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19 Functional Diversity of Arbuscular Mycorrhizal Fungi on Root Surfaces 339<br />

4.1 Diversity of Arbuscular Mycorrhizal Fungi Inside Roots<br />

The benefit to <strong>plant</strong>s through enhanced P uptake is expected to be markedly<br />

altered according to the effectiveness of dominant AM fungi inside roots.<br />

However, species diversity of AM fungi has generally been examined from the<br />

perspective of presence or absence of fungi in soil, not in roots (van der Heijden<br />

et al. 1998a; Bever et al. 2001). There is little evidence of a simple relationship<br />

between the relative abundance of morphotypes of AM fungi inside roots<br />

and spores in soil (Scheltema et al. 1987; Merryweather and Fitter 1998a). The<br />

effectiveness of AM fungi in taking up P in these studies is generally not considered,<br />

but neither is it easy to determine, particularly as effectiveness can<br />

change for the same fungus depending on the P status of the soil and <strong>plant</strong><br />

(Thomson et al. 1986). The diversity of AM fungi needs to be investigated further<br />

in relation to their relative abundance inside the roots (Abbott and Gazey<br />

1994). In addition, the methods applied to selecting combinations of species<br />

of AM fungi in studies of the role of species diversity need to be considered<br />

carefully (Wardle 1999). Another consideration is that AM fungi form associations<br />

with <strong>plant</strong>s that differ markedly in their growth habits and susceptibility<br />

to colonisation, and this makes assessment of the impact of diversity of<br />

AM fungi even more difficult to predict or measure at an ecosystem level.<br />

The diversity of AM fungi could be relevant to communities of AM fungi in<br />

the same way that high <strong>plant</strong> species diversity may help stabilise <strong>plant</strong> community<br />

structure and ecosystem processes (Klironomos et al. 2000; Tilman<br />

1996). However, high diversity can also lead to competitive exclusion and<br />

cause a reduction in the number of co-existing species (Huston 1994). For AM<br />

fungi, this may only reduce the abundance of some species below levels of<br />

detection (Bever et al. 2001). The competitive ability of species of AM fungi in<br />

roots is likely to be an important factor in determining the dominance of AM<br />

fungi inside roots as well as in soil. This is compounded by seasonal changes<br />

in infectivity of AM fungi (Merryweather and Fitter 1998b), which is influenced<br />

by fungal life cycles (Abbott and Gazey 1994) such as sporulation and<br />

associated changes in infectivity of the hyphae (Pearson and Schweiger 1993).<br />

As AM fungi occur as communities in soil and in roots, the extent to which<br />

they are likely to collectively contribute to P uptake (Jakobsen et al. 2001;<br />

Solaiman and Abbott 2003) depends on the mycorrhiza dependency of the<br />

host <strong>plant</strong> (van der Heijden et al. 1998b). Although there have been intensive<br />

studies of single AM fungus function, there have been few investigations of<br />

the contributions of communities of AM fungi. Reconstructed communities<br />

of AM fungi in soil can promote <strong>plant</strong> growth (Daft 1983; Daft and Hogart<br />

1983), or have no effect on <strong>plant</strong> growth (Sylvia et al. 1993). A correlation<br />

between the occurrence of AM fungal morphotypes and seasonal P uptake for<br />

AM fungi in a natural ecosystem was observed (Merryweather and Fitter<br />

1998b), which may be related to differences among fungi in the functional<br />

characteristics of hyphae they form in soil (Smith et al. 2000).

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