Mammal assemblage structure in Amazonian flooded and unflooded forests

By T. Haugaasen, C. A. Peres. Journal of Tropical Ecology, 2005

186 citations recorded by the source corpus.

Subfields: Ecology, Paleontology, Social Psychology

View Paper: https://www.semanticscholar.org/paper/8f2c02d6fbf2f057200ad8bc56a7f8f7a74b5768

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Citations in the corpus

Hunting reduces recruitment of primate-dispersed trees in Amazonian Peru (2008, unknown): “Censuses of mammals used a standardized line-transect method (Bodmer et al., 1997; Peres, 1999; Haugaasen and Peres, 2005) have documented dramatic differences in large mammal presence in protected forests as compared with those hunted >30 years with firearms (Fig.”
Basin‐Wide Effects of Game Harvest on Vertebrate Population Densities in Amazonian Forests: Implications for Animal‐Mediated Seed Dispersal (2007, background): “…surveyed by our own standardized, long-term program (1987–2005) of line-transect censuses of forest vertebrates conducted throughout lowland Amazonia (Peres 1997, 1999b, 2000a, b, Peres & Dolman 2000, Haugaasen & Peres 2005, Palacios & Peres 2005, Peres & Nascimento 2006; C. A. Peres, pers. obs.).”
The combined influence of riverine barriers and flooding gradients on biogeographical patterns for amphibians and squamates in south‐eastern Amazonia (2016, background): “…forest ecosystems subjected to different flooding regimes (Doan & Arriaga, 2002; Pavan, 2007; Bueno et al., 2012; Schietti et al., 2013), especially in the plain sedimentary region of the Amazon basin (Wittmann et al., 2004; Haugaasen & Peres, 2005), where the riparian areas are more developed.”
An evaluation of camera traps for inventorying large‐ and medium‐sized terrestrial rainforest mammals (2008, methodology): “The methods commonly used for mammal inventories are line transects, direct observations, identification of tracks and feces, trapping and interviews with local people (Voss & Emmons, 1996; Voss, Lunde & Simmons, 2001; Trolle, 2003a; Mendes Pontes, 2004; Haugaasen & Peres, 2005).”
Priority areas for the conservation of Atlantic forest large mammals (2009, background): “Differences in floristic composition, habitat structure and soil fertility were also strong predictors of the differences in large mammal assemblage structure between Amazonian terra firme and seasonally-flooded (várzea) forests (Haugaasen and Peres, 2005).”
Phyllostomid Bat Assemblage Structure in Amazonian Flooded and Unflooded Forests (2014, background): “This is the likely cause for higher abundance and biomass of several species on the floodplains compared with terra firme (Haugaasen & Peres 2005a,b), and Pereira et al. (2009) suggest that this is also the underlying cause for higher bat abundance in v arzea forest.”
Rapid evaluation of threats to biodiversity: human footprint score and large vertebrate species responses in French Guiana (2010, background): “…extinctions of South American monkeys in relation to direct human exploitation have also been widely reported in Guyana (Lehman 2000), Venezuela (Urbani 2006), Peru and Bolivia (Freese et al. 1982), and lowland Amazonia (Lopes and Ferrari 2000; Haugaasen and Peres 2005; Peres and Palacios 2007).”
Vertebrate responses to fruit production in Amazonian flooded and unflooded forests (2007, background): “We have shown that fruit abundance in a highly heterogeneous Amazonian forest landscape varies in complex spatial and temporal patterns, and how this may affect resident frugivore populations.”
Thresholds in the relationship between functional diversity and patch size for mammals in the Brazilian Atlantic Forest (2015, background): “We can also consider that the simplified vegetation structure and floristic composition of the forest remnants cause differentiation in the composition of mammal assemblages (Haugaasen & Peres, 2005).”
Assessment of large-vertebrate species richness and relative abundance in Neotropical forest using line-transect censuses: what is the minimal effort required? (2008, background): “Although the design of the survey track is an important issue, the census walk is often restricted to a rather short section, i.e., 4–6 km repeated until a suYcient eVort is obtained, due to logistic and Weld constraints (Haugaasen and Peres 2005a).”