Article

Landscape matrix and species traits mediate responses of Neotropical resident birds to forest fragmentation in Jamaica

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Abstract

Land cover and land use surrounding fragmented habitat can greatly impact species persistence by altering resource availability, edge effects, or the movement of individuals throughout a landscape. Despite the potential importance of the landscape matrix, ecologists still have limited understanding of the relative effects of different types of land cover and land uses on species patterns and processes in natural systems. Here we investigated whether Neotropical resident bird communities in limestone forest patches differed if they were embedded in three different human-dominated matrix types (agriculture, peri-urban development, and bauxite mining) relative to sites in continuous forest in central Jamaica. We found that species richness, community composition, and abundances were matrix-dependent, with agricultural landscapes supporting greater avian diversity and more intact community assemblages than either peri-urban or bauxite landscapes. Abundance of almost 70% of species differed in forest embedded in the different landscape matrix types. Traits related to resource use best predicted species responses, including diet guild, nest height, habitat association, and foraging strata. Insectivores, frugivores, canopy nesters, understory and canopy foragers, and forest-restricted species rarely observed in matrix habitats had lower abundances in forest fragments embedded in human-dominated matrix types than in continuous forest. In contrast, nectarivores, omnivores, granivores, ground and multi-strata nesters, ground foragers, and species regularly in matrix habitats were least sensitive to forest fragmentation. Results suggest that structure, composition, and land use disturbance regimes in matrix areas impact overall habitat quality in landscapes by potentially mediating resource availability inside as well as outside forest habitat. This study reinforces the importance of differentiating among land cover and land uses in fragmentation research and lends support to the hypothesis that resource availability may be a primary factor driving Neotropical bird responses to fragmentation.

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... Urbanization is a major driver of habitat fragmentation (Marzluff and Ewing, 2001), and the importance of matrix composition surrounding habitat fragments has recently been emphasized for the persistence of biodiversity in fragments (Kupfer et al., 2006;Prugh et al., 2008;Franklin and Lindenmayer, 2009). As the surrounding matrix becomes less hospitable, habitat fragments suffer a loss of biodiversity and an increased risk of local extinction (Kennedy et al., 2010;Kennedy et al., 2011). Multiple studies have found that forest fragments in urban landscapes have less biodiversity than forest fragments in rural landscapes (Rodewald and Bakermans, 2006;Miller et al., 2003). ...
... Studies that focused on the direct impacts of urbanization on the matrix found that smaller fragments had lower avian conservation value (Donnelly and Marzluff, 2004;Rodewald and Bakermans, 2006;Mason et al., 2007;Callaghan et al., 2018;Shoffner et al., 2018;Plummer et al., 2020). Studies also found that the avian conservation value of fragments declined as urbanization intensity in the matrix increased (Miller et al., 2003;Donnelly and Marzluff, 2004;Dunford and Freemark, 2005;Rodewald and Bakermans, 2006;De Wan et al., 2009;Kennedy et al., 2010;Kennedy et al., 2011;Pennington and Blair, 2011;Shoffner et al., 2018). The second group of hypotheses explaining the loss of avian diversity from urban fragments attribute declines in urban avoiders to the indirect impacts of nearby urbanization on wildlife living within those fragments, such as noise pollution, light pollution, and invasive species. ...
... Because we were able to untangle urbanization intensity from stressors like anthropogenic noise or invasive species, we were able to treat urbanization intensity as a direct impact of an urbanizing matrix. In other words, we can attribute negative associations between urbanization intensity in the nearby matrix and occupancy to the inability of those species to use an urbanized matrix, and the loss of resources and space associated with this consequence (Kupfer et al., 2006;Kennedy et al., 2010). Total Inclusions 17 17 17 17 17 7 10 10 9 4 9 11 8 8 ...
Article
Urbanization dramatically modifies natural landscapes, fragments previously intact habitats, and is spreading rapidly, making it one of the leading causes of worldwide biodiversity decline. We studied the impact of urbanization on the occupancy of breeding birds in the Great Trinity Forest in Dallas, TX, the largest urban forest in the United States. The matrix of habitat surrounding the Great Trinity Forest varies from highly urbanized industrial landscapes to more rural areas. Between May 15th and July 15th of 2018, 2019, and 2020 we surveyed 404 5-ha plots for forest birds, recording 4274 observations representing 49 species. We used time-to-detection to model avian occupancy in 17 species while accounting for false absences. We found that the avian community responded to anthropogenic impacts of urbanization in the matrix in diverse ways. Urbanization intensity had the largest negative impact on avian occupancy and best explained observed patterns of urban avoidance from previous studies. Occupancy of species with low vocal frequency was negatively impacted by continuous anthropogenic noise from automobile traffic, while a broader group of species was negatively impacted by intermittent noise from airplane traffic. Occupancy exhibited both positive and negative responses to increased feral hog activity. To maintain diverse bird communities in forest fragments with a heavily urbanized matrix, it may be necessary to maintain large habitat tracts and mitigate for the indirect effects of the matrix like noise and invasive species.
... As expected, the proportion of old forest within the reserves was the main factor in explaining the bird community composition. However, in contrast to results from earlier studies (Devictor, Julliard, Clavel, et al., 2008;Kennedy, Marra, Fagan, & Neel, 2010;Stouffer, Strong, & Naka, 2009), our results showed only moderate responses of bird communities to the quality of the matrix. Furthermore, the responses of bird communities were not stronger in small reserves. ...
... were on average larger than in the precedent studies (our study units were 34 km 2 on average, whereas used 4 km 2 study units and Kennedy et al. (2010) worked on 1 km 2 study units). Thus, our results suggest that larger high-quality areas might be better buffered against the matrix effects (Carroll et al., 2004). ...
... Other plausible explanation is that the quality of the matrix in Finnish northern forest reserves is not contrasting enough. In studies in which strong matrix effects were found (Kennedy et al., 2010;McKinney, 2006), the difference in the habitat quality between the focal areas and the matrix was greater (native vs. urban habitats) than in our study. In our case, the lowest matrix quality belonged to recently logged forests, which basically represent forests in the very early successional stage. ...
Article
Full-text available
Protected areas are meant to preserve native local communities within their boundaries, but they are not independent from their surroundings. Impoverished habitat quality in the matrix might influence the species composition within the protected areas through biotic homogenization. The aim of this study was to determine the impacts of matrix quality on species richness and trait composition of bird communities from the Finnish reserve area network and whether the communities are being subject of biotic homogenization due to the lowered quality of the landscape matrix. We used joint species distribution modeling to study how characteristics of the Finnish forest reserves and the quality of their surrounding matrix alter species and trait compositions of forest birds. The proportion of old forest within the reserves was the main factor in explaining the bird community composition, and the bird communities within the reserves did not strongly depend on the quality of the matrix. Yet, in line with the homogenization theory, the beta‐diversity within reserves embedded in low‐quality matrix was lower than that in high‐quality matrix, and the average abundance of regionally abundant species was higher. Influence of habitat quality on bird community composition was largely explained by the species' functional traits. Most importantly, the community specialization index was low, and average body size was high in areas with low proportion of old forest. We conclude that for conserving local bird communities in northern Finnish protected forests, it is currently more important to improve or maintain habitat quality within the reserves than in the surrounding matrix. Nevertheless, we found signals of bird community homogenization, and thus, activities that decrease the quality of the matrix are a threat for bird communities.
