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    CH3CO3H

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    u

    Bleaching is a chemical decoloration and delignification process

    carried out on various types of pulp. e gn cat on

    Removal of the chromophores

    n us r a sca e, eac ng s per orme y c or ne, c or nedioxide, oxygen, hydrogen peroxide, ozone and peracetic acid.

    c ency: 2 = 2 = 3 3 2 2 2

    Often bleaching chemicals are wasted in secondaryreact ons.

    2

    D. Lachenal and C. Chirat, Cellulose Chem. Technol., 39, 5-6, 511-156 (2005)

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    x y-

    # of e- can be exchanged per bleaching molecule

    O3 + 6 e- + 6 H+ 3 H2O

    ClO + 5 e- + 4 H+ Cl- + 2 H O

    O2 + 4 e- + 4 H+ 2 H2O

    H O + 2 e- + 2 H+ 2 H O

    CH3COOOH + 2 e- + 2 H+ CH3COOH + H2O

    # of e- exchanged per molecule decreases in the following order:

    O3 > ClO2 > O2 > H2O2 = CH3COOOH

    3

    D. Lachenal and C. Chirat, Cellulose Chem. Technol., 39, 5-6, 511-156 (2005)

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    u x - 2 3

    g un eac e ra t pu p, appa rom to ~ -

    2.3% ClO2

    (0.034 mole) on pulp: 0.034 x 5 = 0.17 e- is exchanged

    -. 3 . . = .

    Chemicals % consumed1 Kappa number *

    ClO2 2.3 4.5O3 1.5 3.5

    O3 1.4 5.0

    O3 1.3 6.51Chemicals consumed are shown as % on pulp. For example,

    For 2.3% ClO2 consumed: 2.3 g ClO2 was used to bleach 100g pulp.

    * After alkaline extraction: 3% NaOH 10% consistenc 60 min 70 C

    4

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    x - 2 3

    Assume complete aromatic ring rupture should occur for a full

    .

    Assume 200 g/mol of aromatic unit, so 3.75 g lignin in100 g pulp has

    1.87 x 10-2 mole of aromatic unit.

    Theoretical # of e- exchanged is 1.87 x 10-2 x 4 = 0.075, which is lessthan half of the actual # of e- exchanged, 1.7 mole.

    At least half of the chemicals (ClO2, O3) are used in other reactions,

    and there is a considerable potential for chemical saving in the.

    5

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    Actual Electron Exchan e

    - CH3COOOH, H2O2 and O2

    Initial Chemicals T (C) Time (h) Ka a #

    ClO2 or O3, so comparison should be made for a lower total kappa drop.

    charge (%) consumed1 (%)

    Pa 3.00 3.00 90 3 13.5

    P 1.36 1.30 60 3 17.8

    O Excess 1.50* 110 1 13.5

    D 1.07 1.05 70 1 10.2

    Z 0.60 0.60 50 - 10.6n t a appa : . ;

    Kappa # measured after alkaline extraction in the case of Pa, D and Z;1Chemicals consumed are shown as % on pulp;

    6

    * estimation.

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    Actual Electron Exchan e

    - CH3COOOH, H2O2 and O2

    # of e- exchanged to obtain an one unit kappa

    kappa #

    drop

    /kappa unit

    %*

    24.8 ClO 14.6 0.005 100

    24.8 O3 14.2 0.005 100

    24.8 O 11.3 0.016 30

    24.8 H2O2 7.0 0.010 50

    24.8 CH COOOH 11.3 0.007 70

    * Efficiency of the electron exchange (supposed to be 100% for D).

    Efficiency: ClO2 (=Cl2) = O3 > CH3COOOH > H2O2 > O2

    7

    D. Lachenal and C. Chirat, Cellulose Chem. Technol., 39, 5-6, 511-156 (2005)

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    u y u

    Efficiency of the O, P, PAA stages is lower than that

    was observed with the D and Z stages

    Lower efficiency means that, for the same number of e-

    exchanged, delignification is lower.

    One reason in the case of P and PAA, could be their

    decom osition into inactive ox en.

    8

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    y

    From chlorine to chlorine dioxideGeneration of organochlorine compounds, including dioxins

    ClO2

    was used to bleach ~20% of all kraft pulp (2005).

    ECF bleaching is now the dominant technology worldwide,accounting for + 75% of bleached kraft pulp globally.

