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Terrestrial Palaeoecology and Global Change

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Chapter 8. Ecosystem evolution<br />

279<br />

duction of leaf/xylem ratio with extinction of macrophyllous cycadophytes induced dental<br />

innovations in the Late Cretaceous ornithopods, their posterior occlusive dentition <strong>and</strong><br />

toothless beaks increasing the range of palatable plant tissues (Norman & Weishampel,<br />

1985; Wing & Tiffney, 1987). Semenivory <strong>and</strong> frugivory might have evolved in respect to<br />

the ornithopod feeding habits that were reciprocated by endozoochorous adaptations in<br />

plants in turn preparing the herbivore niches for the early mammals (e.g. a hard seed<br />

gnawing in the mid-Eocene: Collinson & Hooker, 2000)<br />

Plant–animal interactions are commonly recognized as a leading factor in the origin<br />

of flowering plants <strong>and</strong> the build-up of their morphological <strong>and</strong> biochemical diversity.<br />

With flowering plants, pollination ecology has become a focal point of ecosystem evolution.<br />

Multistratal canopies of angiosperm communities have greatly enhanced animal<br />

biodiversity while, on the other h<strong>and</strong>, certain angiosperm-dominated biomes, in particular<br />

the grassl<strong>and</strong>s, are sustained by herbivory. With the rise of flowering plants, the herbivore–vegetation<br />

systems (such as the grazer–grassl<strong>and</strong> systems) took control over plant<br />

evolution intercepting the climate–vegetation systems.<br />

Yet, by the appearance of flowering plants, all the essential modes of plant–arthropod–tetrapod<br />

interactions were there, ready for the newcomers to pick up. In this way,<br />

diversification of a new group is prearranged by the antecedent co-adaptations.<br />

VIII.1.4. Coenotic gene pool<br />

An as yet not fully appreciated aspect of co-evolution is related to the role of exogenous<br />

nuclear acids, conceivable since the fundamental discovery by Gershenson (1939).<br />

The genomes of multicellular organisms are not impenetrable to genetic material scattered<br />

over biotic community in the form of DNA <strong>and</strong> RNA molecules stored in soil <strong>and</strong><br />

transduced by various microorganisms (Kordum, 1982). Recent genetic research has<br />

revealed the ubiquity of microbial gene transduction as a powerful mutagenic factor<br />

(Syvanen & Kado, 1998; Vorontsov, 2000). Gene pools of co-existing populations are<br />

thereby included in the higher order, coenotic, gene pool of the biotic community.<br />

The coenotic gene pool concept may prove useful in elucidating the origins of symbiotic<br />

systems. Thus, plant–fungi interactions involve genetic transduction as a method<br />

of symbiotic integration. Plants having ectomycorrhizal symbionts produce elicitors of<br />

fungal growth that comprise chitinases of fungal cell walls (Salzer et al., 1997), a<br />

biochemical convergence owing to a one way or possibly reciprocated flow of genetic<br />

material.<br />

Since physiological responses induced by symbionts are more flexible <strong>and</strong> less costly<br />

than constitutional changes, symbiosis plays a leading role in plant evolution. Plant –<br />

fungi symbiosis is the most ancient one, with primitive plants penetrating the mycelia <strong>and</strong><br />

vice versa. Certain plant – fungi interactions, in particular, with an involvement of haploid<br />

spores <strong>and</strong> pollen grains, are fairly persistent over times (Fig. 112). The developing fun-

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