... Urbanization is a major source of habitat fragmentation (Marzluff & Ewing, 2001), and forest fragments surrounded by an urban matrix have less biodiversity than forest fragments in rural landscapes (Miller et al., 2003;Rodewald & Bakermans, 2006). As the surrounding matrix becomes less hospitable, habitat fragments suffer a loss of biodiversity and an increased risk of local extinction (Kennedy et al., 2010;Kennedy et al., 2011). Species that avoid the matrix around a habitat fragment tend to decline or disappear as the matrix urbanizes, while those that tolerate or exploit the matrix often remain stable or increase in abundance (Gascon et al., 1999). ...
... The amount of impervious surface in a landscape is often used as a surrogate for the intensity of urbanization (e.g., Evans et al., 2015;Rodewald et al., 2013). As urbanization in the matrix surrounding habitat fragments intensifies, these fragments often suffer a loss of biodiversity and an increase in the risk of local extinction (Kennedy et al., 2010;Kennedy et al., 2011). We measured the amount of impervious surface in and around the GTF using ArcGIS Pro's image classification wizard. ...
Article
Full-text available
Conservation of habitat fragments, including those embedded in an urban matrix which typically support fewer species than those in other landscape contexts, is important for combatting the global extinction crisis. Because urban avoiding species are often absent from habitat fragments within an urban matrix, studies of their distributions in these habitats are rare, and therefore the mechanisms by which species are excluded from habitat fragments within an urban matrix are poorly understood. We investigated the impacts of urbanization in the matrix (e.g., noise pollution, light pollution, invasive species) on the distribution of an urban avoiding species, the swamp rabbit (Sylvilagus aquaticus) in the largest urban forest fragment in the United States. We used the location of swamp rabbit latrines and presence‐background species distribution modeling to reveal the impacts of urbanization in the matrix on swamp rabbit distribution while accounting for spatial heterogeneity in naturally occurring environmental variables. Swamp rabbits used mature forest, heterogeneously structured forest, and moderately inundated forest, and they avoided areas of high (Sus scrofa) hog activity at our study site. Our findings provide novel information to conservation practitioners and urban planners attempting to conserve high priority species in habitat fragments as urbanization continues to spread. Feral hog activity, vegetation structure, vegetation composition, and flooding frequency drive swamp rabbit (Sylvilagus aquaticus) distribution in a large urban forest. Swamp rabbits avoid area of high feral hog (Sus scrofa) activity but are not impacted by anthropogenic noise or urbanization intensity in the nearby matrix.
... Habitat quality models that relate the occurrence of bird assemblies with the characteristics of the occupied habitat have been frequently referenced in the literature (KENNEDY et al., 2011). Such models are influenced by the spatial scale that is used which includes not only the hierarchical structure or interdependence of the different environmental variables that are considered, but also the hierarchical responses or interdependence of the birds towards the habitat they are occupying (SMITH et al., 2011;KENNEDY et al., 2010). However, there are still information gaps related mainly to the predictive capacity of the models when trying to associate particular species of birds with particular types of occupied habitats at different spatial scales (KENNEDY et al., 2010). ...
... Such models are influenced by the spatial scale that is used which includes not only the hierarchical structure or interdependence of the different environmental variables that are considered, but also the hierarchical responses or interdependence of the birds towards the habitat they are occupying (SMITH et al., 2011;KENNEDY et al., 2010). However, there are still information gaps related mainly to the predictive capacity of the models when trying to associate particular species of birds with particular types of occupied habitats at different spatial scales (KENNEDY et al., 2010). ...
Article
Full-text available
The degradation of the Llanos foothill ecosystems is one of the biggest ecological problems in the areas surrounding the city of Villavicencio, Meta. The generation of fragments produces new conditions for the establishment of bird guilds. This study was carried out during 2017 - 2018 in areas of the campus Loma Linda at the Santo Tomas University. It was evaluated whether the forest interior, forest border and grassland areas constitute habitats that support the establishment of frugivorous birds. The key factors that affect the richness, diversity and abundance of bird species were identified, from which recommendations were made for the establishment of conservation measures. The richness of birds and their abundance was positively correlated with intermediate values of plant richness and diversity and with the presence and coverage of species of palms and lianas. The abundance and diversity of frugivorous birds were higher in border areas and lower in grasslands and forest interiors. Apparently the diversity of the habitat in border areas of fragmented lands increases the diversity of frugivorous birds through an increase in the abundance values. Artificial enrichment is recommended with different tree, shrubs and palms species planted in the edge and interior areas of the forest, and the maintenance of remaining trees and shrubs in the areas of shrub grasslands. Keywords : fragmentation, frugivorous-birds, diversity, natural regeneration.
... This method allows for the use of the Bray-Curtis dissimilarity calculation, which is ideal when it comes to species abundances as, for example, it is robust to the many zeros involved with count data. I used a Bray-Curtis dissimilarity matrix and excluded species occurring in less than 5% of samples (Kennedy et al. 2010). I used the axis ordination score of each study plot from the axis that explained the greatest percent of variation as the data values for the canopy composition of each plot. ...
... In all avian analysis, I included only species that are known to breed in the study area (eBird 2019, To visually explore the avian community structure in plots invaded by and removed of honeysuckle, I used an NMDS ordination with the Bray-Curtis distance index as the distance measure. I only included avian species that occurred in more than 5% of samples (Kennedy et al. 2010). I combined certain species together to account for potential misidentifications: Carolina chickadee with tufted titmouse, European starling with brown-headed cowbird, and all woodpecker species. ...