    TCF process peaked in the mid-1990s

    Lack of stricter government regulation and consumer demand

    5-6% of bleached kraft pulp is made using TCF sequences (2005),mainly in Finland and Sweden.

    Regulations and consumer demand for TCF pulp and paper aredecreasin .

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    v . u

    Mechanical pulp: remove the chromophores

    2 2 2 2 4 commonly used

    The brightness gains are ~temporary

    Chemical pulp: remove essentially all of the residual lignin on a n muc ess gn n an mec an ca pu ps

    Sodium hypochloritechlorine (1930s) ECF TCF (?)

    10

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    u x

    After bleaching, lignin is degraded into smaller, oxygen-

    water, especially if the pH is greater than 7.

    These molecules must be removed between bleachingstages to avoid excessive use of bleaching chemicals

    .

    12

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    u

    e at ng agents or , p at or near Remove transition metal ions on bleaching

    In TCF bleaching sequences:Acidic ClO2 stages tend to remove metal ions

    TCF stages rely more heavily on oxygen-based bleachingagents which are more susceptible to the detrimental effects

    of the metal ions.

    13

    Ethylenediaminetetraacetic acid Diethylenetriaminepentaacetic acid

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    Whiteness

    a measurement of light reflectance across all wavelengthsof visible light. More common in Europe.

    Brightness

    a measurement of light reflectance of a specific wavelengthof blue light. More common in North America

    Brightness represents a more narrow measurement of light

    reflectance than whiteness.

    14

    2005 Xerox Corporation

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    x -

    CIE Whiteness, developed by the France-based International

    Commission on Illumination, is commonly used.

    Better correlates the visual ratings of whiteness for white and

    near-white surfaces (paper, paint, textile, plastic, etc.).

    easuremen s ma e un er um na on, w c s a

    standard representation of outdoor daylight.

    , ,

    Whiteness would be 100.

    Brightening Agents (OBA) will measure above 100.

    15

    2005 Xerox Corporation

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    w

    An oxidizing bleach

    Works by breaking the chemical bonds that make up the

    .

    This changes the molecule into a different substance that either

    does not contain a chromo hore or contains a chromo hore

    that does not absorb visible light.

    A reducing bleach

    Works by converting sites of unsaturation in the chromophore

    into single bonds with a reducing agent.

    light.

    16

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    x v

    For most bleaching chemicals, oxidative delignification can bedescribed primarily by ring opening of the aromatic units

    17

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    PAA is a organic compound with the formula of CH3CO3H.

    It is a colorless liquid with a characteristic acrid odorreminiscent of acetic acid and can be highly corrosive.

    When pH of water solution = 8.2 (pKa of PAA, weak acid):

    Equal amount of ionized PAA and PAA in acid form

    O O

    3

    O O

    3

    O O-

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    Continuously feeding CH3COOH and H2O2 into an aqueousreaction medium containing a H2SO4 catalyst.

    The equilibrium constant is 0.37 at room T

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    Reaction of acetic anhydride, hydrogen peroxide and

    .

    Reaction of TAED in the presence of an alkaline

    .

    O

    2 2

    N

    N

    O

    2 HOO 2 CH3COOO

    N

    N

    O H

    A series of photochemical reactions involving

    -

    O

    20

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    Used especially for Kraft pulp

    Usually carried out at relatively low pH ~4,5 PAA is in acid form and acts mainly as an electrophile

    Usually carried out at relatively low temperature

    Transition metal content of pulp should be low in order toavoid catalytic decomposition of PAA

    Sequences: O-Q-Eop-PaaQ-PO

    O-Q-Paa-PO-Q-P-Paa-P

    21

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    v u

    Relatively efficient and selective

    Industrial plants for PAA production have been constructed

    an PAA eac ng s current y n use, e t er permanent y oroccasionally, at several mills.

    22

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    v y

    As an electrophile, PAA does not react with aliphatic

    h drox l rou s and therefore does not react with mostcarbohydrates.

    However, hexenuronic acid groups in kraft pulp xylanhave a double bond and thus provide a reactive site for

    electrophilic attack.

    Furthermore, the reducing end groups of carbohydratepo ymers may e ox ze y .

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    v v

    At least 6 different types

    H drox lation demeth lation aromatic rin o enin side-chain cleavage, -ether bond cleavage and epoxidation.

