Degradation of phenanthrene by the rhizobacterium Ensifer meliloti

The biodegradation of the polycyclic aromatic hydrocarbon phenantherene by the rhizobacterial strain Ensifer meliloti P221, isolated from the root zone of plant grown in PAH-contaminated soil was studied. Bacterial growth and phenanthrene degradation under the influence of root-exuded organic acids...

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Veröffentlicht in:Biodegradation (Dordrecht) 2014-11, Vol.25 (6), p.787-795
Hauptverfasser: Muratova, Anna, Pozdnyakova, Natalya, Makarov, Oleg, Baboshin, Mikhail, Baskunov, Boris, Myasoedova, Nina, Golovleva, Ludmila, Turkovskaya, Olga
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creator Muratova, Anna
Pozdnyakova, Natalya
Makarov, Oleg
Baboshin, Mikhail
Baskunov, Boris
Myasoedova, Nina
Golovleva, Ludmila
Turkovskaya, Olga
description The biodegradation of the polycyclic aromatic hydrocarbon phenantherene by the rhizobacterial strain Ensifer meliloti P221, isolated from the root zone of plant grown in PAH-contaminated soil was studied. Bacterial growth and phenanthrene degradation under the influence of root-exuded organic acids were also investigated. Analysis of the metabolites produced by the strain by using thin-layer chromatography, gas chromatography, high-pressure liquid chromatography, and mass-spectrometry revealed that phenanthrene is bioconverted via two parallel pathways. The first, major pathway is through terminal aromatic ring cleavage (presumably at the C3–C4 bond) producing benzocoumarin and 1-hydroxy-2-naphthoic acid, whose further degradation with the formation of salicylic acid is difficult or is very slow. The second pathway is through the oxidation of the central aromatic ring at the C9–C10 bond, producing 9,10-dihydro-9,10-dihydroxyphenanthrene, 9,10-phenanthrenequinone, and 2,2′-diphenic acid. This is the first time that the dioxygenation of phenanthrene at the C9 and C10 atoms, proven by identification of characteristic metabolites, has been reported for a bacterium of the Ensifer genus.
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Bacterial growth and phenanthrene degradation under the influence of root-exuded organic acids were also investigated. Analysis of the metabolites produced by the strain by using thin-layer chromatography, gas chromatography, high-pressure liquid chromatography, and mass-spectrometry revealed that phenanthrene is bioconverted via two parallel pathways. The first, major pathway is through terminal aromatic ring cleavage (presumably at the C3–C4 bond) producing benzocoumarin and 1-hydroxy-2-naphthoic acid, whose further degradation with the formation of salicylic acid is difficult or is very slow. The second pathway is through the oxidation of the central aromatic ring at the C9–C10 bond, producing 9,10-dihydro-9,10-dihydroxyphenanthrene, 9,10-phenanthrenequinone, and 2,2′-diphenic acid. This is the first time that the dioxygenation of phenanthrene at the C9 and C10 atoms, proven by identification of characteristic metabolites, has been reported for a bacterium of the Ensifer genus.</abstract><cop>Dordrecht</cop><pub>Springer Netherlands</pub><pmid>25052918</pmid><doi>10.1007/s10532-014-9699-9</doi><tpages>9</tpages></addata></record>
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ispartof Biodegradation (Dordrecht), 2014-11, Vol.25 (6), p.787-795
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source MEDLINE; SpringerLink Journals - AutoHoldings
subjects Analysis
Aquatic Pollution
Aromatic compounds
Aromatic hydrocarbons
Bacteria
Biodegradation
Biodegradation, Environmental
Biomedical and Life Sciences
Biphenyl Compounds - metabolism
Degradation
Gas chromatography
Geochemistry
High performance liquid chromatography
Life Sciences
Liquid chromatography
Metabolites
Microbiology
Naphthols - metabolism
Organic acids
Original Paper
Pathways
Phenanthrene
Phenanthrenes - metabolism
Polycyclic aromatic hydrocarbons
Rhizobium - metabolism
Root zone
Soil contamination
Soil microbiology
Soil Science & Conservation
Spectrometry
Strain
Terrestrial Pollution
Thin layer chromatography
Waste Management/Waste Technology
Waste Water Technology
Water Management
Water Pollution Control
title Degradation of phenanthrene by the rhizobacterium Ensifer meliloti
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