Anthropogenic determinants of primate and carnivore local extinctions in a fragmented forest landscape of southern Amazonia

By F. Michalski, C. A. Peres. 2005

393 citations recorded by the source corpus.

Subfields: Ecology, Nature and Landscape Conservation, Social Psychology

View Paper: https://www.semanticscholar.org/paper/02d15cbac468fdee82e75df3014945849e74a4f9

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Citations in the corpus

Matrix is important for mammals in landscapes with small amounts of native forest habitat (2011, background): “forest patches can have a greater impact on small habitat patches (Fox and Fox 2000) and can even result in more detrimental effects than patch size (Michalski and Peres 2005).”
Assessing Habitat Fragmentation Effects on Primates: The Importance of Evaluating Questions at the Correct Scale (2013, background): “%) compared forest fragments with 1 (12 papers; for example, Chapman et al. 2007 ; Dausmann et al. 2008 ) to 15 (Michalski and Peres 2005 ) continuous forests (Fig.”
Avian life‐history determinants of local extinction risk in a hyper‐fragmented neotropical forest landscape (2008, background): “1), lies in the southern Amazonian ‘Arc of Deforestation’ and is an ideal model landscape in which to study the effects of habitat fragmentation and perturbation (Michalski & Peres, 2005).”
Habitat patch size modulates terrestrial mammal activity patterns in Amazonian forest fragments (2010, background): “…hypothesis is supported by habitat surveys in the same patches showing that older sites have a higher density of small-seeded softwood trees (Michalski et al. 2007), which provide a poorer quality and quantity of the seeds and fruits that the agoutis depend on (Jorge and Peres 2005; Smythe 1978).”
High mammal species turnover in forest patches immersed in biofuel plantations (2017, background): “This indicates that each landscape presents a fairly distinct subset of species, although agroecosystems typically retain a non-random set of species that often replaces core forest habitat and dietary specialists (Michalski and Peres, 2005; Lyra-Jorge et al., 2010).”
Disturbance‐Mediated Drift in Tree Functional Groups in Amazonian Forest Fragments (2007, background): “Five of the 21 forest patches surveyed were not completely isolated, so to calculate their metrics, we artificially eroded the narrowest, most disturbed forest cover connections (mean width ± SE = 55.6 ± 8.2 m, N = 12), following Michalski and Peres (2005).”
Rapid avifaunal collapse along the Amazonian deforestation frontier (2006, methodology): “Subsequently the region has experienced extremely high deforestation rates: by 2003 only 37% of the pre-frontier forest cover remained in the Alta Floresta region south of the Teles Pires river (Michalski and Peres, 2005).”
Predicting local extinctions of Amazonian vertebrates in forest islands created by a mega dam (2015, background): “In contrast to other Neotropical fragmentation ecology studies in terrestrial landscapes (Estrada et al., 1994; Michalski and Peres, 2005; Sampaio et al., 2010; Thornton et al., 2011a; Canale et al., 2012), we detected an overall greater habitat area effect on local extinctions of mid- to large-size”
Impacts of rain forest fragmentation on butterflies in northern Borneo: species richness, turnover and the value of small fragments (2006, background): “Such habitat disturbance may have populationand community-level effects beyond the influences of patch area and isolation ( Michalski & Peres 2005; Ewers & Didham 2006) but there are insufficient data to address this question.”
Anthropogenic modulators of species–area relationships in Neotropical primates: a continental‐scale analysis of fragmented forest landscapes (2013, methodology): “We also searched and included the study bibliographies, unpublished studies we were aware of, and our own data from three fragmented landscapes (Michalski & Peres, 2005; Benchimol, 2009; Canale et al., 2012).”