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Interference of soil contaminants with laccase activity during the transformation of complex mixtures of polycyclic aromatic hydrocarbons (PAH) in liquid media

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HAL Id: hal-01600210

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Interference of soil contaminants with laccase activity during the transformation of complex mixtures of polycyclic aromatic hydrocarbons (PAH) in liquid media

Christian Mougin, Claude Jolivalt, Christian Malosse, Jean-Claude Sigoillot, Marcel Asther, Veronique Chaplain

To cite this version:

Christian Mougin, Claude Jolivalt, Christian Malosse, Jean-Claude Sigoillot, Marcel Asther, et al..

Interference of soil contaminants with laccase activity during the transformation of complex mixtures of polycyclic aromatic hydrocarbons (PAH) in liquid media. 18th International Symposium on Polycyclic Aromatic Compounds, Sep 2001, Cincinnati, United States. 2001. �hal-01600210�

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Interference of soil contaminants with laccase activity during the transformation of complex mixtures of

polycyclic aromatic hydrocarbons in liquid media

C. Mougin

1

, C. Jolivalt

1

, C. Malosse

1

, J.-C. Sigoillot

2

, M. Asther

2

and V. Chaplain

1

1

Unité de Phytopharmacie et Médiateurs Chimiques Route de Saint-Cyr, F-78026 Versailles Cedex

email: [email protected]

2

Unité de Biotechnologie des Champignons Filamenteux

163, avenue de Luminy, F-13288 Marseille Cedex 09

(3)

Introduction

Laccase-producing fungi are often presented as efficient tools for the

bioremediation of soils and liquid wastes polluted by PAHs, but the efficiency of the enzymes has not been clearly demonstrated

Aims of the study:

 to determine the efficiency of fungal laccases to transform synthetic mixtures of PAHs

 to assay their use for the transformation of PAHs extracted from polluted soils

 to evidence the interference of contaminants co-extracted from the

polluted soils with PAH transformation

(4)

 Distribution: fungi, bacteria, higher plants, insects

 Function: lignin degradation, morphogenesis, pathogenesis transformation of xenobiotics

 Structure: dimeric or tetrameric glycoprotein, with 4 Cu, exocellular, 520 to 550 aa, 60 to 80 kDa

secreting a N-terminal peptide

 Regulation:

inhibitors: small anions, metals, fatty acids, chelating agents inducers: culture medium, lignin and related compounds,

xenobiotics

 Equation: 2RH + ½O

2

 2R

+ H

2

O

Properties of the fungal laccases

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Main catalyzed reactions

 RH = Phenolic compound

oxidation, bond cleavage: C-C, C-N,…

oxidative coupling

C l C l O M e C l C l O M e C l C l

OH l

C l O

O M e O H C l

C l C l H O 2 C O H

O M e

+

HO OH

OH

O

OH

OH

HO

OH

HO

HO NH

O

N O O O N

O ou N

(6)

2,2’-azino-bis(3-ethylbenz-thiazoline-6-sulfonic acid): ABTS

 RH = non phenolic compound

 a redox mediator is needed: Lac + Med  Med*

Med* + RH  Rh

ox

+ Med

O

O

O

O

O O ABTS : Acide 2,2'-azinobis-(3-éthylbenthiazoline-6-sulphonique)

N S

N N

N S

C2H5

-O3S SO3-

H5C2

+

(7)

Experimental

2-liter bioreactors containing :

 1.5 L citrate/phosphate buffer pH 3, 0.1 M

 20 mL Tween 20

 360 mg PAHs dissolved in 500 mL acetonitrile

 2 mM ABTS (redox mediator)

 4000 U laccase of Pycnoporus cinnabarinus

incubated in the dark at 30°C for 48 hours

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Incubation time (hours)

0 12 24 36 48

PAH concentration (mg/L)

0 5 10 15 20 25 80 100 120 140 160 180

Incubation time (hours)

0 12 24 36 48

PAH concentration (mg/L)

5 10 15 20 25 80 100 120 140 160 180

Synthetic mixture Soil extract

mixture, anthracene, benzo[a]pyrene, -lac, +lac

Transformation of PAHs

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Common names Amounts Transformation products

Initial (mg L-1) After 48 h (%)

Naphtalene 10.0 1.2

Acenaphthylene 4.0 31.3 1,8-naphthalic acid anhydride

Acenaphtene 3.0 17.4 1,8-naphthalic acid anhydride

Fluorene 5.0 53.7 9-fluorenone

Phenanthrene 25.0 57.2 9,10-phenanthrene dione

Anthracene 17.0 4.3 9,10-anthracene dione

Fluoranthene 22.0 59.3

Pyrene 20.0 57.3 1,6- 1,8-pyrene diones

Benzo[a]anthracene 9.0 68.6 7,12-benzo[a]anthracene dione

Chrysene 5.0 95.6

Benzo[b]fluoranthene 17.0 63.5

Benzo[k]fluoranthene 15.0 99.3

Benzo[a]pyrene 21.0 16.5 1,6- 3,6- 6,12-benzo[a]pyrene diones

Dibenzo[ah]anthracene 1.0 73.7

Benzo[ghi]perylene 1.0 80.0

Indeno[123cd]pyrene 3.0 71.8

16 PAHs 178.0 49.7

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2) ABTS

2+

+ ABTS 2 ABTS°

+

Mechanism of laccase-mediated oxidation of BaP

O

O

Lac 0.58 V Lac

1) ABTS ABTS°

+

ABTS

2+

- e

-

0.5 V - e

-

0.9 V

OH

- 6e

-

- 6H

+

+ 2H

2

0

BaP BaPQ

sensitivity to metals Fe

++

K

4

Fe(CN)

6

0.9 V (SCE)

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Fe concentration (mM)

0.000 0.075 0.150 0.225 0.300 0.375

Inhibition of BaP oxidation (%)

0 20 40 60 80 100

Effect of K 4 Fe(CN) 6 on BaP oxidation by ABTS ++

30 min

60 min

120 min

240 min

360 min

2 mL 0.1 M citrate-phosphate buffer pH 3: 5 mM peroxodisulfate

0.1 mM ABTS, 0.1 mM BaP, 0.075 to 0.375 mM K

4

Fe(CN)

6

(12)

Conclusions

 fungal laccases are able to transform 10 PAHs in a synthetic mixture of 16 compounds. The reaction needs the presence of a redox mediator

 metals, present in polluted soils, inhibit PAH transformation in withdrawing the electrons delivered by the mediator

 as the inhibition by metals is limited in time, other unknown mechanisms may explain the lack of activity of the laccases

 Are laccases really efficient in polluted soils?

How can we enhance their potential?

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Perspectives

 the results presented here have been obtained by using purified laccases from P. cinnabarinus. Similar data have been obtained later with enzymes from

T. versicolor

 we have now cloned and sequenced a gene encoding for a laccase of T. versicolor

 we have expressed it in E. coli, soon in the yeast Yarrowia lipolytica

 the directed evolution of the enzyme should also be performed

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