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6 Wood Discoloration

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4.4 Cellulose Degradation 97<br />

metabolism of cellobiose instead of β-glucosidase.TheroleofCDHforcellulose<br />

degradation was discussed (Hyde and <strong>Wood</strong> 1997; Kruså et al. 2005). It<br />

was hypothesized that CDH act as link between cellulolytic and ligninolytic<br />

pathways (Temp and Eggert 1999).<br />

Insoluble, native cellulose is attacked comparatively slowly by a system of<br />

cellulolytic enzymes. A limited introduction of substituents into the cellulose<br />

molecule reduces the number of hydrogen bonds of cellulose chains in proportion<br />

to the degree of substitution (DS) and the pattern of occurrence along<br />

the cellulose chain. Depending on these features and the nature of the substituent,<br />

water solubility of cellulose derivatives may be obtained at DS values<br />

between 0.4 and 0.7, and cellulose loses its ordered structure and becomes<br />

enzymatically accessible. Cellulose acetates up to a DS of 1.4 were deacetylated<br />

by various enzyme preparations (Altaner et al. 2001).<br />

For in vitro-degradation tests, carboxymethylcelluloses (CMC) are often<br />

used as soluble cellulose substrate (e.g., Schmidt and Liese 1980). The molecular<br />

structure of CMCs was characterized e.g., by Saake et al. (2000).<br />

Pure crystalline cellulose substrates, like cotton or Avicel, are degraded by<br />

white and soft-rot fungi. Most brown-rot fungi hardly show enzyme activity<br />

against crystalline celluloses and attack only pre-treated cellulose derivatives<br />

(Highley 1988; Enoki et al. 1988), because brown-rot fungi do not possess the<br />

synergistic endo/exo glucanase system, but have only endoglucanases. Within<br />

the woody cell wall, brown-rot fungi, however, depolymerize cellulose rapidly.<br />

Thus, the presence of lignin, lignin breakdown products, hemicelluloses, or<br />

simple sugars was postulated.<br />

Due to the limitation of enzyme accessibility to the woody cell wall by its<br />

pore sizes, the conceptions on cellulose degradation within wood by brownrot<br />

fungi focused both on non-enzymatic procedures and enzymatic mechanisms<br />

(e.g., Eriksson et al. 1990; Highley and Illman 1991; Micales 1992;<br />

Ritschkoff et al. 1992; Goodell 2003). Bailey et al. (1968) postulated as preceeding<br />

non-enzymatic agent a “precellulolytic phase”. Koenigs (1974) and<br />

others showed that cellulose was oxidatively degraded by Fenton reagents<br />

[Fe(II) + H2O2 → Fe(III) + OH − +OH 0 ]. Since ferrous iron is required in Fenton<br />

reactions, which is, however, absent in oxygenated wood decay processes,<br />

asearchforamechanismtoreduceironwasmade.H2O2 can also react with<br />

copper ions and some chromium, vanadium and nickel species to generate<br />

OH 0 (Halliwell 2003).<br />

Numerous investigations stress the participation of oxalic acid (e.g., Green<br />

et al. 1991a, 1993; Micales 1992), as the acid reduces Fe 3+ to Fe 2+ , which forms<br />

from H2O2 the reactive hydoxylradical, which then depolymerizes the cellulose.<br />

In several brown-rot fungi, like Coniophora puteana, Serpula lacrymans<br />

and Oligoporus placenta, extracellular H2O2 was proven (Ritschkoff et al. 1990,<br />

1992; Ritschkoff and Viikari 1991; Backa et al. 1992; Tanaka et al. 1992). Serpula<br />

lacrymans dissolved by means of oxalic acid iron from stonewool, which<br />

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