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Insects are threatened from the drivers of global habitat loss and fragamentation.
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Insect diversity and conservation have been overlooked across conservation programs.
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Poor taxonomy and sampling biases restrict the understanding of diversity patterns.
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Erebidae moths are underrepresented across conservation polygons of southern Mexico.
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Protected areas are not effectively at preserving hyperdiverse groups.
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The global road network is rapidly growing.
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Population-level studies represent a minority on road ecology.
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Most of them focused large mammals from high-income countries.
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More research on threatened species from developing countries is need.
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Long-term (>4.2 years) contamination and ecological risks of the Rio Doce estuary.
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Sediment metal(loid)s concentrations support a continued potential adverse biological effect.
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Despite a decrease in metal(loid)s concentration, the chronic contamination is still above reference values.
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The Rio Doce estuary works as a sink for tailings and a source of toxic metal(loid)s.
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Environmental diversity efficiently represents marine mammal diversity.
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Environmental diversity is an effective abiotic surrogate for biodiversity conservation.
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Environmental variables can be effectively used in marine biodiversity conservation.
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Detection method information is absent in 38% of deer records in protected areas.
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Most of the records (60%) used unsuitable methods for deer species identification.
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Forest deer species are the most impacted regarding unreliable identification.
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Greater scientific rigor on data acquisition is necessary for conservation planning.
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Review of peer-reviewed literature on biodiversity conservation in insular Caribbean between 2000 and 2015.
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On a per year base, Caribbean-based authors found in 32% of papers, accounted for 22% of lead paper authorships, represented 17% of authors per paper.
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No evidence of improvement in the above metrics over time.
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Marked differences in paper contributions among Caribbean locations, with evidence of low intra-regional collaboration.
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The expansion of bat habitat generalists coupled with range contraction of bat habitat specialist will homogenize the Neotropical bat communities.
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Warm-adapted bat species might expand their ranges towards higher altitudes, while mountain-top specialists will run out of suitable climate.
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Monitoring programs will be important to track species that are predicted to become extinct and also the projected range expansion of sanguivorous bats.
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The most effective way to protect Neotropical bat species will be increasing landscape connectivity and safeguarding the refugia highlighted here.
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Ryegrass promotion sites (through the application of herbicide glyphosate) had lower vegetation cover <10 cm than other grazing sites.
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Structure of bird communities varied among management treatments.
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Ryegrass promotion sites had a negative effect on nearctic migrants.
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Understanding ecological processes are benefitial for wildlife conservation.
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We used Maxent ecological niche modeling to quantify habitat suitability of invasive plant species (IPS).
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Functional trait context dependence could affect suitable habitat distributions of IPS across different biomes.
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We suggested to use community mean functional traits to predict suitable habitat distributions of IPS.
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Global climate and land-use changes will have a serious impact on individual species and communities of hummingbirds.
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Existing protected areas showed an important reduction of surface across the species distribution and hotspot areas for future.
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A large proportion of “safe places” does not match the areas targeted for agriculture expansion in future scenarios.
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It is imperative that policy-makers promote policies that are resilient to both threats as soon as possible.
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Pollinators not yet reported as crop pollinators could likely contribute to agriculture.
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The neglected diversity of bees as potential crop pollinators in Brazil is 88.4%.
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The proportion of vertebrate pollinators not yet recorded as pollinating crops is 95.2%.
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Many plant–pollinator interactions are off the conservation agenda for agricultural stability.
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Efforts to protect agricultural pollinators should consider even species not yet recorded as crop pollinators.
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