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mineralization, by comminution <strong>of</strong> plant debris, and via faecal deposition for<br />

subsequent microbial attack (Beare et al., 1995).<br />

2.2.2 Diversity <strong>of</strong> habitats<br />

Soils are the most complex <strong>of</strong> microbial habitats as the characteristics <strong>of</strong> solid soil<br />

components are spatially and temporally variable. This influences the physical and<br />

chemical properties <strong>of</strong> soils, thus affecting both plant and microbial growth (Marshall,<br />

1976). Soil differs from other habitats in that it possesses a solid phase comprising<br />

approximately half the soil’s volume and consisting <strong>of</strong> particulate matter <strong>of</strong> varying<br />

size, which can bind biological molecules (Nannipieri et al., 2003). The remainder <strong>of</strong><br />

the soil volume consists <strong>of</strong> pores filled with air and water. The amount <strong>of</strong> pore space<br />

depends on the texture, structure and organic matter content <strong>of</strong> the soil, with<br />

individual pore size, total pore space and pore continuity affecting water movement<br />

and retention (Alexander, 1977).<br />

The most important interfaces affecting microbial behaviour in natural habitats are<br />

those <strong>of</strong> the solid-liquid type. Moisture availability at this interface can limit the<br />

movement <strong>of</strong> soil microorganisms (Marshall, 1976), with water and air movement<br />

regulating the activities <strong>of</strong> the micr<strong>of</strong>lora. Bacteria are rarely free in the liquid phase<br />

<strong>of</strong> soil, with most cells (approximately 80–90%) adhering to solid surfaces such as<br />

clay particles and humus (Alexander, 1977). Soil microhabitats are dynamic systems<br />

since environmental factors are constantly changing (Nannipieri et al., 2003). Within<br />

soil, several microhabitats exist such as the rhizoplane, the rhizosphere, aggregates,<br />

decaying organic matter and the bulk soil itself (Lynch et al., 2004).<br />

Nannipieri et al. (2003) described soil as a structured, heterogeneous, discontinuous<br />

system that is generally poor in energy sources and nutrients (compared with nutrient<br />

concentrations required for optimal in vitro microbial growth) where microbes occupy<br />

discrete microhabitats. Although available space in soil is extensive, less than 5% is<br />

generally occupied by living microorganisms (Alexander, 1977). The heterogeneous<br />

nature <strong>of</strong> soil results in the presence <strong>of</strong> so-called ‘hot spots’ (micro-sites) or areas <strong>of</strong><br />

increased biological activity, where micr<strong>of</strong>lora and fauna are concentrated because<br />

8

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