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Introduction to Fungi, Third Edition

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526 HOMOBASIDIOMYCETES<br />

An equally important ecological role played by<br />

the Homobasidiomycetes in the global environment<br />

is that of saprotrophs involved in the<br />

decomposition of the two most abundant organic<br />

carbon sources, cellulose and lignin, thereby<br />

releasing nutrients locked up in wood and leaf<br />

litter. The degradation of wood is achieved in<br />

two different ways, white-rot and brown-rot,<br />

and these are described briefly on pp. 527 532.<br />

A few wood-rotting species are plant pathogens,<br />

e.g. Armillaria mellea, Phellinus noxius and Crinipellis<br />

perniciosa, whereas others, notably the dry rot<br />

fungus Serpula lacrymans, cause economic damage<br />

of timber built in<strong>to</strong> houses.<br />

19.3.1 Ec<strong>to</strong>mycorrhiza<br />

Many members of the Homobasidiomycetes<br />

(including gasteromycetes), as well as a few<br />

Ascomycota such as the truffles (Tuber spp.; see<br />

p. 423), form ec<strong>to</strong>mycorrhizal associations with<br />

coniferous and broad-leaved trees. These are<br />

distinguished from the vesicular arbuscular<br />

mycorrhiza between herbaceous plants and<br />

Zygomycota (see p. 217) in several key features<br />

which have been reviewed by Smith and Read<br />

(1997) and Peterson et al. (2004). The most<br />

immediately obvious is that the bulk of the<br />

fungal biomass is located outside the plant root,<br />

hence the term ec<strong>to</strong>mycorrhiza. The colonization<br />

of a tree root by an ec<strong>to</strong>mycorrhizal fungus has<br />

reciprocal morphogenetic effects. Lateral roots<br />

show stunted growth accompanied by increased<br />

branching which is often dicho<strong>to</strong>mous<br />

(Fig. 19.10a) in response <strong>to</strong> fungal colonization,<br />

and they are covered by a thick sheath of hyphae,<br />

the mantle (Fig. 19.10b). There is also a limited<br />

colonization of the root cortex in the shape of<br />

the Hartig net, a system of unusually richly<br />

branched intercellular hyphae (Fig. 19.10b). The<br />

sequence of colonization events probably starts<br />

with hyphae being initially attracted <strong>to</strong> root tips<br />

by their exudates or possibly those of microorganisms<br />

associated with the rhizosphere, such<br />

as fluorescent pseudomonads (Garbaye, 1994;<br />

Smith & Read, 1997). Following contact with a<br />

root hair, hyphae grow alongside it until they<br />

meet the surface of the main root (Thomson<br />

et al., 1989). There, morphogenetic changes are<br />

initiated, such as hyphal branching and anas<strong>to</strong>mosis<br />

which lead <strong>to</strong> the establishment of the<br />

mantle (Massicotte et al., 1987). These changes<br />

may result from the specific recognition of wall<br />

surface molecules between the root and fungus<br />

hypha (Giollant et al., 1993; Lapeyrie & Mendgen,<br />

1993). Outside the mantle, the mycelium<br />

may extend in<strong>to</strong> the soil by a few centimetres,<br />

or much further if the fungus is capable of<br />

forming mycelial cords (see p. 581). The roots of<br />

different plants in complex forest ecosystems<br />

may be linked by common ec<strong>to</strong>mycorrhizal<br />

fungi, and there may be a net transfer of<br />

carbon from sunlit plants <strong>to</strong> those growing in<br />

the shade (Leake et al., 2004). Mineral nutrients,<br />

notably phosphate, as well as water are transported<br />

from the fungus <strong>to</strong> the plant.<br />

Carbohydrates travel the opposite way. Sucrose,<br />

the main transport carbohydrate in plants,<br />

is secreted in<strong>to</strong> the apoplast and hydrolysed <strong>to</strong><br />

give fruc<strong>to</strong>se and glucose. The latter is taken up<br />

by the fungus and converted <strong>to</strong> glycogen, trehalose<br />

or polyols (Smith & Read, 1997). Some 10% of<br />

the net pho<strong>to</strong>synthetic assimilate may be allocated<br />

<strong>to</strong> mycorrhizal fungi which make up<br />

20 30% of the microbial biomass in forest soils<br />

(Leake et al., 2004). Fruit bodies are a major sink<br />

for translocated carbon. Colourless (achlorophyllous)<br />

plants may obtain their carbon by plugging<br />

in<strong>to</strong> the mycorrhizal network, a strategy known<br />

as mycoheterotrophy (Smith & Read, 1997).<br />

Fossil records of ec<strong>to</strong>mycorrhizal associations<br />

date back some 50 million years (LePage et al.,<br />

1997), although they are more likely <strong>to</strong> be<br />

around 200 million years old (Cairney, 2000).<br />

Mycorrhizae of this kind are particularly prominent<br />

in nutrient-poor or dry soils. Many ec<strong>to</strong>mycorrhizal<br />

fungi have retained the capacity<br />

<strong>to</strong> produce hydrolytic enzymes and are capable<br />

of solubilizing, for example, phosphorus and<br />

nitrogen from complex sources (Perez-Moreno &<br />

Read, 2000). They are therefore often associated<br />

with humus layers in which saprotrophic<br />

species also grow. Ec<strong>to</strong>mycorrhizal fungi may<br />

show a greater or lesser degree of host specificity;<br />

for instance, Suillus grevillei is associated almost<br />

exclusively with larch (Larix spp.), whereas<br />

Amanita muscaria (fly agaric), Boletus edulis<br />

(cep or penny bun) or Cantharellus cibarius

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