THE VARIABLE INVASIVE SUCCESS OF CORTADERIA SPECIES IN A COMPLEX LANDSCAPE

By J. Lambrinos. 2002

112 citations recorded by the source corpus.

Subfields: Ecology, Ecology, Evolution, Behavior and Systematics, Nature and Landscape Conservation

View Paper: https://www.semanticscholar.org/paper/71f4a8635fd6864b57a5af3580efbb5e2aad3726

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In Ecology

In Ecology, Evolution, Behavior and Systematics

In Nature and Landscape Conservation

Citations in the corpus

Emerging invasive alien plants for the Mediterranean BasinBrundu3, G. Fried4 (2010, background): “In many regions, including several countries in the Mediterranean Basin, C. selloana is considered invasive (Bossard et al., 2000; Lambrinos, 2001, 2002), particularly in the South of France, in Corsica (Natali & Jeanmonod, 1996), in Italy, in Sardinia (Brundu et al., 2003), in Spain and it escaped…”
Kudzu (Pueraria montana): History, Physiology, and Ecology Combine to Make a Major Ecosystem Threat (2004, background): “Invasive species are one of the most significant factors in anthropogenic global change and will continue to be a problem for the foreseeable future (Rejmanek, 1996; Thompson et al., 2001; Lambrinos, 2002).”
Introduction bias: Cultivated alien plant species germinate faster and more abundantly than native species in Switzerland (2011, background): “…previous studies showed that among alien plant species, the more invasive ones (or the more widely naturalized ones) frequently germinate faster and more successfully than the less invasive ones (e.g. ForcelIa, Wood, & Dillon 1986; van Clef & Stiles 2001; Lambrinos 2002; Mihulka et al. 2003).”
Altitudinal distribution of alien plant species in the Swiss Alps (2005, background): “This is partly because so many different aspects – phylogenetic groups, communities, habitats – must be considered in developing a general theory (cf. Mack et al., 2000; Lambrinos, 2002).”
Modelling invasion for a habitat generalist and a specialist plant species (2008, methodology): “BLM data sets included the results from a Noxious Weeds Inventory ( N ≥ 24,000) conducted by the BLM Utah State Office in 1997 (M. Benson, unpublished data) and from the Rangeland Health Monitoring Program ( N = 285) conducted by resource managers at the GSENM between 1999 and 2003 (Pellant et al .,”
Subtle differences in two non-native congeneric beach grasses significantly affect their colonization, spread, and impact (2012, background): “Although much less common, comparisons of non-native congeners can provide important insights into the mechanisms of invasion dynamics by assessing diff erences among phylogenetically similar non-native species (Rice and Nagi 2000, Lambrinos 2001, 2002, Muth and Pigliucci 2006).”