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6 Wood Discoloration

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104 4 <strong>Wood</strong> Cell Wall Degradation<br />

veratryl alcohol (with presence of H2O2) to the aldehyde, whose amount is<br />

measured at 310 nm (Faison and Kirk 1985; Schoemaker et al. 1991).<br />

The second enzyme involved in lignin degradation is manganese peroxidase<br />

(MnP) [Mn(II):hydrogen-peroxide oxidoreductase, EC 1.11.1.13], which needs<br />

free phenolic groups at the aromatic ring and does not oxidize veratryl alcohol.<br />

The hemoprotein enzyme was first detected in P. chrysosporium (Glenn and<br />

Gold 1985) and occurs e.g., in Armillaria species, Lentinula edodes, Pleurotus<br />

ostreatus and T. versicolor. It oxidizes in the presence of hydrogen peroxide<br />

Mn(II) to Mn(III), a strong oxidant, which oxidizes phenolic structures by<br />

single-electron-oxidation (Perez and Jeffries 1992; Kofugita et al. 1992; Robene<br />

Soustrade et al. 1992; Chatani et al. 1998; Kamitsuji et al. 1999). MnP polymerizes<br />

more extensively and depolymerizes less than lignin peroxidase (Tanaka<br />

et al. 1999). Treatment of water-insoluble 14 C-labeled milled wheat straw and<br />

milled straw lignin with MnP preparations from the white-rot fungus Nematoloma<br />

frowardii resulted in the direct release of 14 CO2 and in the formation<br />

of soluble 14 C-lignin fragments (Hofrichter et al. 1999). MnP also degraded<br />

polyethylene (Iiyoshi et al. 1998).<br />

For the degradation of native lignin, a fungus must have enzymes, which attack<br />

both phenolic and non-phenolic lignin components (Martinez-Inigo and<br />

Kurek 1997). The lignin peroxidase is most likely responsible for the degradation<br />

of the non-phenolic components and the laccase as well manganese<br />

peroxidases for the oxidation of the phenolic parts (Evans 1991). All together,<br />

there is a variety of oxidative enzymes that may be utilized by white-rot fungi for<br />

lignin degradation (Highley and Dashek 1998). Various enzymes, low molecular<br />

weight agents, free-radical reactions, and metals have been proposed to<br />

participate in lignin degradation (Messner et al. 2003; Reading et al. 2003):<br />

Lignin peroxidase (LiP), manganese peroxidase (MnP), cellobiose dehydrogenase<br />

(CDH), laccases, oxalate, hydrogen peroxide, small molecule mediators,<br />

methyl transferases, and the plasma membrane redox potential are involved<br />

in the degradation systems. There is, however, still some uncertainty on their<br />

accurate participation in lignin degradation.<br />

Progress has been made concerning the molecular genetics of lignin and<br />

cellulose biodegradation by white-rot fungi, primarily with Phanerochaete<br />

chrysosporium, but also with Bjerkandera adusta, Phlebia radiata, and Trametes<br />

versicolor (reviews by Highley and Dashek 1998 and Li 2003). Genes encoding<br />

Lip and MnP have been cloned and sequenced (e.g., Irie et al. 2000). The<br />

total genome sequence of P. chrysosporium has been disclosed by the DoE Joint<br />

Genome Institute in the USA, which has facilitated cDNA cloning of various cellulase<br />

genes from P. chrysosporium and successive production of recombinant<br />

proteins from them (Samejima and Igarashi 2004). The X-ray crystal structures<br />

of both LiP and MnP have also been elucidated. By means of recombinant<br />

DNA techniques, laccase catalysis has been studied, and the crystal structure<br />

of a T2-copper deleted laccase has been reported. In Pycnoporus cinnabarinus,<br />

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