Habitat associations of trees and seedlings in a Bornean rain forest

By Campbell O. Webb, D. Peart. 2000

331 citations recorded by the source corpus.

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

View Paper: https://www.semanticscholar.org/paper/3b80c7290447ce2c23307095b40bc4e869976532

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Citations in the corpus

Pushing the limits in marine species distribution modelling: lessons from the land present challenges and opportunities (2011, background): “A limited number of terrestrial SDM applications have examined the importance of incorporating different life-history stages (Webb & Peart, 2000; Jones et al., 2007; Ficetola et al., 2009).”
Exploring the Phylogenetic Structure of Ecological Communities: An Example for Rain Forest Trees (2000, methodology): “The data set consisted of trees ( ‚ 10 cm DBH) sampled in 28, 0.16-ha plots (40 m # 40 m) in lowland mixed dipterocarp forest at the Gunung Palung National Park, West Kalimantan, Indonesia (Webb 1997; Webb and Peart 1999, 2000).”
Phylogenies and Community Ecology (2002, background): “Similarly, Webb & Peart (2000) assessed the species, genus, and family associations of rain forest trees with three habitat types and found both genera and families that had all of their species associated with a particular habitat.”
Phylogeography of the Southeast Asian stone oaks (Lithocarpus) (2003, methodology): “…as the one used in this study, can test basic hypotheses about various elements of structure in the data and do not make any assumptions about the 2003 Blackwell Publishing Ltd, Journal of Biogeography, 30, 211–226 underlying distribution (Fox, 1987; Manly, 1994; Simon, 1995; Webb & Peart, 2000).”
High seed dispersal rates in faunally intact tropical rain forest: theoretical and conservation implications (2001, methodology): “By comparing the species lists of tree plots with those of nested seedling plots in rain forest at Gunung Palung, we found that the proportion of local seedlings arising from active dispersal events (via wind or animals, but not simply dropped from parent trees) was high: 68% of species and 46% of t”
Drought effects on seedling survival in a tropical moist forest (2005, background): “At the same time, soil moisture variation may underlie plant associations with topography (e.g., ridge, slope; Webb and Peart 2000; Harms et al. 2001; Chuyong et al. 2003; Guntilleke et al. 2003; Johns and Dattaraja 2003).”
Evidence of species-specific neighborhood effects in the dipterocarpaceae of a Bornean rain forest (2005, background): “Small-scale habitat speciﬁcity may be less important than limited seed dispersal as an explanation for spatial aggregation (Newbery et al. 1996, Plotkin et al. 2000, Webb and Peart 2000).”
Mesoscale distribution patterns of Amazonian understorey herbs in relation to topography, soil and watersheds (2005, result): “…forests (e.g. Kahn 1987; Tuomisto & Ruokolainen 1994; Ruokolainen et al. 1997; Burnett et al. 1998; Clark et al. 1999; Vormisto et al. 2000; Webb & Peart 2000; Harms et al. 2001; Duque et al. 2002; Potts et al. 2002; Itoh et al. 2003), but most studies did not distinguish soil from…”
Spatial patterns in the understorey shrub genus Psychotria in central Amazonia: effects of distance and topography (2005, background): “…patterns of distribution and abundance of plants in tropical forests (Clark et al. 1999, Itoh et al. 2003, Kahn 1987, Lieberman et al. 1985, Potts et al. 2002, Ruokolainen et al. 1997, Svenning 1999, Tuomisto & Ruokolainen 1994, Valencia et al. 2004, Vormisto et al. 2000, Webb & Peart 2000).”
Developmental changes in habitat associations of tropical trees (2007, methodology): “Even when data on both seedling and adult tree distributions with respect to habitat are available, comparisons of associations at the two stages may be confounded by the fact that seedling distributions are strongly influenced by seed dispersal patterns ( Webb & Peart 2000 ).”
EDAPHIC SPECIALIZATION IN TROPICAL TREES: PHYSIOLOGICAL CORRELATES AND RESPONSES TO RECIPROCAL TRANSPLANTATION (2005, background): “5 E-mail: jbaltzer@oeb.harvard.edu observation that many tropical tree species are distributed nonrandomly among edaphic patch types suggests that edaphic heterogeneity strongly influences species diversity in a given locality (Lescure and Boulet 1985, Webb and Peart 2000, Itoh et al. 2003).”
Leaf phenology is associated with soil water availability and xylem traits in a tropical dry forest (2012, background): “At local scales, topography is the main factor determining the habitat of species (Webb and Peart 2000; Harms et al. 2001; Balvanera et al. 2002; Segura et al. 2003; PinedaGarcı́a et al. 2011).”
SEEDLING SURVIVAL AND GROWTH OF THREE FOREST TREE SPECIES: THE ROLE OF SPATIAL HETEROGENEITY (2003, background): “…niche differentiation, or microhabitat specialization (Maguire and Forman 1983, Collins and Good 1987, Collins 1990, Latham 1992, Sipe and Bazzaz 1995, Ashton and Larson 1996, Gray and Spies 1997, Broncano et al., 1998, Carlton and Bazzaz 1998, van der Meer et al. 1998, Webb and Peart 2000).”
Liana habitat associations and community structure in a Bornean lowland tropical forest (2006, background): “In contrast, Webb and Peart (2000) examined one of the habitats defined by Cannon and Leighton (2004) in more detail (dipterocarp hill forest on granite parent rock) for finer-scale habitat associations among ridges, plateaus, and gullies and found that only 35% of trees (‡10-cm DBH) showed…”
Seed dispersal patterns produced by white‐faced monkeys: implications for the dispersal limitation of neotropical tree species (2003, background): “Microsite limitation is likely to be particularly important for small-seeded and light-demanding species (Dalling & Hubbell 2002), but may also be significant for larger seeded, shade-tolerant species with topographically determined habitat requirements ( Webb & Peart 2000; Harms et al . 2001).”
Species-habitat associations change in a subtropical forest of China (2009, background): “4), the absence of a positive association with the same habitat at their sapling and juvenile stages may be a result of lower seedling establishment or recruitment success in that habitat (Webb & Peart 2000; Comita et al. 2007).”
Tree species distributions and local habitat variation in the Amazon: large forest plot in eastern Ecuador (2004, background): “The ridge-valley difference is not surprising: catenas are fundamental in plant ecology in general and in the tropics in particular (Gartlan et al. 1986; Weaver 1991; Tuomisto & Ruokolainen 1994; Tuomisto et al. 1995; Clark et al. 1999; Svenning 1999; Webb 2000).”
Tropical tree species assemblages in topographical habitats change in time and with life stage (2011, background): “…tropical tree species typically do not form at early life stages (i.e. seed germination and seedling establishment) and that species often show different ecological habitat associations across life stages (Webb & Peart 2000; Paoli, Curran & Zak 2006; Comita, Condit & Hubbell 2007; Lai et al. 2009).”
Seed mass, seedling size and neotropical tree seedling establishment (2005, background): “reported by Welden et al. (1991). By contrast, a longerterm study (12 years) for 23 species at the Paracou site, including the eight studied here, reveals no relationship between seed mass and sapling survival (F1,22 = 0.”