2019
DOI: 10.1007/s10530-019-01933-x
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Invasive grass affects seed viability of native perennial shrubs in arid woodlands

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Cited by 14 publications
(11 citation statements)
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“…For example, high total and specific leaf area (Allred et al 2010), high germination rates (Deschenes et al 2019), specific mechanism of nitrogen acquisition (Laungani and Knops 2009), and chemical inhibition of native plant photosynthesis (Musil et al 2009) have all, among others, been identified as features of invasive plants contributing to their invasion success. Also, competition for space and resources during recruitment or the production of allelochemicals by invasive plants may prevent native species from growing populations that could resist the invasion (e.g., Edwards et al 2019;Esch et al 2018;Grove et al 2017).…”
Section: Assessing Vulnerability To Invasionmentioning
confidence: 99%
“…For example, high total and specific leaf area (Allred et al 2010), high germination rates (Deschenes et al 2019), specific mechanism of nitrogen acquisition (Laungani and Knops 2009), and chemical inhibition of native plant photosynthesis (Musil et al 2009) have all, among others, been identified as features of invasive plants contributing to their invasion success. Also, competition for space and resources during recruitment or the production of allelochemicals by invasive plants may prevent native species from growing populations that could resist the invasion (e.g., Edwards et al 2019;Esch et al 2018;Grove et al 2017).…”
Section: Assessing Vulnerability To Invasionmentioning
confidence: 99%
“…Whereas other serious weeds of central Australia, like Tamarix aphylla and Parkinsonia aculeata, are outcompeted by established natural vegetation or are largely restricted to agricultural or disturbed areas with enhanced water or nutrient availability (Grice & Martin, 2006), buffel is an aggressive invader of many Australian arid and semi‐arid zone habitats (Fensham, Wang, & Kilgour, 2015; Firn et al., 2015; van Klinken & Friedel, 2018). Buffel directly suppresses (Abella, Chiquoine, & Backer, 2012; Eilts & Huxman, 2013) and threatens the persistence of many native plants (Clarke et al, 2005; Edwards, Schlesinger, Ooi, French, & Gooden, 2019; Eyre, Wang, Venz, Chilcott, & Whish, 2009; Fairfax & Fensham, 2000; Friedel et al., 2006) including threatened species (Griffin, 1993; Jackson, 2005). Changes in vegetation composition and structure following buffel invasion also affect species and assemblages of fauna (Bonney, Andersen, & Schlesinger, 2017; Pavey & Nano, 2009; Read & Ward, 2011; Smyth, Friedel, & O’Malley, 2009; Williams, Mulligan, Erskine, & Plowman, 2012; Schlesinger, Kaestli, Christian & Muldoon, 2020; Young & Schlesinger, 2014) and may increase the risk of extinctions.…”
Section: Introductionmentioning
confidence: 99%
“…Hence, our results indicate that the change in plant-pollinator network structure occurred due to the interaction rewiring mediated by the decline in floral resource availability and not by species turnover, or the turnover of plant functional traits. Also, despite the short-term resilience of our community in terms of functional diversity of floral traits, the persistence of invasive species in native communities may lead to cumulative changes (Strayer et al 2006;Edwards et al 2019;Yang et al 2019). Over the long term, such changes can have greater impacts on the community structure, reducing, even more, the species richness and abundance, which eventually will reduce the functional diversity and convert an originally diverse grassland community into a simplified pasture dominated by only a few species (Strayer et al 2006).…”
Section: Discussionmentioning
confidence: 99%