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Nitrogen Enrichment and Plant Invasions 167<br />

ecosystem-dependent. In sand plains in the South African fynbos, alien nitrogen-fixing<br />

Acacia species increase soil nitrogen and phosphorus contents,<br />

and enhance nitrogen return in litterfall (e.g.,Yelenik et al. 2004). Remarkably,<br />

they enhance soil nitrogen mineralization rates only at nutrient-rich sites,<br />

while phosphorus mineralization was increased in Acacia stands of both<br />

nutrient-rich and nutrient-poor ecosystems (Witkowski and Mitchell 1987;<br />

Stock et al. 1995). It has been suggested that these effects are only in part the<br />

result of nitrogen fixation, and rather due to associations with mycorrhiza<br />

(Versfeld and van Wilgen 1986). There are indications that enhanced soil<br />

nitrogen caused by Acacia species promotes the invasion of other plant<br />

species. For example, a bioassay experiment showed that the alteration of N<br />

availability by Acacia increases growth rates of the weedy grass Ehrharta<br />

calycina (Yelenik et al. 2004).<br />

Lupinus arboreus. Pickart et al. (1998) studied the invasion of Lupinus<br />

arboreus in parts of North America where it does not occur naturally. Ammonium<br />

and nitrate levels in the soil of nutrient-poor coastal dunes of northern<br />

California were found to increase at higher abundance of L. arboreus. In addition,<br />

by removing L. arboreus from restoration plots, other invasive species<br />

were reduced. Pickart et al. (1998) suggested that L. arboreus invasion results<br />

in both direct and indirect soil enrichment, as a result of the associated<br />

encroachment of other nonnative species, particularly grasses.<br />

Robinia pseudoacacia. According to Boring and Swank (1984), Robinia<br />

pseudoacacia is the second most abundant deciduous tree in the world, and<br />

one of the most aggressive invaders worldwide. They reported that N 2 fixation<br />

of this species can amount to 75 kg N ha –1 year –1 . Rice et al. (2004) investigated<br />

the influence of this nitrogen-fixing species on nitrogen cycling, when it was<br />

invading a nutrient-poor sand plain ecosystem in temperate North America.<br />

They carried out a comparison between pine-oak stands and 20–35 year-old<br />

R. pseudoacacia stands in terms of soil nutrient contents, soil nitrogen transformation<br />

rates, and annual litterfall biomass and nitrogen concentrations.<br />

Compared with soils of pine-oak stands, soils of R. pseudoacacia stands had<br />

1.3–3.2 times greater nitrogen concentration. They also showed elevated net<br />

nitrification rates (25–120 times higher than in pine-oak stands), higher total<br />

net N mineralization rates, and elevated soil P pools.<br />

Ulex europaeus. In New Zealand, Egunjobi (1969) studied nine ecosystems<br />

between 1 and 57 years of age and invaded by nitrogen-fixing Ulex europaeus.<br />

In vegetation stands up to 10 years old, U. europaeus was dominant, and dry<br />

matter accumulation and nitrogen contents of dead litter and soil were highest.<br />

In later stages of succession, non-fixing species were dominant, and dry<br />

matter accumulation and nitrogen contents declined with vegetation age,<br />

indicating that U. europaeus can increase soil nitrogen levels.

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