Extracellular laccases from submerged cultures of Coriolus versicolor BKM F-116, Panus tigrinus 8/18, Phlebia radiata 79 (ATCC 64658), Phlebia tremellosa 77-51 and from cultures of Pa. tigrinus 8/18, Ph. radiata 79 and Agaricus bisporus D-649 grown on wheat straw (solid-state fermentation) were purified. All enzymes from submerged cultures had a blue colour and characteristic absorption and EPR spectra. Laccases from the solid-state cultures were yellow-brown and had no typical blue oxidase spectra and also showed atypical EPR spectra. Comparison of N-terminal amino acid sequences of purified laccases showed high homology between blue and yellow-brown laccase forms. Formation of yellow laccases as a result of binding of lignin-derived molecules by enzyme protein is proposed.
Yellow and blue forms of laccase from solid-state and submerged cultures of Panus tigrinus were isolated. Both laccases had similar molecular masses and specific activity, but yellow laccase had no 'blue' maximum in the absorption spectrum. Blue laccase oxidized veratryl alcohol and a nonphenolic dimeric lignin model compound only in the presence of 2,2'-azino-bis-(3-ethylbenzothiazoline-6-sulfonic acid) as electron-transfer mediator. Yellow laccase catalyzed these reactions without any additional compounds. It is supposed that yellow laccase is formed as a result of blue laccase modification by products of lignin degradation. These compounds might play a role of natural electron-transfer mediators for the oxidation of non-phenolic substances, catalyzed by yellow laccase.
Polycyclic aromatic hydrocarbons (PAHs) are natural and anthropogenic aromatic hydrocarbons with two or more fused benzene rings. Because of their ubiquitous occurrence, recalcitrance, bioaccumulation potential and carcinogenic activity, PAHs are a significant environmental concern. Ligninolytic fungi, such asPhanerochaete chrysosporium, Bjerkandera adusta, andPleurotus ostreatus, have the capacity of PAH degradation. The enzymes involved in the degradation of PAHs are ligninolytic and include lignin peroxidase, versatile peroxidase, Mn-peroxidase, and laccase. This paper summarizes the data available on PAH degradation by fungi belonging to different ecophysiological groups (white-rot and litter-decomposing fungi) under submerged cultivation and during mycoremediation of PAH-contaminated soils. The role of the ligninolytic enzymes of these fungi in PAH degradation is discussed.
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