Thesis
Amur honeysuckle (Lonicera maackii) was introduced to North America in the late 1880s and has since become highly invasive throughout the midwestern and northeastern United States. Amur honeysuckle-dominated habitat can be detrimental to wildlife including birds. The invasive shrub attracts generalist avian species and represents an ecological trap where manipulative habitat signals have been shown to negatively influence avian populations. Due to its detrimental effects on ecosystems, managers have invested substantial effort towards removing the shrub. Albeit many studies have explored the negative effects that Amur honeysuckle has on avian species, there is a lack of research that identifies how removing the shrub impacts birds, especially in rural areas. In order to help optimize management strategies in this regard and better understand how removing this shrub influences birds, I investigated how Amur honeysuckle removal in rural riparian forests affects the composition of avian assemblages. To accomplish this, I identified plots along the Little Miami River in Greene County, Ohio that are either invaded by or removed of Amur honeysuckle. During the 2019 peak breeding season, I performed avian point counts in order to survey avian assemblages and collected vegetation data in order to measure Amur honeysuckle prevalence and differences in habitat structure and composition among plots. I used a non-metric multidimensional scaling ordination and analysis of similarity to explore differences in avian community structure between plot types and determine whether a community difference existed. I used N-mixture and generalized linear models to explore the impact of removal on avian abundances and species richness and diversity respectively. I found that avian community composition was different between plots removed of Amur honeysuckle and plots invaded by Amur honeysuckle. The variation in avian community structure was explained, in part, by Amur honeysuckle removal. Avian species were overall more abundant in removed plots. Greater abundances of woodpeckers and species that prefer open woodlands were found in plots removed of Amur honeysuckle vs. plots invaded by Amur honeysuckle. While Amur honeysuckle removal had a positive effect on the Acadian flycatcher (Empidonax virescens), other species, i.e., the American robin (Turdus migratorius), blue-gray gnatcatcher (Polioptila caerulea), Carolina wren (Thryothorus ludovicianus), indigo bunting (Passerina cyanea), northern cardinal (Cardinalis cardinalis), northern parula (Setophaga americana), combined tufted titmouse (Baeolophus bicolor) and Carolina chickadee (Poecile carolinensis), and red-eyed vireo (Vireo olivaceus), were unaffected. Avian species diversity and richness appeared to be greater in areas removed vs. invaded by Amur honeysuckle. These findings provide insight to land managers in southwest Ohio regarding how the removal of Amur honeysuckle in rural riparian forests impacts avian community composition. Permalink: http://rave.ohiolink.edu/etdc/view?acc_num=osu1598006298750454
... Collectively, this means that islands and mainland areas will converge in their SARs at lower levels of landscape 'islandness'. Moreover, matrix type (Kennedy et al. 2010), history of disturbance (e.g. clear-cut or burned forests; Stouffer and Bierregaard 1995), time since habitat patch isolation (Jones et al. 2016), and direct human disturbance (e.g. ...
... Many factors could account for such a variation in significance and model parameters (fit and slope). For example, the patch:matrix contrast (Kennedy et al. 2010), disturbance severity (Stouffer and Bierregaard 1995), relaxation time (Robinson 1999) and accessibility for hunters (Canale et al. 2012) can all affect the number of species in habitat patches, thereby modulating ISARs. Furthermore, the influx of matrix-derived species into habitat patches may either attenuate (Matthews et al. 2014) or even reverse (Lövei et al. 2006) the estimated impact of patch size on species richness. ...
Article
Full-text available
We investigated 1) the role of area per se in explaining anuran species richness on reservoir forest islands, after controlling for several confounding factors. We also assessed 2) how sampling design affects the inferential power of island species–area relationships (ISARs) aiming to 3) provide guidelines to yield reliable estimates of area‐induced species losses in patchy systems. We surveyed anurans with autonomous recording units at 151 plots located on 74 islands and four continuous forest sites at the Balbina Hydroelectric Reservoir landscape, central Brazilian Amazonia. We applied semi‐log ISAR models to assess the effect of sampling design on the fit and slope of species–area curves. To do so, we subsampled our surveyed islands following both a 1) stratified and 2) non‐stratified random selection of 5, 10, 15, 20 and 25 islands covering 1) the full range in island size (0.45–1699 ha) and 2) only islands smaller than 100 ha, respectively. We also compiled 25 datasets from the literature to assess the generality of our findings. Island size explained ca half of the variation in species richness. The fit and slope of species–area curves were affected mainly by the range in island size considered, and to a very small extent by the number of islands surveyed. In our literature review, all datasets covering a range of patch sizes larger than 300 ha yielded a positive ISAR, whereas the number of patches alone did not affect the detection of ISARs. We conclude that 1) area per se plays a major role in explaining anuran species richness on forest islands within an Amazonian anthropogenic archipelago; 2) the inferential power of island species–area relationships is severely degraded by sub‐optimal sampling designs; 3) at least 10 habitat patches spanning three orders of magnitude in size should be surveyed to yield reliable species–area estimates in patchy systems.
... Abrupt habitat edges can have a variety of negative and positive influences (edge effects) on wildlife populations, community dynamics, and ecological processes (e.g., Laurance and Yensen, 1991;Murcia, 1995). The direction and strength of edge effects appear dependent on factors that function at multiple spatial scales, including species attributes (Heske, 1995;Kennedy et al., 2010), competition and predation (Lima and Dill, 1990), patch composition and structure (Anderson et al., 2003;Villasenor et al., 2015), and surrounding matrix habitat (Sisk et al., 1997). Numerous studies have evaluated the effect of habitat edges on population parameters of interest (e.g., population density or predation risk) by comparing patch interior habitat to patch edge habitat to ascertain differences (positive or negative) associated with edge habitats (e.g., Wolf and Batzli, 2002;Marcello et al., 2007;Klein and Guy, 2012). ...
... Although informative this approach often does not involve sampling the surrounding matrix and therefore ignores the possible effect of matrix habitat on patch-dependent organisms. The omission of surrounding matrix habitat from sampling designs may inaccurately portray the influence of habitat edges on population dynamics (Ricketts, 2001;Kennedy et al., 2010;Prevedello and Vieira, 2010), particularly for generalist species known to utilize matrix resources. ...
Article
The influence of forest fragmentation and associated habitat edges differentially affects forest-dependent organisms, particularly when certain species are able to use resources from surrounding matrix habitats. The white-footed mouse is a forest habitat generalist and is known to disperse among adjoining farmland habitats, including agricultural matrix, in fragmented agro-ecosystems. However, little is known about spatial variation in population density within adjoining farmland habitats or how this relationship varies seasonally. In addition quantifying the extent to which white-footed mice use agricultural matrix as habitat is important for inferring potential ecosystem services (predation of weed seed and waste grain) rendered within row-crop fields. We used spatially explicit capture-recapture models to estimate density of white-footed mice along a gradient of patch (forest fragment) interior to matrix (crop field) interior that spanned fragmented habitat edges. Spatial variation in population density within adjoining habitats was related to the distance from habitat edge, and the magnitude of this relationship (edge effect) varied among seasons and crop cycles within the agricultural matrix. Within-field densities were greater during periods of summer crop growth relative to spring crop emergence or following fall crop harvest. Populations of white-footed mice in forest fragments appear to seasonally spill over from patch habitat into surrounding agricultural matrix. Acquisition of resources from surrounding agricultural matrix may contribute to the inverse density-area relationship observed for white-footed mice within forested habitat in fragmented landscapes. Furthermore, seasonal foraging within matrix habitat likely provides weed seed predation ecosystem services in row-crop fields.
