2006) as in the case of native fynbos afforestation in South Africa where geophytes and wind dispersed species survived under plantations whereas woody large-leaved species such as protea did not (Richardson and Van Wilgen 1986). Changes in community structure are also reflected in changing amounts
of exotic versus native species. While native species richness decreased in all cases that reported it, exotic species increased (or was unaffected in two cases) in all reporting cases. Increased dominance of exotic species may be attributed to increased disturbance, changes click here in light and soil conditions, and, in some cases, changes in land management, including exclusion of grazing (Buscardo et al. 2008). Natural grasslands and shrublands have historically received little conservation attention in comparison to forested ecosystems (Andres and Ojeda
2002; Putz and Redford 2010). The low number of case studies in the shrubland to plantation and grassland to plantation categories is reflective of the paucity of publications examining the effects of afforestation on biodiversity. While SN-38 purchase this is changing with increased appreciation of their high biodiversity value, many non-forested ecosystems lack formal conservation measures to prevent afforestation (Andres and Ojeda 2002; Buscardo et al. 2008) and are rarely given consideration in carbon-based conservation efforts (Putz and Redford 2010). Afforestation of natural and semi-natural grasslands and shrublands has been shown to decrease soil carbon and stream flow (Guo and Gifford 2002; Farley et al. 2004, 2005) and to increase stream acidity (Farley et al. 2008). Given that other ecosystem services, in addition to biodiversity, are also often adversely affected, afforestation of natural
and semi-natural grasslands and shrublands, from an ecological perspective, can be seen as generally leading to a suite of negative impacts (Sapitinib order Brockerhoff et al. 2008; Buscardo et al. 2008). Our finding that primary forests supported an average of 35% more species than plantations is not surprising Cepharanthine as, regardless of management, species selection, age, or land-use history, primary forests will most often support higher levels of native species richness and abundance than plantation forests (Cavelier and Tobler 1998; Lindenmayer and Hobbs 2004; Brockerhoff et al. 2008; Goldman et al. 2008). The intensity of land use during any intermediate agricultural phase can affect soil properties, the amount of relict vegetation, and micro-topography, which in turn will influence biodiversity outcomes (Aubin et al. 2008; Brockerhoff et al. 2008). For this reason, it is important to distinguish between plantations directly replacing native forests and plantations established in already degraded areas in order to avoid “inappropriate comparisons” (Paquette and Messier 2010).