Chemistry of Chlorine Dioxide Pulp Bleaching - UT KnoxvilleChemistry of Chlorine Dioxide Pulp...

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Transcript of Chemistry of Chlorine Dioxide Pulp Bleaching - UT KnoxvilleChemistry of Chlorine Dioxide Pulp...

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Chemistry of Chlorine Dioxide Pulp Bleaching

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Bleaching History

• Bleach - blecan (Anglo Saxon) – to fade• First dates back to ancient Gauls: sunlight on

vegetable fibers moistened with alkaline solution from wood or vegetable ash

• Process: alkali treatment, exposure on grassy meadows to sun, washing, repeat, final treatment with lactic acid from sour milk– Became known as “grass bleaching”– Perfected around Haarlem, Holland– Material generally of linen fibers

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Bleaching History• 1756 – Francis Home (Scotland)

– Discovered that by substituting dilute sulfuric acid for lactic acid in last step, operating time is reduced.

– Still is a grass bleaching operation and not used yet for paper – “White” paper made from sorted white rags

• 1774 – Karl Wilhelm Scheele (Swedish Chemist) – discovered chlorine and pioneered use as a bleaching chemical on

vegetable fibers• Berthollet – French chemist

– discovered chlorine could be absorbed in solution of caustic potash and resulting solution had efficient bleaching action with less degrading effect on the finished goods (product)

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Bleaching History

• Thomas Henry – English – extended use of bleaching solution to paper (rag)

• 1798 – Charles Tennant – Scotland – formulated calcium hypochlorite by reaction of

chlorine gas with milk of lime

• 1799 – Charles Tennant – patent on production of bleaching powder by action of

chlorine on slaked lime – became world’s most dominant bleaching agent

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Bleaching History

• 1920’s: Continuous operating bleaching introduced by Thorne in multi-stage bleaching – for purification of pulp from demand for large

tonnages of nitrocellulose during WWI– 2 stage hypochlorite then added alkaline

extraction in between hypochlorite stages• Use of Chlorine dioxide investigated from

1920 – 1940, put into production 1940’s

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Chlorine Dioxide History

• 1946 – 1980’s used as a later bleaching stage, not for delignification – CEHDED, CEDED

• Late 1980’s realized that ClO2 and Cl2 used together had a higher delignification efficiency than Cl2 alone

• Environmental regulations dictated the switch from elemental chlorine (Cl2 & HOCl) to ClO2 and other TCF methods

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Chlorine Dioxide• Molecular Weight: 67.45• Boiling Point: 11°C• Yellow green to orange

gas, with a sharp pungent odor

• Water soluble, 10 g/L• Oxidant• Density: 2.4 x’s water• Decomposes to Cl2 and O2

with noise, heat, flame, and minor pressure wave

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Formation of Chlorine Dioxide

• Reduction of chlorate in acidic medium: – ClO3

- + 2 H+ + e- ClO2 + H2O

• Oxidation of chlorite ion: – ClO2

- ClO2 + e-

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Reductive Chemistry

• Reducing agents are used to make the e-

– SO2 + 2 H2O SO42- + 4 H+ + 2 e-

– CH3OH + H2O HCOOH + 4 H+ + 4 e-

– Cl- ½ Cl2 + e-

– H2O2 O2 + 2 H+ + 2 e-

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Making Chlorine Dioxide

• 2 ClO3- + SO2 2 ClO2 + SO4

2-

• 4 ClO3- + CH3OH + 4 H+ 4 ClO2 +

HCOOH + 3 H2O• ClO3

- + Cl- + 2 H+ ClO2 + Cl2 + H2O• 2 ClO3

- + H2O2 + 2 H+ 2 ClO2 + O2 + 2 H2O

• ClO3- + 6 H+ + 6e- Cl- + 3 H2O

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Chlorine Dioxide

Chemical properties:

One of several known oxides of chlorine.

Chlorine dioxide is a powerful oxidizing agent - an electron receiver. This means that the chlorine dioxide molecule is in constant search for an additional electron. → Disinfection The destruction of pathogenic and other kinds of

microorganisms by physical or chemical means

When a bacterial cell comes into contact with chlorine dioxide it donates an electron from its cell wall, thereby creating a breach in the cell wall through which cell contents pass in an attempt to bring the concentrations on either side of the cell membrane to equilibrium. The cell dies through lysis.

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Chlorine Dioxide

How long has chlorine dioxide been used? Chlorine dioxide has found widespread use since the early 1950s in the treatment of drinking water and swimming pools.

Today, chlorine dioxide is used by many large cities in Europe, such as (1956) Brussels, Zurich, Düsseldorf, Toulouse and Vienna, to sanitize the drinking water supply.