... We identified several patterns that agree with those reported in the previous global and regional literature reviews: (i) species richness increases with vegetation structure and complexity (e.g., Cardozo et al. 2008;Leveau 2013;, greenspace patch size (e.g., Garitano-Zavala and Gismondi 2003;Suarez-Rubio and Thomlinson 2009;dos Santos and Cademartori 2010;, and environmental heterogeneity (e.g., Silva and Blamires 2007;Navarro et al. 2011;González-Oreja et al. 2012a, b); (ii) species richness decreases with human activity (e.g., pedestrians, vehicle traffic; Heil et al. 2007;González-Oreja et al. 2012a;) and urban infrastructure (e.g., buildings, streets, squares; Carbó-Ramírez and Zuria 2011; MacGregor-Fors and Schondube 2011; ; and (iii) insectivorous birds are successful in urban areas (Germain et al. 2008;Fernández et al. 2009;Maragliano et al. 2009;Bispo and Scherer-Neto 2010;Brummelhaus et al. 2012), as well as generalist and exotic species (Garaffa et al. 2009;Presti and Echevarria 2009;Athiê and Dias 2010;. As pinpointed in the global literature reviews, recent studies developed in Latin America have been carried out in specific urban locations (e.g., parks, university campuses; Lopes and dos Anjos 2006;Muñoz et al. 2007;González-Oreja et al. 2012b;Charre et al. 2013), along urbanization gradients (Garaffa et al. 2009;Juri and Chani 2009;Villegas and Garitano-Zavala 2010;Leveau et al. 2015), and comparing urban versus nonurban sites (e.g., agriculture, native ecosystems; Rodríguez-Estrella 2007; Kennedy et al. 2010;Dario and De Vincenzo 2011;. Multiple Latin American studies have also included water bodies and wetlands either within or near urban locations, underlining their importance as habitats for many bird species Silva and Blamires 2007;Molina et al. 2012;. ...
... Most studies (71%) comparing bird numbers among sites with different urbanization intensities were located within the urban matrix (Varela-Contador 2003; MacGregor-Fors et al. 2010a;Silva et al. 2016); yet, others were conducted in urban greenspaces (Toledo 2007;Suarez-Rubio and Thomlinson 2009;González-Oreja et al. 2012). Fewer studies compared bird abundances among urbanization intensity scenarios, for instance: (i) between urban greenspaces and nonurban areas Kennedy et al. 2010;); (ii) at increasing distances from urban settlements (Thornton et al. 2012; Lozano and Malo 2013); (iii) and in urban wetlands (Villaneda-Rey and Rosselli 2011; . Although most of the studies were performed in a single urban area, a couple of studies were conducted in three or more cities (Thornton et al. 2012;Campbell 2014). ...
Book
This book gathers a representative sample of the relevant knowledge related to the ecology, behavior, and conservation of birds in urban Latin America. Latin America is one of the most biodiverse regions of the world, yet it is still understudied. Although it concentrates most of its population in rapidly growing cities under considerable economic, social, and environmental disparity, the study of the effects that urbanization has on biodiversity in Latin America is still insufficient. Among the best-studied wildlife groups, birds have been widely used as bioindicators in urban areas. Going from general to specific information regarding avian communities, populations, behavior, threats, and conservation issues, this book describes the state-of-the-art of avian urban ecology in the region. Such knowledge will hopefully promote the regional consolidation of the field and encourage future mechanistic studies that untangle the recorded patterns in order to have the required information to bridge the gap between evidence-based knowledge and practice in urban systems. Thus, the information included in this document will allow scientists, students, and even decision takers to relate with the current knowledge and gaps related to the topic, providing perspective for future studies and actions.
... We identified several patterns that agree with those reported in the previous global and regional literature reviews: (i) species richness increases with vegetation structure and complexity (e.g., Cardozo et al. 2008;Leveau 2013;, greenspace patch size (e.g., Garitano-Zavala and Gismondi 2003;Suarez-Rubio and Thomlinson 2009;dos Santos and Cademartori 2010;, and environmental heterogeneity (e.g., Silva and Blamires 2007;Navarro et al. 2011;González-Oreja et al. 2012a, b); (ii) species richness decreases with human activity (e.g., pedestrians, vehicle traffic; Heil et al. 2007;González-Oreja et al. 2012a;) and urban infrastructure (e.g., buildings, streets, squares; Carbó-Ramírez and Zuria 2011; MacGregor-Fors and Schondube 2011; ; and (iii) insectivorous birds are successful in urban areas (Germain et al. 2008;Fernández et al. 2009;Maragliano et al. 2009;Bispo and Scherer-Neto 2010;Brummelhaus et al. 2012), as well as generalist and exotic species (Garaffa et al. 2009;Presti and Echevarria 2009;Athiê and Dias 2010;. As pinpointed in the global literature reviews, recent studies developed in Latin America have been carried out in specific urban locations (e.g., parks, university campuses; Lopes and dos Anjos 2006;Muñoz et al. 2007;González-Oreja et al. 2012b;Charre et al. 2013), along urbanization gradients (Garaffa et al. 2009;Juri and Chani 2009;Villegas and Garitano-Zavala 2010;Leveau et al. 2015), and comparing urban versus nonurban sites (e.g., agriculture, native ecosystems; Rodríguez-Estrella 2007; Kennedy et al. 2010;Dario and De Vincenzo 2011;. Multiple Latin American studies have also included water bodies and wetlands either within or near urban locations, underlining their importance as habitats for many bird species Silva and Blamires 2007;Molina et al. 2012;. ...
... Most studies (71%) comparing bird numbers among sites with different urbanization intensities were located within the urban matrix (Varela-Contador 2003; MacGregor-Fors et al. 2010a;Silva et al. 2016); yet, others were conducted in urban greenspaces (Toledo 2007;Suarez-Rubio and Thomlinson 2009;González-Oreja et al. 2012). Fewer studies compared bird abundances among urbanization intensity scenarios, for instance: (i) between urban greenspaces and nonurban areas Kennedy et al. 2010;); (ii) at increasing distances from urban settlements (Thornton et al. 2012; Lozano and Malo 2013); (iii) and in urban wetlands (Villaneda-Rey and Rosselli 2011; . Although most of the studies were performed in a single urban area, a couple of studies were conducted in three or more cities (Thornton et al. 2012;Campbell 2014). ...
