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    Dyes in textile effluents -

    role of dyeing (printing) technologies and dye structures

    Biotreatment of dyes in effluents

    classical aerobic sewage treatment process adsorption on the sludge that

    depends on the dye solubility

    acid dyes their high solubility leads to low adsorption ( depending on the degree of sulfonation)

    direct dyes high level of adsorption not depending on sulfonation

    reactive dyes very low degree of adsorption

    basic dyes high adsorption

    disperse dyes adsorption in the high to medium range

    Reactive dyes

    high consumption, applied in high concentrations in some technologies

    relatively high concentrations in textile effluents

    small molecules, high water solubility

    decolourization

    dearomatization

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    Pathways for the aerobic

    microbial degradation of man-

    made sulfonated azo dyes by

    peroxidases from

    Phanaerochete chrisosporium

    Primarily asymmetric

    cleavage of azo linkage is

    supposed that leads to

    obtaining of sulfonamide

    and phenolic structures

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    Advantages of covalently immobilized enzyme systems

    immobilized whole cells keep a high level concentration

    of intracellular inducible multi-enzyme system

    activity of these systems remains relatively high as far as

    the immobilization does not affect the cell integrity

    possibility for use in reactors for continuous processes

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    IMMOBILIZATION of the FUNGI STRAIN of

    Trichosporon cutaneum and Phanaerochete chrisosporium

    carrier activated acrylamide copolymer

    treatment of granules with cell suspension

    suspending in synthetic nutrient medium

    ( 24 hours treatment)

    washing

    control for free cells ( spectrophotometrically)

    microscopy

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    Table 1Microbial strainMicrobial strain CarrierCarrier ImmobilizedImmobilized

    cellscells ((mg/g drymg/g dry

    carrier)carrier)

    TrichosporonTrichosporon

    cutaneumcutaneum

    SyntheticSynthetic polymerpolymer

    granulesgranules

    38.4/38.4/8,48,4forforCellulose granulesCellulose granules

    PhanerochetePhanerochete

    chrysosporiumchrysosporium

    SyntheticSynthetic polymerpolymer

    granulesgranules

    42,342,3

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    PHENOL TRANSFORMATIONABILITY

    OF IMMOBILIZED CELLS

    adaptation in a phenol medium (0,1g/l)

    phenol transformation at 0,35 g/l , 0,65 g/l

    and 1g/l substrate concentration

    HPLC measurements of phenol concentration(absorbance at 256 nm)

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    KINETICS OF PHENOL CONVERTION

    Cells Trichosporon cutaneumTrichosporon cutaneum

    0,35 g/l phenol (Immobilized cells

    proliferate, remaining stable and

    active for 22 cycles)

    0,65 g/l phenol

    1,00 g/l phenol

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    BIODEGRADATION OF PHENOL BY

    MULTYENZYME ENZYME PRODUCED IN

    IMMOBILZED Trichosporon cutaneum CELLS

    Hydroxylation

    of phenolic

    structures

    Dearomatization by

    oxidase/hydrolase

    system in

    Trichosporon

    Cutaneum

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    STUDYOF Phanarochete chrysosporium BEHAVIOUR

    immobilized cells showed a relatively slow phenoldegradation compared to Trichosporon cutaneum

    source of exo-oxidase enzyme system containing

    lccase, lignin peroxidase and manganese peroxidase

    ultrafiltration and immobilization of the aboveenzyme system

    characterization of the immobilized system with

    respect of manganese peroxidase activity

    Michaelis constant of the reaction with Phenol Red

    has the same range for free and immobilized

    manganese peroxidase

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    EnzymeEnzyme BoundBound

    proteinprotein

    [mg/g[mg/g

    drydry

    carrier]carrier]

    pHpH

    optimumoptimum

    TemperatureTemperature

    optimumoptimum [[00C]C]

    SpecificSpecific

    activityactivity

    [U/mg][U/mg]

    RelativeRelative

    activityactivity

    [%][%]

    KKmm

    [M][M]

    FreeFree

    manganesemanganese

    peroxidaseperoxidase-- 4,54,5 3030 1,3901,390 -- 6.106.10

    --55

    ImmobilizedImmobilized

    manganesemanganese

    peroxidaseperoxidase

    6,26,2 4,54,5 3535 0,1110,111 8,028,02 7,8.107,8.10--55

    Table 2

    Phenol Red

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    KINETICS OF BEZAKTIV Brill.RED V-GG DECOLOURIZATION

    BYTHE IMMOBILIZED ENZYME SYSTEM PRODUCED OF

    Phanaerochete chrisosporiumI step - dye water solution treatment (decolourization)

    II step possibility for dearomatization with immobilized Trichosporon

    cutaneum cells should be additionally investigated

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    CONCLUSIONS

    Fungi can be immobilized at high concentration

    covalently to synthetic beads retaining a high levelof stability and activity

    Immobilized cells are viable and can be used as a

    source of multy-enzyme systems

    Trichosporon cutaneum immobilized cells can beapplied for phenolic structures dearomatization

    Phanaerochete chrisosporium oxidase multy-

    enzyme immobilized on synthetic beads decolourize

    monoazo dyes in water solution

    Trichosporon cutaneum immobilized cells

    treatment of decolourized solutions have a potential

    to be used for dearomatization of above solutions