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Chlorine Dioxide

• Food industryFruit and vegetable washingMeat and poultry disinfectionSanitizing food process equipment

• Medical“Tristel” sterilizing solutions for medical instrumentsAir disinfection and building decontamination. (2001 anthrax attacks, US)

• Personal hygieneMouthwashes (~0.003%)ToothpastesContact lens cleaners

• Other industryCooling systems and towers in the control of Legionella.(Gram negative bacterium)

Chlorine dioxide has many applications:

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Bleaching Pulp with Chlorine Dioxide

Advantages

High brightness and brightness stabilityExcellent for shive and dirt removal - the bestHighly selective - little degradation of pulpLess organic chlorine than Cl2 and ClO-

Radical scavenger

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Bleaching Pulp with Chlorine DioxideDisadvantages

Highly explosive – hence generate on-siteHighly corrosive - need titanium equipment -high capital costExpensiveToxic - handle with careAOXChlorate formation

26-40% loss in oxidation power

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ClO2 Delignification Process Conditions

• Total Chemical Charge: 0.15 – 0.25 kappa factor

• Chlorine dioxide charge: 25 – 100% of the total

• Temperature: 30 -60° C• Total Time: 20 – 60 minutes• End pH: 1.5 – 3• Consistency: 3 – 4%

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Chlorine Dioxide Puffs

• Puff – deompostion of chlorine dioxide– 2 ClO2 Cl2 + 2 O2 + heat– Low speed wave of reaction (< 1m/s)

• Explosion: > 300 m/s

– Generators designed for up to 200 mm Hg

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AOX vs. ClO2 Substitution

012345678

0 20 40 60 80 100

ClO2 Substitution, %

AO

X, k

g/ad

mt

Unbl 30EO 23.5EOP 20.5O 16.6

Kappa

Liebergott

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Substitution of Chlorine Dioxide

• AOX Generation– AOX (kg/t) = 0.1 (Cl2, kg/t active chemical)– AOX (kg/t) = 0.1(1/2.63)(.526)(ClO2, kg/t active chemical)

0.02(ClO2, kg/t act chemical)

• On an equal weight basis ClO2 is 2.63 times as as reactive as Cl2

Cl2 + 2e- = 2Cl- ⇒ 71/2 = 35.5ClO2 + 5e- = Cl- ⇒ 67.5/5 = 13.5

35.5 / 13.5 = 2.63

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Chloroform – CHCl3

00.05

0.10.15

0.20.25

0.30.35

0 0.1 0.2 0.3 0.4

Chlorine Factor

Chl

orof

orm

, kg/

odm

t

100%71%46%28%0%

% ClO2 sub

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Effect of Chlorine Multiple on Dioxin Formation

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Substitution of Chlorine Dioxide for Chlorine

Old Bleaching Sequences:(CD)E1D1E2D2 O (CD)E1D1E2D2

ECF Sequences:D0E1D1E2D2 O D0E1D1E2D2

ECF = Elemental Chlorine-Free

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Chlorine Dioxide

O Cl O O Cl O O Cl O

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Chlorine Dioxide

• ChemistryClO2 + e-⇒ ClO2

-

ClO2- + 3H+ + 2e-⇒ HClO + H2O

HClO + H+ + 2e- ⇒ Cl- + H2O ClO2 + 4H+ + 5e- ⇒ Cl- + 2H2O

Equivalent Weight: ClO2 = 67.5/5 = 13.5Cl2 = 71/2 = 35.5

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Basic Cation Radical Mechanism of Chlorine Dioxide

R = Alkyl or R2

R1 = H, Alkyl or Aryl CT - Complex

π-Complex

Non-phenolic structures Phenolic structures

OR1

OCH3

R

ClO2

OOCH3

R

+ H+

- HClO2

R1 = Alkyl or arylR1 = H

R

OR1

OCH3

ClO2

R

OR1

OCH3

R

OR1

OCH3

+

R

OR1

OCH3+

R

OHOCH3

+

Brage, Ericksson and Gierer, Holzforschung, 45(1):23 (1991)

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- HClO2

O

H3CCOOCH3

OCH3O

- HClO2

- HOCl

CH3

OOCH3O

Dimers and polymers

O

H3CCOOCH3

O

- HOCl

+ H2O

CO2CH3

CH3

CO2H

+ H2O

- HOCl

+ HClO2

OHOCH3

CHO

OHOCH3

CH2OH

OHOCH3

H2C OClO-

OHOCH3

OHCH3O

CH3

CH2

OOCH3

ClO2 ClO2CH3

OOCH3

-OClOCH3

OOCH3

H-OClO

ClO2

+ H2O

- CH3OH

CH3

O OCH3

OClO-

CH3

OO

CH3

OOCH3

CH3

OOCH3

CH3

OOCH3

CH3

OOCH3

+ H2O

- HOCl

Bicreosol

Basic Phenolic Compound Reactions

Brage, Ericksson and Gierer, Holzforschung, 45(1):23 (1991)

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Basic Non-Phenolic Compound ReactionsCH3

OCH3

OCH3

+

CH3

OCH3

OCH3+

CH3

OCH3

OCH3H

+

CH3

OCH3CH3O+

CH3

OCH3

OCH3

H

+

CH3

OCH3

OCH3

+

CH3

OCH3

OCH3H

-OClO+

CH3

OCH3

OCH3

H-OClO +

ClO2ClO2 ClO2

ClO2

CH3

OCH3

O

O

+ H2O

- HOCl- H+

+

CH3

OCH3CH3O OClO-

CH3

OCH3

OCH3

O

- CH3OH - CH3OH

- H+- HOCl

+ H2O+ H2O- HClO2- H+- CH3OH

+ H2O- HOCl

CH3

HO HO

CO2CH3

CH3

OCH3

OCH3

-OClO

+

CO2CH3

CH3

CO2CH3

CH3

OCH3

OCH3

ClO2

ClO2

ClO2 ++ ClO2

Brage, Ericksson and Gierer, Holzforschung, 45(1):23 (1991)

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0

20

40

60

80

100

0 50 100 150Reaction Time (min.)