Chapter
Among human activities, urbanization represents one of the most worrisome for biodiversity due to the intensity and long-term effects in the place where a city develops, as well as their indirect effect in its area of influence. Birds are one of the most studied groups to assess the impacts that urbanization has on biodiversity, but there is a lag in the knowledge of highly biodiverse regions like Latin America. This region is the most diverse in avian species, but at the same time is one of the most affected by poverty, social inequality, and population growth, representing a priority for studying urban bird responses to urbanization. In this chapter, we compare results of studies of urban birds in Latin American cities published in recent years with an earlier regional review. We found more than one-third of publications in the last six years than in the previous 35 years; however, there is still a bias in the knowledge toward most populated countries, while urban Central America remains understudied. Although there is a lack of information on the mechanistic processes molding urban avian communities, there are important advances in ecological topics, as novel resource use, urban noise, and urban avian diseases. We urge scientists of Latin American latitudes to join efforts in the understanding of avian communities in urban areas. Results of evidence-based studies ought to be communicated to decision-makers to generate strategies that improve urban management and planning.
... We identified several patterns that agree with those reported in the previous global and regional literature reviews: (i) species richness increases with vegetation structure and complexity (e.g., Cardozo et al. 2008;Leveau 2013;, greenspace patch size (e.g., Garitano-Zavala and Gismondi 2003;Suarez-Rubio and Thomlinson 2009;dos Santos and Cademartori 2010;, and environmental heterogeneity (e.g., Silva and Blamires 2007;Navarro et al. 2011;González-Oreja et al. 2012a, b); (ii) species richness decreases with human activity (e.g., pedestrians, vehicle traffic; Heil et al. 2007;González-Oreja et al. 2012a;) and urban infrastructure (e.g., buildings, streets, squares; Carbó-Ramírez and Zuria 2011; MacGregor-Fors and Schondube 2011; ; and (iii) insectivorous birds are successful in urban areas (Germain et al. 2008;Fernández et al. 2009;Maragliano et al. 2009;Bispo and Scherer-Neto 2010;Brummelhaus et al. 2012), as well as generalist and exotic species (Garaffa et al. 2009;Presti and Echevarria 2009;Athiê and Dias 2010;. As pinpointed in the global literature reviews, recent studies developed in Latin America have been carried out in specific urban locations (e.g., parks, university campuses; Lopes and dos Anjos 2006;Muñoz et al. 2007;González-Oreja et al. 2012b;Charre et al. 2013), along urbanization gradients (Garaffa et al. 2009;Juri and Chani 2009;Villegas and Garitano-Zavala 2010;Leveau et al. 2015), and comparing urban versus nonurban sites (e.g., agriculture, native ecosystems; Rodríguez-Estrella 2007; Kennedy et al. 2010;Dario and De Vincenzo 2011;. Multiple Latin American studies have also included water bodies and wetlands either within or near urban locations, underlining their importance as habitats for many bird species Silva and Blamires 2007;Molina et al. 2012;. ...
... Most studies (71%) comparing bird numbers among sites with different urbanization intensities were located within the urban matrix (Varela-Contador 2003; MacGregor-Fors et al. 2010a;Silva et al. 2016); yet, others were conducted in urban greenspaces (Toledo 2007;Suarez-Rubio and Thomlinson 2009;González-Oreja et al. 2012). Fewer studies compared bird abundances among urbanization intensity scenarios, for instance: (i) between urban greenspaces and nonurban areas Kennedy et al. 2010;); (ii) at increasing distances from urban settlements (Thornton et al. 2012; Lozano and Malo 2013); (iii) and in urban wetlands (Villaneda-Rey and Rosselli 2011; . Although most of the studies were performed in a single urban area, a couple of studies were conducted in three or more cities (Thornton et al. 2012;Campbell 2014). ...
Chapter
Following a massive migration toward cities, more than half of the total human population is now urban. Given the unbalanced metabolism of urban systems, urbanization has been recognized to be a major ecological driver with worrisome consequences at different spatial and temporal scales. Such an environmental issue has drawn the attention of ecologists from across the globe since the late 1990s, when urban ecology consolidated as a discipline. Although urban ecology has developed importantly in the last three decades, our comprehension of the effects of urbanization on wildlife communities is heavily biased toward developed countries, most of which are located in temperate regions. Woefully, there is a dearth of knowledge from highly biodiverse areas with increasing urbanization rates and major urban agglomerations. Latin America is not an exception, with most of its population in rapidly growing urban centers. Given that the region concentrates important biodiverse areas in a scenario of considerable economic and social disparity, understanding the effects that urbanization has on wildlife species is of special concern. Even though ecological studies performed in urban Latin America started in the 1970s, urban ecology in the region is still in the process of consolidation, with birds being the most studied group. Several ecological patterns hold in urban Latin America when contrasted with those from other regions; yet, important differences have been identified, making evident the need to understand the response of wildlife species in the region. In this book, we gathered regional experts to set the state-of-the-art of bird studies in urban Latin America. Starting with an updated review, the book transits across topics such as urban bird species richness, composition, abundance, demography, population dynamics, behavior, threats, and conservation, as well as their relationships with ‘green’ and ‘gray’ infrastructures. After reviewing the specific topics with information from across the globe, each chapter contrasts the global findings with those from Latin America, identifying knowledge gaps and research needs to suggest future directions. The gathered information sets the foundation for the study of birds in urban Latin America, hopefully promoting the consolidation of the field in the region and encouraging future mechanistic studies that untangle the recorded patterns to have the required information to bridge the gap between evidence-based knowledge and practice in urban systems.
... It is expected that abundance of conservation-related species as well as migrant bird diversity and abundance could be higher at less disturbed sites (low human activity, i.e., low bivalve culture and aquaculture) with more natural/semi-natural habitats (e.g., mudflats and wetlands) [17,[26][27][28]; but see 29,30]. Spatial distribution patterns of migratory birds are also likely related to species' traits (e.g., body mass, foraging stratum, and family) because species' traits can mediate species' responses to disturbance and determine species occurrence in a habitat by interacting with environmental characteristics of the habitats [31,32]. However, the patterns may be inconsistent between seasons, especially winter and spring/fall due to variations in species composition. ...