    Main reactions between pulp components and PAA

    Delignification (1)Hexenuronic acid decomposition (2)

    e rate o s muc aster t an t at o , ut are otequally T sensitive.

    24

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    w

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    Oxidative ring cleavage (initiated by nucleophilic attack of peracetate ion) is

    .

    pH

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    v

    The optimum pH profile for a conventional PAA stage isan initial pH in the neutral range and a final pH of 4 - 5.

    The new stage has an initial pH of 7, after 20 minutesincreasing to pH 9.5, and a final pH in a neutral range.

    carbohydrate degradation is not affected.

    Better bleachin effect is obtained at the ex ense of hi her

    PAA consumption

    More consumed in the bleaching reactions

    Enhanced decomposition

    27

    A.V. Heiningen et al. Appita Journal, 51, 5 (1998)

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    ompar son o e wo eren rocesses

    (PH)

    (Chelated oxygen delignified pulp, 3% PAA, 20% pulp, 60 min)

    Temperature

    C

    Brightness

    % ISO

    Viscosity

    mPa.s

    Residual PAA

    % on pulp

    Untreated - 37.7 23.4 -

    PAA 60 64.9 22.3 0.65

    PA A(PH) 60 68.9 21.7 0.03

    . . .

    PAA (PH) 80 70.8 21.6 0.04

    28

    A.V. Heiningen et al. Appita Journal, 51, 5 (1998)

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    pH < 6.0, PAA is very stable (~5.5% decomposition)

    6.0 < pH < 8.1, decomposition increases 8.1 < pH < 10.0, decomposition decreases slightly

    Koubek classified the mechanisms of PAA decomposition

    in aqueous solution as follows:Hydrolysis

    ase-cata yze spontaneous ecompos t on

    Trace metal ion catalyzed decomposition

    erma ecompos on

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    y y

    No loss of active oxygen content

    A loss of active bleaching agent, since H2O2 is not an effectiveeac ng agent at ow T.

    Koubek reported that hydrolysis can occur under acidic, neutral,

    or a a ne con ons, u e mec an sms an ne cs er.

    In all cases, however, the rate is 1st order in PAA concentration.

    30

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    yz

    Free radicals are likely to be generated by metal catalyzed

    decomposition of peroxide.

    Gaseous products are generated through a radical chain

    .

    2 2

    of PAA.

    31

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    - Hexenuronic Acid Groups

    It is another main reaction besides delignification and consumesconsiderable amounts of PAA and therefore it is advisable to remove

    . At neutral pH: hexenuronate anion and PAA (much faster)

    At low pH: undissociated hexenuronic acid and PAA

    5-oxohexuronic acidFormic acid

    The electron density of the conjugated double bond in the carboxylate ion

    is higher than in the undissociated carboxylic acid group, which implies

    32

    A.S. Jaaskelainen and K. Poppius-Levlin, Nordic pulp and paper research journal, 15, 2 (2000)

    .

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    Reaction with Carboh drates

    - Reducing End GroupsPAA react easily with reducing ends of carbohydrates, however, theamount o t at n pu p s re at ve y ow.

    33

    K. Poppius-Levlin, Journal of wood chemistry and technology, 20(1), 43-59 (2000)

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    ow o mprove e ec v y

    At low pH

    Increasing the PAA charge: Hydrolysis of carbohydrates is notepen ent on t e c arge, so t e se ect v ty o e gn cat oncan be increased.

    Not increasin tem erature: Increases both the rate of

    delignification and the rate of cellulose depolymerization. At neutral pH

    Increasing PAA charge: Increase the rate of delignification.

    Increasing the temperature: Increased the rate of delignification but

    a no s gn can e ec on ce u ose epo ymer za on

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    Properties of the leaving group affect the electrophilicity

    and reactivitity of peracids with H2SO5 > HC(O)OOH >

    CH3C(O)OOH H2SO5 is more electrophilic and it favors aromatic ring

    hydroxylation

    CH3C(O)OOH is more nucleophilic and it favors oxidativering cleavage

    After Paa Pulp Bleaching:

    Residual lignin has a higher amount of PhOH The amount of acid groups is increased thereby improving the hydrophilicity

    of lignin.

    decreased improving the hydrophilicity.

    Pulp is more bleachable 35