THE EFFECTS OF HERBIVORY AND POLLEN LIMITATION ON A DECLINING POPULATION OF TRILLIUM GRANDIFLORUM
By T. Knight. 2004
193 citations recorded by the source corpus.
Subfields: Ecology, Ecology, Evolution, Behavior and Systematics, Nature and Landscape Conservation
View Paper: https://www.semanticscholar.org/paper/1f0ced3dd5334d205b395daa5c704b7dc443a6b7
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In Ecology
In Ecology, Evolution, Behavior and Systematics
In Nature and Landscape Conservation
Citations in the corpus
- Impacts of insect herbivory on cactus population dynamics: experimental demography across an environmental gradient (2009, background): “…low- and mid-elevation zones than effects reported for species with limited adult longevity (e.g., Shea and Kelly 1998, Parker 2000, Rose et al. 2005), but within the range reported for other longlived perennials (e.g., Ehrlen 1995, Garcia and Ehrlen 2002, Froborg and Eriksson 2003, Knight 2004).”
- Population growth rate of a common understory herb decreases non-linearly across a gradient of deer herbivory (2009, methodology): “In contrast, herbaceous understory plants often experience greater herbivory at larger, reproductive stages (Augustine and Frelich 1998, Rooney and Gross 2003, Knight 2003, 2004, McGraw and Furedi 2005).”
- Restoring forest herb communities through landscape-level deer herd reductions: Is recovery limited by legacy effects? (2010, background): “For Trillium spp., we recorded the proportion of stems in three distinct demographic stages (one-leafed individual, threeleaf non-reproductive, three-leaf reproductive; Knight, 2004) and height in all three census periods as well as total stem density in 2003 and 2007.”
- Interaction frequency as a surrogate for the total effect of animal mutualists on plants (2005, background): “Extrapolating these effects to the population level would require assuming strong dependence of plant density on seed production, which is not necessarily the case (Bierzychudek 1982; Ehrlén & Eriksson 1995; Parker 1997; Knight 2004).”
- Hunting for fear: innovating management of human–wildlife conflicts (2013, background): “Overabundant populations also threaten the functioning of more natural ecosystems, for example by reducing ecosystem productivity and biodiversity, as has been suggested for cervids in the United States, Europe, Japan and New Zealand (Côt e et al. 2004) and elephants in fenced reserves in southern ”