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Tidal flats provide critical habitat for migratory waterbird species; however, populations of migratory waterbirds have significantly declined due to tidal flat loss and degradation caused by human activities, particularly in Asia. Gochang getbol is one of tidal flats located on the southwest coast of South Korea and a center of clam production. Using bird monitoring data collected at five zones (zone1 to zone5) established across Gochang getbol and near coastal area, we examined distribution patterns of migratory bird diversity and conservation-related species along the coast of Gochang getbol. The intensity of human activity ‒ mudflat culture (mostly bivalve) and aquaculture was relatively high at zone2 and zone3, occupying > 30% of 2km circular area surrounding most sample points of these zones. Zone1 and particularly zone4 contained more natural/semi-natural habitats (less disturbed mudflats and wetlands) and zone5 had smallest mudflat than others. Shannon diversity, species richness, and abundance of migratory birds differed between zones (Anova test, P ≤ 0.02) except Shannon diversity in winter. In fall, all values were higher at zone4 than zone3 and zone5. In winter, zone1 showed greatest species richness and higher abundance than zone2, zone3, and zone5. In spring, while most differences were found between zone4 and zone5, abundance at zone4 was somewhat higher than zone2. The results from the fourth corner analysis indicated that abundance of species foraging at mudflat level was positively associated with zone1 (winter) but negatively with zone3 (fall). Sandpipers were positively associated with zone4. Abundance distribution maps of conservation-related species, created by inverse distance-weighted interpolation modeling, also showed high abundance of most conservation-related species at zone4 and 1. The findings of our study suggest the importance of natural/semi-natural habitat, and the possible link between human activity and distribution patterns of migratory birds in Gochang getbol. While we need further investigation on direct response of migratory birds to human activity, areas with low human activity with more natural/semi-natural habitat, e.g., zone4 and zone1 may be crucial for the conservation of migratory birds.
... Increases in 2D habitat heterogeneity led to assemblages comprised of proportionally more ground and understory foraging species, higher prevalence of granivore diets, aquaticassociated traits, and on average larger body mass. Granivores and ground foraging species are shown to be less sensitive to 2D habitat heterogeneity, with changes in resource availability between disturbed and non-disturbed habitats being a key driver of the observed differences in trait responses (Kennedy et al. 2010). Therefore, species foraging at higher strata and in dietary guilds other than granivorous might be more sensitive to disturbance and less represented in areas of high 2D habitat heterogeneity. ...
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Understanding how 3D habitat structure drives biodiversity patterns is key to predicting how habitat alteration and loss will affect species and community-level patterns in the future. To date, few studies have contrasted the effects of three-dimensional (3D) habitat composition with those of 3D habitat configuration on biodiversity, with existing investigations often limited to measures of taxonomic diversity (i.e., species richness). Here, we examined the influence of Light Detecting and Ranging (LiDAR)-derived 3D habitat structure–both its composition and configuration–on multiple facets of bird diversity. Specifically, we used data from the National Ecological Observatory Network (NEON) to test the associations between eleven measures of 3D habitat structure and avian species richness, functional and trait diversity, and phylogenetic diversity. We found that 3D habitat structure was the most consistent predictor of avian functional and trait diversity, with little to no effect on species richness or phylogenetic diversity. Functional diversity and individual trait characteristics were strongly associated with both 3D habitat composition and configuration, but the magnitude and the direction of the effects varied across the canopy, subcanopy, midstory, and understory vertical strata. Our findings suggest that 3D habitat structure influences avian diversity through its effects on traits. By examining the effects of multiple aspects of habitat structure on multiple facets of avian diversity, we provide a broader framework for future investigations on habitat structure. Posted on 24 May 2024 | The copyright holder is the author/funder. All rights reserved. No reuse without permission. | https://doi.org/10.22541/au.171654107.71445289/v1 | This is a preprint and has not been peer-reviewed. Data may be preliminary.
... In addition, considering that there is no standardized continuous surface representing the landscape analogous to vegetation cover classification, we tested the effectiveness of principal polar spectral indices (PPSi) (Moffiet et al., 2010) as an alternative to more traditional metrics (e.g., NDVI) to represent variation in vegetation cover under the GM. The vegetation cover type and its variation across the landscape have been related to aspects of bird ecology such as feeding, dispersal ability, behavior, reproduction, and predation probability (Bélisle et al. 2001;Barlow et al. 2007;Kennedy et al. 2010;Neuschulz et al. 2013;Carrara et al. 2015;Walter et al., 2017;Geoffroy et al., 2019). Thus, we expect that species responses to PPSi indices and greenness-based surface metrics can be interpreted in terms of habitat use preference. ...
... In addition, considering that there is no standardized continuous surface representing the landscape analogous to vegetation cover classification, we tested the effectiveness of principal polar spectral indices (PPSi) (Moffiet et al., 2010) as an alternative to more traditional metrics (e.g., NDVI) to represent variation in vegetation cover under the GM. The vegetation cover type and its variation across the landscape have been related to aspects of bird ecology such as feeding, dispersal ability, behavior, reproduction, and predation probability (Bélisle et al. 2001;Barlow et al. 2007;Kennedy et al. 2010;Neuschulz et al. 2013;Carrara et al. 2015;Walter et al., 2017;Geoffroy et al., 2019). Thus, we expect that species responses to PPSi indices and greenness-based surface metrics can be interpreted in terms of habitat use preference. ...
Article
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Context The patch-mosaic model (PMM) is the most common way to describe the landscape in ecological research. Despite this, the gradient model (GM) was proposed as a more accurate representation of the heterogeneity of landscapes; however, little has been explored on the behavior and performance of continuous variables and surface-based metrics from GM under different analytical scenarios. Objectives We address the question: which landscape metrics, patch-based or surface-based, best explain habitat occupancy patterns of six bird species with different ecological preferences? Methods We generated detection histories for six bird species in a fragmented Andean landscape from Colombia. We obtain patch-based metrics from a land cover classification and surface-based metrics from the principal polar spectral indices (PPSi) to describe the landscape. Finally, we fitted dynamic occupancy models using variables derived from landscape models and compared their performance using quasi-AIC for each species. Results We obtained 909 detections for the six selected bird species. We found that PPSi and surface-based metrics were more informative when assessing occupancy patterns for five of the six species studied. In addition, surface-based metrics allowed to detect interspecific differences between species beyond an affinity for a particular cover type. Conclusions Surface-based metrics can be an alternative for assessing species response to landscape heterogeneity, particularly those that may be more sensitive to fine-scale changes in vegetation cover. However, there is no single “best” model to describe the landscape for all cases. PPSi can be very useful for land cover analysis in landscape ecology studies as an alternative to more popular vegetation indices.
... Bird communities are an excellent model system to investigate the effects of matrix quality on community assembly after habitat loss because it is a key factor in determining birds' movements and resource use in anthropogenic landscapes (Barros et al., 2019;Boesing et al., 2018a;Deikumah et al., 2013;Kennedy et al., 2010). Birds are especially mobile organisms, which allows them to actively search and respond to pulses of resources in ways not generally possible for other vertebrates, allowing them to leave areas in which resources are no longer sufficient and relocate to more productive locations (Whelan et al., 2008). ...
