Formal Report Experiment 8

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    QUANTITATIVE DETERMINATION OFDISSOLVED OXYGEN CONTENT BY WINKLERREDOX TITRATION

    W. YBAÑEZNATIONAL INSTITUTE OF MOLECULAR BIOLOGY AND BIOTECHNOLOGY, COLLEGE OF SCIENCE

    UNIVERSITY OF THE PHILIPPINES, DILIMAN, QUEZON CITY 1101, PHILIPPINES

    DATE SUBMITTED: 23 FEBRUARY 2016

    DATE PERFORMED: 18 FEBRUARY 2016

    ABSTRACT

    INTRODUCTION

    The dissolved oxygen (DO) content in

    water is an important index in the

    consideration of water suitability.

    Sufficient concentration of DO is critical

    for the survival of most aquatic life, aswell as in waste water treatment. It is a

    key parameter for characterizing natural

    and wastewaters and for assessing the

    state of the environment in general.[1] 

    The Winkler method is a premier and

    classical method for the determination of

    DO content in water sample. A sample of

    water is collected in such a way that itsexposure to the atmosphere is minimized.

    This is because exposure might alter the

    level of dissolve O2. To fix the DO content

    of the water sample, it is treated with a

    solution of MnSO4, and then added with

    and then with a solution of NaOH and KI

    (hereafter referred to as alkaline iodide

    azide).[2] 

    The basis of this method is thequantitative oxidation of Mn2+ to Mn3+ by

    dissolved O2 in the water sample. Then,

    the trivalent Mn oxidizes I- to I2 in a

    subsequent redox reaction; the amount of

    I2 generated is determined by the titration

    with a standard S2O32- solution. The

    endpoint is determined by the color

    change brought by the formation of a

    starch-triiodide complex.[3] 

    The objectives of the experiment was to

    perform the water sampling and

    pretreatment techniques accurately, to

    calculate the DO content of the water

    sample, and to discuss the chemistry

     behind the Winkler method for dissolved

    oxygen determination.[4]

    METHODOLOGY

    Firstly, the solutions prepared for the

    experiment were 25.0mL of 4.0M MnSO4,

    25.0mL of alkaline iodide azide, 250.0mL

    of 0.125M stock Na2S2O3, 50.0mL 0.5M

    H2SO4, and freshly prepared starch

    solution. Then, 250.0mL of 0.0125M

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    standard Na2S2O3 solution was prepared

    from the stock Na2S2O3solution.

    For the standardization of the

    Na2S2O3solution, 0.1500g KIO3 powderwas weighed and subsequently dissolved

    into a 50mL beaker. The contents were

    transferred to 100-mL volumetric flask

    and bulked to mark. Three 10.00mL

    aliquots were transferred each into 250-mL

    Erlenmeyer flasks, diluted with 20.0mL

    distilled water and added with 1.0g KI

    and 10.0mL of 0.5M H2SO4. The solution

    was then titrated with standard Na2CO3until pale yellow colour is observed. Until

    then, 1.0mL of the starch solution was

    added to the analyte. Titration was

    continued until the disappearance of the

     blue colour. The procedure was repeated

    for the other two flasks.

    For the analysis of the water sample, a

    glass bottle covered with aluminium foilwas filled to the brim with pond water. It

    was added with 0.5mL MnSO4 solution

    and 0.5mL alkaline iodide azide solution,

    taking care to avoid inclusion of air

     bubbles. The sample was then mixed and

    the formation of a brown precipitate was

    observed. The sample was added with

    2.0mL concentrated H3PO4, again taking

    care to avoid the inclusion of air bubbles.The sample was mixed, and left to stand

    for 10 minutes. 50mL aliquot of the

    sample was transferred into a 250mL

    Erlenmeyer flask and titrated with

    standard Na2CO3 solution until pale

    yellow colour was observed. 1.0mL of the

    starch solution was added to the analyte

    and titration was continued until the

    disappearance of the blue colour. Theanalysis was performed in triplicate.

    RESULTS AND DISCUSSION

    The Na2S2O3 solution is not stable and is

    therefore standardized against a primarystandard, IO3

    - to become an effective

    titrant. During the standardization, the

    comproportionation redox reaction

     between IO3- and I- occurs as seen in (1).[5] 

    −¿+3 H 2O(1)+¿→3  I 

    3

    ¿

    −¿+6  H ¿

    −¿+8  I ¿

     IO3

    ¿

    The reaction in (1) yields I3- which is then

    titrated with S2O32-, as seen in (2).

    2−¿(2)−¿+S

    4O

    6

    ¿

    2−¿→3 I ¿

    −¿+2S2O

    3

    ¿

     I 3

    ¿

    Therefore, integrating reactions (1) and

    (2), we get a stoichiometric ratio of 1 mol

    IO3- is to 6 moles of S2O3

    2- (see Appendix C

    for the dimensional analysis).

    Before the standardization of the

    thiosulfate solution with IO3-, excess KI

    and H2SO4 was added to the solution

    containing the primary standard, in that

    specific order. KI was added for the

    comproportionation reaction to occur.

    H2SO4 is added to create an acidic

    environment for the reaction, enabling it

    to occur. It is important to add KI before

    sulfuric acid since the H+ ions released

    from H2SO4 will react with the IO3- in the

    solution to form iodic acid. HIO3 is a weak

    acid, and its formation from itsconstituents in solution is highly probable.

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