removal of steroid hormones by activated carbon adsorption

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    REMOVAL OF STEROID

    HORMONES BY

    ACTIVATED CARBON

    ADSORPTION -

    KINETIC AND

    THERMODYNAMICSTUDIES

    by: Augustine O. Ifelebuegu

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    EndocrineDisrupting Chemicals

    - are substances that alter the hormonal system.

    - 17beta-estradiol(E2) and 17alpha-

    ethinylestradiol(EE2) are examples of EDC.

    - usually found as discharged to the environment

    through effluent from wastewater treatment.

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    Granular Activated Carbon

    - usually used in the treatment of potable water.

    - can remove E2 and EE2 steroid hormones by

    adsorption.

    Parameters such as pH, temperature, and weight of

    adsorbent (GAC) are deliberated using adsorption

    isotherm, pseudo first and second order kinetics,

    Gibbs free energy, enthalpy and entropywere used.

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    Effects of pH (4, 5, 6, 8 and 10)

    - Percentage efficiency was better in the acidic and

    neutral pH ranges.

    - Negative carbon particles reduce the sorption

    process by electrostatic repulsion.

    - Higher pH results in the production of aquacomplexes which reduces the adsorption capacities

    of the activated carbon.

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    Effect of varying adsorbent dose

    - The adsorption rate of E2 and EE2 increased

    initially up to a certain level and remained constant

    afterwards.

    - The initial increase is attributed to the greater

    availability of the surface area and increased

    adsorption site at higher concentrations of the

    adsorbents.

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    Pseudo 1stand 2ndorder

    = 1( )(1)

    = 2( )

    2(2)

    where: t is contact time in (min)

    k1is pseudo 1storder adsorption rate constant,

    (min-1

    )qe, q are the amount of the adsorbate at equilibrium

    time

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    Pseudo first order kinetics can be obtained by:

    = (3)

    while,1

    1

    = (4)

    will give the k for the pseudo second order

    kinetics

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    Intra-particle diffusion kinetics

    = 1/2 + C(5)

    - Non of the plots for E2 and EE2 passed through

    the origin.

    - There are two sections on the plot which show

    some fit (the initial and the last sections).

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    - The initial part may be considered as the faster

    adsorption stage and can be attributed to the

    boundary layer diffusion of E2 and EE2 on the

    external surface of the activated carbon.

    - The last stage shows decrease as a result of lower

    adsorbate concentration.

    - The middle stage (curved part) is where the intra-

    particle diffusion kinetics is controlled.

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    Effects of Temperature

    - sorption process showed increase with increasing

    temperature.

    = (6)

    = (7)

    = (8)

    where: R is gas constant

    T is temperature (K)

    =

    is the quantity of the adsorbate that

    adsorbed onto the adsorbent (L/g)

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    - Enthalpy indicates chemical nature of the sorption

    process.

    - Increase in temperature increases the sorption

    capacity.

    - Positive entropy suggest an increased randomness

    after the adsorption process.

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    Adsorption Isotherms

    =

    1+ (9)

    = ()(

    )(10)

    where: qeis the amount of adsorbate adsorbed per

    unit mass of adsorbent (mg/g)

    Ceis equilibrium concentration

    qm, b, kf, n are emperical constants

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    Langmuir equations:

    - qmcorresponds to the surface

    concentration.

    - b relates to the energy of adsorption.

    Freundlich equations:

    - kf estimation of the adsorption capacity.

    - 1/n measure of strength of adsorption.

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    - Based on the data, there was no perfect fit of the

    experimental data to any of the models.

    - Langmuir isotherm model obtain better fits

    - Adsorption of E2 and EE2 occurs in localized sites.

    - Freundlich isotherm model showed fairly good fit.

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    - Organics present in the water may have effects in

    isotherm models.

    - Freundlich isotherm, n is below unity the adsorption

    process is chemical process.