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Habitat loss represents a major threat to biodiversity, however, the modulation of its effects by the nonhabitat matrix surrounding habitat patches is still undervalued. The landscape matrix might change community assembly in different ways. For example, low‐quality matrices can accentuate environmental filtering by reducing resource availability and/or deteriorating abiotic conditions but they may also excessively limit dispersal of organisms and make communities more prone to ecological drift. To understand how matrix quality modulates the effects of habitat loss, we quantified the relative importance of environmental filter and ecological drift in bird communities across more local (400 m buffer around sampling sites) and broader (2 km focal landscapes) gradients of habitat loss embedded in low‐ and high‐quality matrices. We used a trait‐based approach to understand habitat loss filtering effects on occurrences of forest specialist and habitat generalist birds. We found that low‐quality matrices, composed mainly of low‐productive pasturelands, increased the severity of habitat loss filtering effects for forest specialist birds, but only at the landscape scale. Bird occurrences were in general higher in high‐quality matrices, that is, more heterogeneous and with low‐contrasting edges, indicating the role of the matrix quality in attenuating species extinction risks at the landscape scale, probably due to mass effect. Moreover, forest specialists presented a strong negative response to habitat loss filtering across different functional traits, while generalists presented a high variability in traits response to habitat loss. Synthesis and applications: We raised evidence in supporting that landscape habitat loss filtering may be relaxed or reinforced depending on the quality of the matrix, evidencing that matrix quality has a strong impact in modulating community assembly processes in fragmented landscapes. In practical terms, it means that improving matrix quality may help in maintaining the high diversity of birds even without any increase in native forest cover.
... the structural complexity of each survey point, we estimated the per cent cover of ground herbaceous vegetation (trees (>6 m) within a 10-m radius of each point count location's centre (Figure S4a). We divided the 10-m radius circles into four equal quadrants divided along the four cardinal directions(Kennedy et al., 2010). During each survey, we estimated the per cent vegetative cover in each height class for each of the four quadrants. ...
Article
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Birds play many roles within agroecosystems including as consumers of crops and pests, carriers of pathogens and beloved icons. Birds are also rapidly declining across North America, in part due to agricultural intensification. Thus, it is imperative to identify how to manage agroecosystems to best support birds for multi‐functional outcomes (e.g. crop production and conservation). Both the average amounts of services/disservices provided and their temporal stability are important for effective farm planning. Here, we conducted point count surveys for 4 years across 106 locations on 27 diversified farms in Washington and Oregon, USA. We classified birds as ecosystem service or disservice providers using indices spanning supporting, regulating, provisioning and cultural services/disservices. We then examined service/disservice index pairwise correlations and assessed the relative importance of local, farm and landscape complexity on the average and temporal stability of avian service/disservice provider indices. Generally, service provider indices (production benefitting birds, grower appreciation and conservation scores) were positively correlated with each other. Foodborne pathogen risk, grower disapproval and identity/iconic value indices were also positively correlated with each other. However, the crop damaging bird index generally had low correlations with other indices. Farms that implemented more conservation‐friendly management practices generally had higher average service provider indices, but farm management did not impact disservice provider indices, except for grower disapproval. Average disservice provider indices were lower on farms in complex landscapes. Local vertical vegetation complexity tended to increase the temporal stability of service provider indices but did not affect the disservice provider indices. Greater landscape complexity was generally associated with increased temporal stability of service and disservice provider indices. Increased landscape complexity may stabilize bird communities by increasing bird community evenness, which in turn, positively predicted temporal stability of all service/disservice provider indices. Policy implications. Our results suggest that farmers can effectively manage their farms to harness ecosystem services from birds through farm diversification. Disservices provided by birds, however, appear to be most negatively impacted by landscape‐level complexity. Thus, greater incentives for farmers to increase semi‐natural cover at the landscape scale are likely necessary to achieve multifunctional outcomes for conservation and agriculture.
... Avian and vegetation depend not only on each other but also on the entire food chain for additional food, shelter, and reproduction. All in all, the species traits provide a mechanistic link between the functional diversity of the avian community and the landscape characteristics, for they are directly related to vegetation characteristics [13] . The increased concerns of climate change have prompted research in preserving our wildlife, more notably wetlands. ...
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Background: Vegetation cover has an essential role in wetland habitats in controlling avian populations throughout the world. The vegetation cover structure in grassland systems varies dramatically among seasons on the same sites. Variation in vegetation cover-abundance richness and diversity has been studied through one hundred forty-seven quadrate samples during summer and autumn, 2019, winter, and spring 2020. Avian species richness and diversity were recorded during the same period. Results: The correlation analysis results confirmed that: (1) there was no apparent seasonal difference in the abundance of vegetation cover while avian abundance was statistically different. (2) Plant abundance in summer was positively correlated with the number of avian, while in autumn it was negatively correlated. Plant and avian abundance at the genus level showed a positive correlation while maintaining a negative correlation at the species level (p < 0.05). However, during summer and autumn, a strong linear relationship exists between vegetation coverage and avian. The Shannon diversity index and Simpson diversity index have a positive linear relationship between vegetation coverage and avian families and genera. Conclusions: We conclude that vegetation coverage richness significantly impact avian communities. We suggest further research into the relationship between other biological communities and farming practices in the wetlands.
... All in all, the species traits provide a mechanistic link between the functional diversity of the avian community and the landscape characteristics, for they are directly related to vegetation characteristics [13] . The increased concerns of climate change have prompted research in preserving our wildlife, more notably wetlands. ...
Preprint
Full-text available
Vegetation cover has an essential role in wetland habitats in controlling avian populations throughout the world. The vegetation cover structure in grassland systems varies dramatically among seasons on the same sites. Variation in vegetation cover-abundance richness and diversity has been studied through one hundred forty-seven quadrate samples during summer and autumn, 2019, winter, and spring 2020. Avian species richness and diversity were recorded during the same period. Meanwhile, correlation analysis results confirmed that: (1) there was no apparent seasonal difference in the abundance of vegetation cover while avian abundance was statistically different. (2) Plant abundance in summer was positively correlated with the number of avian, while in autumn it was negatively correlated. Plant and avian abundance at the genus level showed a positive correlation while maintaining a negative correlation at the species level (p < 0.05). However, during summer and autumn, a strong linear relationship exists between vegetation coverage and avian. The Shannon diversity index and Simpson diversity index have a positive linear relationship between vegetation coverage and avian families and genera. Therefore, we conclude that vegetation coverage and richness significantly impact avian communities. We suggest further research into the relationship between other biological communities and farming practices in the wetlands
... These findings indicate that even small losses of green areas lead to strongly impoverished bird communities. Specialist birds (forest specialists, insectivores) are particularly sensitive to habitat loss and fragmentation and thus avoid urban matrices (Kennedy et al. 2010). Also in our study, specialists like the jungle myna (Acridotheres fuscus) or the western cattle egret (Bubulcus ibis) were only observed on vegetable farms with low impervious area (<20%). ...
