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Symbiotic Fungi: Principles and Practice (Soil Biology)

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294 J. Álvarez-Sánchez et al.<br />

wind exposure can also be increased, which can cause tree damage or death<br />

(Laurance et al. 2000; Benítez-Malvido <strong>and</strong> Martínez-Ramos 2003).<br />

These changes also produce alterations in soil microbiota, of which one of the<br />

most important components are the mycorrhiza-forming fungi <strong>and</strong> nitrogen-fixing<br />

bacteria. Hart <strong>and</strong> Reader (2004) observed that the arbuscular mycorrhizal fungi of<br />

the suborder Gigasporineae were significantly less affected by soil disturbance than<br />

Glomineae, considering root colonization <strong>and</strong> spore density.<br />

18.1.2 Restoration<br />

One of the principal objectives of restoration programs should be the facilitation of<br />

system function reestablishment, maintaining long-term stability. This could require<br />

the restoration of soils using a native microbiotic community (Haselw<strong>and</strong>ter<br />

1997; Requena et al. 2001), especially arbuscular mycorrhizal fungi which allow<br />

soil retention by forming aggregates <strong>and</strong> retaining organic material. This improves<br />

soil structure <strong>and</strong> reduces or prevents water <strong>and</strong> wind erosion, along with their<br />

respective nutrient loss (Jasper 1994; Haselw<strong>and</strong>ter 1997).<br />

Facing rapid rain forest deterioration, restoration ecology practices are extremely<br />

necessary as they allow ecosystem recuperation. Restoration ecology is defined as a<br />

process where the objective is to recuperate one or more ecosystem functions<br />

or attributes. This allows the recuperation of species composition as well as their<br />

interactions <strong>and</strong> relationships until a close resemblance to the original community is<br />

obtained (SER 2004; Hobbs 2005). Restoration is based on successional models<br />

in order to reconstruct the abiotic environment, <strong>and</strong>, in turn, helping natural succession<br />

processes <strong>and</strong> a return to the original system conditions (Suding et al. 2004).<br />

In the tropical rain forest, regeneration <strong>and</strong> succession occur naturally due to<br />

the life histories of the species, which are adaptive responses to environmental<br />

conditions. Light-dem<strong>and</strong>ing species (pioneers) occupy the first successional stages,<br />

grow in high light environments, have rapid growth rates, produce many small fruits,<br />

<strong>and</strong> can have invasive growth patterns <strong>and</strong> low herbivore defense capacities. Shadetolerant<br />

species (late successional) have slower growth rates, produce larger fruits in<br />

smaller quantities, develop more herbivore defense <strong>and</strong> can form seedling banks<br />

(Martínez-Ramos 1994). Other species traits are shown in Table 18.1.<br />

18.1.3 What is the Role of Arbuscular Mycorrhizal <strong>Fungi</strong><br />

in Habitat Recovery?<br />

In the last decade, the use of arbuscular mycorrhizal fungi (AMF) as an additional<br />

tool in restoration has been proved to be effective. Maintaining or reestablishing<br />

a native community of these fungi can contribute to the recuperation of some soil<br />

properties (Allen et al. 2003).

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