Vs/Cs)

    (A/Ao) (Vx +Vs/Cs)

    Trial 1 Trial 1 Trial 3 Trial 1 Trial 1 Trial 31 0 0 0 0 0 0 0

    2 6 6 60.105 0.6547 0.6755 0.6593

    3 12 13 120.113 1.3682 1.4289 1.3520

    4 23 24 22 0.125 2.8493 2.9650 2.8089

    A/Ao= 0.1696/ 0.027=6

    (Vx +Vs)/Cs= (10+0.50)/100= 0.105

    (A/Ao )(Vx +Vs)/

    = 6 X 0.105= 0.6547

    STANDARD ADDITIONMETHOD

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    Kamote

    0 2 4 6 8 10 12

    0

    2

    4

    6

    8

    10

    12f(x) = 1.#NANxR = 1.#NANf(x) = 1.#NANxR = 1.#NANf(x) = 1.#NANxR = 1.#NAN

    LinearRegressionfor

    LinearRegressionfor

    LinearRegressionfor

    Volume of Standard (Vs)

    (A/Ao) (Vx +Vs/Cs)

    Cx = (1/m)Linear Equations:

    y = 1.2152x + 0.0524Cx=0.8229y = 1.2673x + 0.0573Cx=0.7891y = 1.1979x + 0.0469Cx=0.8348

    Average of Cx = 0.8156 ppm

    Accounting for dilution:(0.8156mg/L)(50mL/10mL)(50mL)

    (1L/1000mL)/2g= 0.1019 mg/g

    STANDARD ADDITIONMETHOD

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    discussion

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    Atomic AbsorptionSpectrophotometry

    AAS Simple, low cost

    Application: effective determination of

    trace amounts of heavy metals inbiological samples

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    Atomic AbsorptionSpectrophotometry

    Cathodelamp

    made ofmetal underinvestigation

    emit the line

    spectrumcharacteristic of theparticularelement

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    Sample Preparation

    Air dried

    Advantage: ease of homogenization

    [Cu] reported per dry mass Rinsed

    remove surface contaminants

    Oven dried Further drying

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    Sample Preparation

    Solid samples should be brought intosolution

    acid attack

    alkali fusion and subsequent acid attack

    dissolution in solvent

    Acid attack important not to add components that

    interfere with the copper determination

    nitric acid causes no interference in the

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    Direct Calibration Method

    Plot the measured absorbanceagainst the concentration of thestandard solution (ppm)

    copper atoms in the flame

    follow the Beers Lambert Equation

    A = bc

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    Direct Calibration Method

    Blank determination exhibits little absorbance

    distilled water used as blank contains

    traces of copper ions

    Standard Solution

    copper metal

    high purity: minimize chemicalinterference effects due to chemicalimpurities present in some inorganic

    salts available in the laboratory

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    Standard Addition Method

    Absorbance of several solutionscontaining a constant volume ofdigested kangkong and kamote

    sample and varying volume ofstandard copper solution wasmeasure

    Derivation:

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    Standard Addition Method

    Standard Addition

    accounts for the matrix effects

    used when sample matrix affects theresponse of the analyte.

    usually necessary for complicatedsamples such as leaves

    some components in the leaves canaffect the response of the copper

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    Interference

    Spectral Interference

    presence of very few atoms

    Interference from flame emissions whichcan be reduced by modulating lamp

    Interference from molecular speciesabsorbing lamp photons that occurs at

    shorter wavelengths which can beremoved by using a deuterium lampwhich has a broader band light source.

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    InterferenceChemical Interference Solution

    Matrix effect standard addition method

    Poor nebulization because ofhigh viscosity

    Use hotter flames

    Poor volatility Use hotter flames

    Formation of metal oxides andhydroxides

    Using fuel rich flame

    Ionization of analyte atoms Add an ion that has a lowerionization potential

    Light scattering by particles inthe flame

    Background correction ORSelecting the optimum temperaturewhere the background signal andanalyte can be effectivelyseparated ORUsing broad band light source (i.e.

    deuterium)

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    Interference

    Other methods in overcoming someinterference

    using higher temperature flame such as

    nitrous oxide which sufficiently causecomplete dissociation of some refractorycompounds

    extracting the analyte element extracting the interferent

    use of releasing agents that will

    combine with the interferents.

    I t f i C

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    Interference in Cudetermination

    High Zn/Cu ratio which lowers theobserve absorption.

    Some papers suggest the use of nitrous

    oxide can lessen the interference.

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    Possible Sources of Errors

    Low concentration of standardssolutions

    solns deteriorate due to the absorption

    of the analyte in the walls of thecontainer

    Oxide coating of the metal standard

    (Cu metal) was not properly removed Differences in the amount of sample

    and standard that reach the flame

    because of the differences in the

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    CONCLUSION

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    CONCLUSION

    Trace amounts of severalnutritionally important elements invegetable samples could be

    successfully determined throughAtomic AbsorptionSpectrophotometry.

    The analyte concentration wasdetermined from the absorption ofits solution using the Beer-Lambert

    equation.

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    CONCLUSION

    In the experiment, two methods wereused to determine the copperconcentration in leaf samples: direct

    calibration method and the standardaddition method.

    In direct calibration method, the

    equation y = 0.1089x + 0.088 wasobtained as standard curve. Thecalculated concentrations of Copperwere -0.0112 mg/g and 4.76E-3 mg/g for