21.03.2015 Views

Introduction to Fungi, Third Edition

Introduction to Fungi, Third Edition

Introduction to Fungi, Third Edition

SHOW MORE
SHOW LESS

Create successful ePaper yourself

Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.

454 LICHENIZED FUNGI (CHIEFLY HYMENOASCOMYCETES: LECANORALES)<br />

be <strong>to</strong>o hostile for free-living forms. The lichen<br />

symbiosis can thus be considered an alternative<br />

adaptation <strong>to</strong> terrestrial life as compared <strong>to</strong><br />

higher plants.<br />

16.2.6 Lichens and pollution<br />

Lichens are particularly sensitive <strong>to</strong> aerial pollutants,<br />

and especially <strong>to</strong> sulphur dioxide, SO 2<br />

(Seaward, 1993; Gries, 1996; Nash & Gries, 2002).<br />

The pho<strong>to</strong>biont appears <strong>to</strong> be generally more<br />

sensitive than the mycobiont. The disappearance<br />

of lichens from the centres of urban and<br />

industrial areas was first recognized by Nylander<br />

(1866), who had already correlated this phenomenon<br />

with aerial pollution. Because different<br />

lichens show a differential sensitivity <strong>to</strong> SO 2 ,<br />

the presence or absence of key species can be<br />

used as an index of the level of air pollution<br />

(Hawksworth & Rose, 1970). The most SO 2 -<br />

<strong>to</strong>lerant lichen, Lecanora conizaeoides, may have<br />

evolved in SO 2 -polluted areas and went on <strong>to</strong><br />

become Northern Europe’s most abundant lichen<br />

by the 1950s (Richardson, 1975). This lichen may<br />

actually require elevated SO 2 levels for good<br />

growth (Nash & Gries, 2002), as shown by its<br />

disappearance from some areas after the implementation<br />

of legislation <strong>to</strong> curb SO 2 emissions.<br />

At the same time, formerly polluted areas are<br />

being re-colonized by many SO 2 -sensitive species<br />

(Rose & Hawksworth, 1981; Seaward, 1993). An<br />

example of this trend has been given by Masuch<br />

(1993) for the city of Munich. Between 1891 and<br />

1956, the ‘lichen desert’ (i.e. lichen-free zone) in<br />

the city centre increased from 8 <strong>to</strong> 56 km 2 , and<br />

then it decreased again, disappearing al<strong>to</strong>gether<br />

by 1983. The size of the ‘lichen desert’ has been<br />

correlated with the degree of SO 2 pollution in<br />

the air. Careful studies of lichen population<br />

dynamics have revealed that lichen species recolonizing<br />

a lichen desert may be different from<br />

those initially present. This phenomenon has<br />

been explained by the eutrophication of urban<br />

habitats, i.e. their enrichment especially with<br />

nitrogen (Seaward, 1997; Seaward & Coppins,<br />

2004). One of these newcomers in urban lichen<br />

deserts is Dirina massiliensis f. sorediata, which is<br />

the cause of a rapid decay of limes<strong>to</strong>ne monuments<br />

(Seaward & Edwards, 1997).<br />

Lichens obtain most of their mineral nutrients<br />

from the air and rainwater in which these<br />

are present only in very low concentrations.<br />

Not surprisingly, therefore, lichens can accumulate<br />

dissolved substances from very dilute<br />

solutions. For instance, lichens concentrate<br />

radioactive nuclides which enter the food chain<br />

lichen!reindeer!man, leading <strong>to</strong> their accumulation<br />

in human tissues (Richardson, 1991).<br />

Lichens are also being used <strong>to</strong> moni<strong>to</strong>r the<br />

radioactive contamination resulting, for example,<br />

from the explosion of the Chernobyl nuclear<br />

reac<strong>to</strong>r in 1986 (Seaward, 2004).<br />

16.2.7 Taxonomy of lichens<br />

The discovery of a fossilized cyanolichen in the<br />

Rhynie chert sediments (Taylor et al., 1997)<br />

indicates that lichens were present some<br />

400 million years ago when the terrestrial habitat<br />

was first colonized. Indeed, there is evidence of<br />

even older lichen-like associations (Yuan et al.,<br />

2005). A huge diversity of lichens exists <strong>to</strong>day,<br />

and there is good phylogenetic evidence that the<br />

lichenized habit has been developed and lost<br />

independently on several occasions in the course<br />

of evolution (Gargas et al., 1995; Lutzoni et al.,<br />

2001). This is also evident from the scattered<br />

placement of lichenized fungi in a wider ascomycete<br />

context. Lutzoni et al. (2001) even suggested<br />

that some of <strong>to</strong>day’s groups consisting<br />

entirely of non-lichenized species, notably the<br />

Plec<strong>to</strong>mycete lineage (Chapter 11), originated<br />

from lichenized ances<strong>to</strong>rs. Part of the proposed<br />

argument is a chemotaxonomic one, i.e. the<br />

presence of numerous secondary metabolites<br />

(especially polyketides) in the lichens and<br />

Plec<strong>to</strong>mycetes, but their absence or less-frequent<br />

occurrence in certain other groups of fungi. As<br />

with many DNA-based analyses, the phylogenetic<br />

arrangement of taxa may vary with the kinds<br />

of sequences used, and other schemes showing a<br />

less scattered distribution of lichenized fungi<br />

within the Ascomycota have been put forward<br />

(Fig. 8.17; Liu & Hall, 2004).<br />

Whereas much work remains <strong>to</strong> be done on<br />

the taxonomy of ascomycetes in general and<br />

lichenized ascomycetes in particular, some<br />

orders are beginning <strong>to</strong> take shape. These are

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!