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Long-term monitoring of different drivers of changes increases the effectiveness of protected areas.
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Long-term Ecological Research Program helps detecting complex environmental changes.
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The effects of disturbances on biodiversity and ecosystems were explored over 22 years in the central Cerrado.
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Even in Protected Areas, changes in surroundings affect biodiversity and ecosystems.
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Significant ecological changes were detected in responses to long-term stressors.
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We reviewed the use of network science in sustainable agriculture.
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Network science can be used to understand, harness and restore ecological processes in agricultural systems.
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Social, economic and ecological aspects of agriculture can be incorporated using novel methods.
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Agricultural systems can be managed using a network-based framework.
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Neotropical governments and their environmental agencies have generally poor governance.
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Poor governance can be influencing human-top predator conflicts in the Neotropics.
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Forty percent of interviewees disapproved the current top-down local management.
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Disapproval of top-down local management influenced human tolerance independently.
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Neotropics need a better balance between bottom-up and top-down governance.
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Bird color diversity increased during the breeding season.
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The standardized effect size of bird color diversity did not change between seasons.
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Urban areas presented the lowest color diversity along the year.
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Bird color composition was stable between seasons in urban areas.
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9847 wasps classified into 75 species and 23 genera were recorded.
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Inter-habitat dissimilarity decreased with increasing forest cover in the landscape.
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Landscape diversity, edge density, and pesticide usage did not affect spillover.
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Forested landscapes provide more spillover opportunities than do crop landscapes.
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Anthropization drives directional changes on functional traits of bird communities of Neotropical seasonal forests.
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Birds within anthropized habitat have short life cycles, rapid development, high fecundity, and broad ecological niches.
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According to the Ecological Strategies Theory, birds could show the ruderal strategy within the perturbed anthropic habitat.
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Climate change threatens Cerrado anurans.
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∼70% of anuran species tend to lose potential distribution areas.
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Not all species are likely to be equally affected by climate change.
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Anurans’ responses to climate change are mediated by biogeographic character.
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Caatinga dry forests are becoming increasingly drier and chronically disturbed.
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Herb communities negatively respond to rainfall reduction and increase disturbance.
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Responses may be mediated by the local density of woody plants.
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Multiple successional pathways should emerge with the new environmental conditions.
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Management and conservation actions are urgent to protect Caatinga herb diversity.
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Agriculture-frontier classification allows organizing social-ecological processes.
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Forest exploitation and real-estate transactions are daily drivers in the early stages.
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Global agribusiness and livestock are drivers dominating the advanced stages.
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Only crop replacement takes place during mature frontier stages.
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Extra-regional people and governments are mentioned as the responsible social actors.
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Simulations show that neutral processes and reduced dispersal across rivers can maintain two species in allopatry for many generations.
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Reduced dispersal maintained allopatry despite repeated river crossings allowing rivers to act as effective secondary barriers.
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Neutral processes across contact zones provide a potential mechanism for the maintenance of Amazonian biodiversity.
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More understanding of the dispersal characteristics of organisms and factors that limit river crossing are needed to make predictions about the role of rivers in maintaining Amazonian biodiversity.
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The tropical montane cloud forests (TMCF) in Ecuador are endangered ecosystems that may be affected by climate change.
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Community – level ecological niche models are useful to reconstruct TMCF boundaries to guide conservation strategies.
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By year 2050, 42 -54 % TMCF area reduction and 207 – 429 m upwards elevational shift was predicted by our models.
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TMCF model corresponds to 68% of the Ecuadorian ecosystem map, with transitional zones on adjacent montane ecosystems.
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TMCF under protected areas might increase in future scenarios, as climatic suitability areas will move to higher elevations.
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The abundance-suitability relationship differs between protected and unprotected populations of Euterpe edulis.
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The magnitude and direction of the relationship is modulated by population density.
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The abundance-suitability relationship is positive only outside protected areas and in low-density populations.
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Protection status and density-dependence should be incorporated into abundance-suitability models of threatened species.
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There is no evidence of genetic population structure in Ashy red colobus monkeys inhabiting a highly fragmented landscape.
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A “stepping stone” model could maintain connectivity between the main forest and the fragments improving the viability of red colobus populations.
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Forest stepping stones can be established through restoration efforts of non-arable areas between fragments and the park.
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A community-based forest restoration effort can benefit multiple stakeholders and increase the conservation value of forest fragments.
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