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      Severity of deforestation mediates biotic homogenisation in an island archipelago

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          High-resolution global maps of 21st-century forest cover change.

          Quantification of global forest change has been lacking despite the recognized importance of forest ecosystem services. In this study, Earth observation satellite data were used to map global forest loss (2.3 million square kilometers) and gain (0.8 million square kilometers) from 2000 to 2012 at a spatial resolution of 30 meters. The tropics were the only climate domain to exhibit a trend, with forest loss increasing by 2101 square kilometers per year. Brazil's well-documented reduction in deforestation was offset by increasing forest loss in Indonesia, Malaysia, Paraguay, Bolivia, Zambia, Angola, and elsewhere. Intensive forestry practiced within subtropical forests resulted in the highest rates of forest change globally. Boreal forest loss due largely to fire and forestry was second to that in the tropics in absolute and proportional terms. These results depict a globally consistent and locally relevant record of forest change.
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            iNEXT: an R package for rarefaction and extrapolation of species diversity (Hill numbers)

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              Confounding factors in the detection of species responses to habitat fragmentation.

              Habitat loss has pervasive and disruptive impacts on biodiversity in habitat remnants. The magnitude of the ecological impacts of habitat loss can be exacerbated by the spatial arrangement -- or fragmentation -- of remaining habitat. Fragmentation per se is a landscape-level phenomenon in which species that survive in habitat remnants are confronted with a modified environment of reduced area, increased isolation and novel ecological boundaries. The implications of this for individual organisms are many and varied, because species with differing life history strategies are differentially affected by habitat fragmentation. Here, we review the extensive literature on species responses to habitat fragmentation, and detail the numerous ways in which confounding factors have either masked the detection, or prevented the manifestation, of predicted fragmentation effects. Large numbers of empirical studies continue to document changes in species richness with decreasing habitat area, with positive, negative and no relationships regularly reported. The debate surrounding such widely contrasting results is beginning to be resolved by findings that the expected positive species-area relationship can be masked by matrix-derived spatial subsidies of resources to fragment-dwelling species and by the invasion of matrix-dwelling species into habitat edges. Significant advances have been made recently in our understanding of how species interactions are altered at habitat edges as a result of these changes. Interestingly, changes in biotic and abiotic parameters at edges also make ecological processes more variable than in habitat interiors. Individuals are more likely to encounter habitat edges in fragments with convoluted shapes, leading to increased turnover and variability in population size than in fragments that are compact in shape. Habitat isolation in both space and time disrupts species distribution patterns, with consequent effects on metapopulation dynamics and the genetic structure of fragment-dwelling populations. Again, the matrix habitat is a strong determinant of fragmentation effects within remnants because of its role in regulating dispersal and dispersal-related mortality, the provision of spatial subsidies and the potential mediation of edge-related microclimatic gradients. We show that confounding factors can mask many fragmentation effects. For instance, there are multiple ways in which species traits like trophic level, dispersal ability and degree of habitat specialisation influence species-level responses. The temporal scale of investigation may have a strong influence on the results of a study, with short-term crowding effects eventually giving way to long-term extinction debts. Moreover, many fragmentation effects like changes in genetic, morphological or behavioural traits of species require time to appear. By contrast, synergistic interactions of fragmentation with climate change, human-altered disturbance regimes, species interactions and other drivers of population decline may magnify the impacts of fragmentation. To conclude, we emphasise that anthropogenic fragmentation is a recent phenomenon in evolutionary time and suggest that the final, long-term impacts of habitat fragmentation may not yet have shown themselves.
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                Author and article information

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                Journal
                Ecography
                Ecography
                Wiley
                0906-7590
                1600-0587
                July 2022
                May 18 2022
                July 2022
                : 2022
                : 7
                Affiliations
                [1 ]Durrell Inst. of Conservation and Ecology (DICE), School of Anthropology and Conservation, Univ. of Kent Canterbury UK
                [2 ]Dept of Animal and Plant Sciences, Univ. of Sheffield Sheffield UK
                [3 ]Birdlife International, David Attenborough Building Cambridge UK
                [4 ]Dept of Forest Management, Univ. Pattimura Ambon Indonesia
                [5 ]Univ. Halu Oleo Southeast Sulawesi Indonesia
                [6 ]Birdpacker Pakembinangun Yogyakarta Indonesia
                [7 ]Jakartabirder Jakarta Indonesia
                [8 ]Dept of Forest Sciences, Univ. Sam Ratulangi Manado North Sulawesi Indonesia
                [9 ]Dept of Biology, Faculty of Mathematics and Natural Sciences, Univ. Negeri Gorontalo Gorontalo Indonesia
                [10 ]Operation Wallacea, Old Bolingbroke Lincolnshire UK
                [11 ]Dept of Biology, Faculty of Mathematics and Natural Sciences Depok Indonesia
                [12 ]Research Center for Climate Change, Univ. Indonesia Depok Indonesia
                Article
                10.1111/ecog.05990
                b491e51c-40aa-435d-96fe-001cbf31b339
                © 2022

                http://creativecommons.org/licenses/by/3.0/

                http://doi.wiley.com/10.1002/tdm_license_1.1

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