Previous Page  2 / 17 Next Page
Information
Show Menu
Previous Page 2 / 17 Next Page
Page Background

Page 44

conferenceseries

.com

Volume 5, Issue 2 (Suppl)

Occup Med Health Aff, an open access journal

ISSN: 2329-6879

Environmental Health 2017

September 7-8, 2017

September 7-8, 2017 | Paris, France

Environmental Health & Global Climate Change

2

nd

International Conference on

POLYCYCLIC AROMATIC HYDROCARBONS (PAHS): THE PECULIARITIES OF THEIR

DEGRADATION BY LIGNINOLYTIC FUNGI

Olga Turkovskaya

a

, Natalia Pozdnyakova

a

, Ekaterina Dubrovskaya

a

, Sergei Golubev

a

and

Svetlana Balandina

a

a

Russian Academy of Sciences, Russia

P

rimary screening of 20 strains of ligninolytic fungi belonging to wood- and soil-inhabiting

basidiomycetes

and

ascomycetes

for degradative activity toward PAHs (phenanthrene, anthracene, and fluorene) showed that all the

basidiomycetes

examined were active in degrading the studied compounds. Of the three compounds tested, anthracene was the least available

to all the fungi. The degradation of this compound varied from 16 to 91%.

P. ostreatus

MUT2977, Lenzites

betulina

,

T. versicolor

MUT3403, and T. maxima metabolized phenanthrene, anthracene, and fluorene more intensely (up to 90%). Phenanthrene

and fluorene were degraded by basidio- and

ascomycetes

. Their decrease with

P. ostreatus

D1 was about 100%. One of the most

active was the ascomycete

C. herbarum

, which degraded all the PAHs 100%.

The ligninolytic enzyme system catalyzes the key stages of PAH degradation by fungi. We showed that all examined members

of the genera Pleurotus and Trametes, as well as

Len. betulina, St. murashkinskyi

, and

Sch. commune

, produced laccase and

Mn-peroxidase. Lignin peroxidase and Mn-peroxidase activities were detected in B. adusta only, whereas laccase activity was

in

Str. rugosoannulata

only. These properties are typical of these fungi. We found for the first time that PAH degradation by the

ascomycetes

Lec. aphanocladii,

F. oxysporum

and

C. herbarum

was accompanied by the production of Mn-peroxidase only. In

the ascomycete

G. candidum

, ligninolytic enzyme activity was not found.

Despite some differences, the degradation of phenanthrene, anthracene, and fluorene followed the same scheme, forming

quinone metabolites at the first stage: 9,10-anthraquinone in the case of anthracene, 9-fluorenone in the case of fluorene, and

phenanthrene-9,10-quinone in the case of phenanthrene. Data were obtained which supported the hypothesis that the degree

of PAH degradation may depend on the composition of the extracellular ligninolytic complex. The presence in the cultivation

medium of only laccase (

Str. rugosoannulata

) resulted in accumulation of the corresponding quinones in the medium.

Successive production of laccase and Mn-peroxidase (

P. ostreatus

D1) resulted in the formation and subsequent utilization of

these metabolites. The simultaneous presence of two enzymes, the activity of one of which is low (

St. murashkinskyi

), resulted

in slow degradation of these quinones. Finally, if both enzymes were highly active (

T. hirsuta

), the quinone metabolites formed

were degraded quickly. The metabolites of “deep” degradation of the PAHs (2,2’-diphenic and phthalic acids), which are

included in basal metabolism of fungi, were found.

Therefore, the affiliation of the fungi with different eco-physiological groups and their cultivation conditions affect the

composition and dynamics of production of the ligninolytic enzyme complex and, consequently, the completeness of

PAH utilization. From the data obtained, we speculate that laccase can catalyze the initial attack on the PAH molecules to

give quinones and that peroxidase catalyzes the following oxidation of these compounds, ultimately resulting in pollutant

mineralization.

Biography

Olga Turkovskaya is head of the Environmental Biotechnology Laboratory at the Institute of Biochemistry and Physiology of Plants and Microorganisms, Russian Academy

of Sciences. Her Main research areas are degradation of xenobiotics by bacteria, plants, and fungi at natural sites and in wastewater, basic aspects of plant and microbial

interactions with man-made environmental pollutants, influence of pollutants on natural ecosystems, selection and study of Plant-Growth-Promoting Rhizobacteria (PGPR)

and development of biotechnologies for nature protection.

turkovskaya_o@ibppm.ru

Olga Turkovskaya et al., Occup Med Health Aff 2017, 5:2(Suppl)

DOI: 10.4172/2329-6879-C1-032