Perc

ent C

ompo

und

I

pH 2pH 4pH6pH 8

ClO2 Oxidation of Methylveratrylalcohol

Effect of pH on Rate of Reaction

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O

O

H3C

OCH3

O

OCH3

OCH3

CHHO CH3

Cl

OCH3

OCH3

OH3C

OCH3

OCH3

Cl

Cl

CHCH3HO

OCH3

OCH3

O

O

OCH3

3 5 6

8 9 10

Effect of pH on the Reaction of ClO2 with Methylveratrylalcohol (MVA)

OCH3

OCH3

CH3HO

MVA

Gunnarsson and Ljunggren, Acta Chem. Scand., 50: 442 (1996)

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Effect of End pH in a D1 Stage on Brightness and Chlorite and Chlorate Formation

6668707274767880828486

2 3 5 7 8 10End pH in the D1 stage

Brig

htne

ss, %

ClO2-ClO3-ClO3- + ClO2-Brightness

1.81.6

1.4

1.2

1.00.80.60.40.2

Chlorate and/orchlorite, % ofavailable chlorine on pulp

Rapson, H., and C.B Anderson, Tappi, 61 (10):97 (1978)

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0.0

1.0

2.0

3.0

4.0

5.0

0 2 4 6 8 10 12

End pH

Con

cent

ratio

n (m

M)

ChloriteChlorate

Kappa no. 10.7, kappa factor 0.20, pulp consistency, 3.5%, 60oC, 60 min

Effect of pH on ClO3- and ClO2

- formation in ClO2prebleaching of oxygen delignified kraft pulp

Wang, L. J. and B. H. Yoon, Paper presented at the International symposium on Cellulose and Lignocellulosics Chemistry 2000, Dec. 16-18, 2000, Kunming, China

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Effect of End pH in a D1 Stage on Brightness and Chlorite and Chlorate Formation

6668707274767880828486

2 3 5 7 8 10End pH in the D1 stage

Brig

htne

ss, %

ClO2-ClO3-ClO3- + ClO2-Brightness

1.81.6

1.4

1.2

1.00.80.60.40.2

Chlorate and/orchlorite, % ofavailable chlorine on pulp

Rapson, H., and C.B Anderson, Tappi, 61 (10):97 (1978)

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2ClO2 + HOCl + H2O 2ClO3- + HCl + 2H+ (4)

ClO2 + Free Radical + H2O ClO3- (1)

2ClO2 + HO- HClO2 + ClO3

- (2)

HClO2 + ClO2- HOCl + ClO3

- (3)

ClO2- + HOCl + H2O* *ClO3

- + HCl + H2O (5)

Chlorate Forming Reactions

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pK1~ 1.8 pK2 ~ 7.5Cl2 + H2O ClO- + H+K1 K2

H + Cl + ClOH

H C lO 2 C lO 2- + H +

p K a ~ 2 .3

Dissociation Constants of Hypochlorousand Chlorous acids

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-d(ClO2-)/dt = k1(HClO2)2 + k2(ClO2

-)(HClO2)

HClO2 ClO2- + H+

pKa~2.3

HClO2 + Cl- + H+ 2HOCl (7)Fast

HClO2 + ClO2- HOCl + ClO3

- (3) Slow

Disproportionation of Chlorous Acid

Kieffer andGordon, Inorganic Chem., 7(2):239 (1968)

Hong and Rapson, Canadian J. Chem., 46:2053 (1968)

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ClO2- + HOCl Cl Cl

O

O-HO-

ClO2- 2ClO2 + Cl- (6)

H2O

ClO3- + HCl + H+ (5)

Oxidized Lignin + Cl-/ 2Cl-

Lignin + ClOH/Cl2

Organic-Cl + H2O/ Cl-

Competitive Reactions of Hypochlorous Acid

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Summary

• In D0, the increase in chlorate and bleaching efficiency levels off at end pH below 3.4, whereas AOX continues to increase with decreasing pH.

• In D0, the phenolic hydroxyl content of lignin in pulp has little effect on either chlorate formation or bleaching efficiency.

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Summary• The phenolic lignin structures have demonstrated enhanced reactivity with chlorine dioxide over that of the non-phenolic units.

• The initial stage of ClO2 delignification is believed to be the abstraction of an electron from the phenolate anion followed by further degradation caused by additional equivalents of chlorinedioxide.• Lactones, muconic acid esters, maleic acid, oxiranes and quinoidstructures are the dominant oxidation products along with significant levels of methanol.• Chlorinated organics are produced during ClO2 bleaching, primarily due to the in situ formation of hypochlorous acid.