Chapter
In the last few decades, Bengaluru’s rapid urban expansion and associated population growth brought about profound changes in farming practices, reflected in an increase in irrigated land compared to rainfed land and a growing use of mineral fertilizers. Since it is not clear how intensification of land use due to urbanisation is affecting physical soil properties and field water cycle, we attempt to clarify this at two experimental sites established at the University of Agricultural Sciences Bangalore (UASB). The results show higher bulk densities, lower air capacities, and lower saturated hydraulic conductivity (Ksat) values in the rainfed field compared to the irrigated field. Soil moisture was observed to be higher in deeper layers of several plots with low N-level treatments in both experiments. However, it was not significant in other plots. Further statistical investigations and comparisons especially of model simulations are required to assess the effect of land use intensifications. Here the experimental approach and some preliminary results are presented.
... These findings indicate that even small losses of green areas lead to strongly impoverished bird communities. Specialist birds (forest specialists, insectivores) are particularly sensitive to habitat loss and fragmentation and thus avoid urban matrices (Kennedy et al. 2010). Also in our study, specialists like the jungle myna (Acridotheres fuscus) or the western cattle egret (Bubulcus ibis) were only observed on vegetable farms with low impervious area (<20%). ...
Chapter
Urban areas are increasing in number and extent worldwide. Few other anthropogenic land uses alter landscapes in a more persistent fashion; however, the effects of urbansiation on biodiversity remain poorly studied. Here, we studied bird communities along the rural–urban interface of the Indian megacity Bengaluru. Birds were assessed with point counts on 36 vegetable-growing farms situated within three urbanisation stages (urban, peri-urban and rural) and across three seasons (monsoon, winter, summer). We recorded 4617 individuals comprising 149 species. Bird richness was highest in peri-urban farms and lowest in rural areas, while urban areas were intermediate. Bird abundance did not differ among urbanisation stages. Increasing amount of impervious area in the surrounding landscape reduced bird richness and abundance, with the greatest effect up to 20% impervious area, levelling off beyond this threshold. Bird community composition on urban farms was distinct from rural areas, while peri-urban areas supported species from both species pools. In conclusion, urbanisation and particularly impervious areas threaten Bengaluru’s bird diversity. Peri-urban areas that mark the transition from rural to urban areas are hotspots of bird diversity. City planning should aim to retain green areas and avoid densification, particularly in the peri-urban interface where urbanisation happens most rapidly.
... Forest vertebrates have been particularly useful as model organisms for understanding the influence of landscape context (attributes of the environment surrounding habitat patches) as they generally show strong responses to it (Betts et al., 2006;McAlpine et al., 2006). Nevertheless, the majority of studies have been conducted in patches embedded in agricultural contexts and other disturbance regimes where the matrix is more benign, allowing frequent movement of fauna between habitat patches Kennedy et al., 2010Kennedy et al., , 2011. There is therefore a need for more studies conducted in landscapes where the matrix is more inhospitable and less permeable to movement (Kennedy et al., 2011). ...
Article
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The loss and fragmentation of natural habitats is a major threat to biodiversity globally. In fragmented landscapes, species are not only affected by patch-level attributes but also by the influence of the whole mosaic of landscape elements surrounding habitat patches. Therefore, it is important to understand the simultaneous effects of local and landscape-level attributes on biodiversity. In this study, we determined the influence of landscape context on species richness of forest mammals in an urban-forest mosaic of the EThekwini Municipality Area, Durban, South Africa. We determined presence/absence of mammals in 28 patches using remote-triggered camera traps over two sampling periods. We applied generalised linear modelling within an information-theoretic framework to quantify the effects of within-patch, isolation, matrix, and landscape level attributes on species richness. The results showed the importance of landscape context for occurrence patterns of mammals in fragmented landscapes. In particular, they showed that patch size, shape complexity, habitat amount in the immediate environment, habitat proximity and road density were the most important factors influencing mammalian richness patterns. Overall, the results stressed the importance of habitat area (patch size, habitat amount in the immediate environment, and habitat proximity) and its spatial configuration to faunal preservation and suggest that management efforts in this landscape should be aimed at protecting fragments from further loss and disturbance and matrix improvement to increase landscape connectivity.
... To understand how changes in vegetation influence bird communities, birds can be placed into guilds, or groups of species with similar preferences for foraging substrate, nesting type, and breeding habitat (Simberloff and Dayan 1991). Using guilds allows for the examination of bird habitat requirements at the community level as opposed to the species level (Kennedy et al. 2010;Lesak et al. 2011;Weisberg et al. 2014). Additionally, bird guilds can improve the prediction of rare species or data deficient species (Leathwick et al. 2006). ...
Article
Riparian areas are among the most ecologically diverse terrestrial ecosystems but make up <2% of landscape area in southwestern USA. Many species of resident and neotropical migratory birds utilize riparian habitats for breeding, foraging, and nesting. We quantified vegetation composition and structure to predict bird guilds on Wild and Scenic portions of the Verde River, Arizona. We grouped plant species into guilds based on similar functional traits to describe composition. We surveyed birds during the breeding and migrating season to determine abundance and categorized species into guilds using preferences of breeding habitat, foraging substrate, and nest placement. Riparian obligate and facultative breeding guilds were most common. Both vegetation composition and structure were useful predictors of birds. Vegetation structure was most complex in gallery riparian forest. Abundance of riparian-obligate birds in the breeding guild were positively associated with vegetation structure of dense, multi-canopy canopy and tall trees. Abundance of most bird guilds were positively associated with composition of tall trees (Populus fremontii, Salix gooddingii) and drought tolerant shrubs (Prosopis velutina, Celtis reticulata). Our findings show complex riparian habitat important to wildlife is created by both composition and structure of near-stream vegetation that is tied to hydrology and sensitive to flow change.
... and Penelope spp.) which feed mostly on the ground were poorly represented in the present study. Overall, frugivores are more susceptible to local extinction because their populations are possibly limited by the availability of fruit during periods of scarcity (Antunes, 2005;Cleary et al., 2007;Kennedy et al., 2010) and by hunting (Peres, 2001). Thus, species belonging to this guild tend to disappear from small patches, since they require areas with a wide variety of tree species that produces fruit at different seasons of the year (Willis, 1979;Piratelli et al., 2005;Ferger et al., 2014). ...
Article
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The Volta Grande region in the Brazilian state of Minas Gerais is classified as of “High Biological Importance” for the conservation of birds in the state. Despite this, the avifauna of the region has yet to be adequately sampled, as evidenced by the few papers on the region in ornithological literature. The results of an avifaunal inventory conducted between March 2013 and January 2014 in five sites located throughout the region of the Volta Grande Hydroelectric Power Plant in Southeast Brazil are presented. Point-counts, ad libitum observations and mist-nets recorded 224 species for the region, with insectivorous and omnivorous being the predominant feeding habits. Species that are “independent” of forest habitats comprised 52% of the recorded species. Three species are endemics of the Cerrado, 83 are migratory and 32 are under some degree of threat of extinction. These findings demonstrate that the region of the Volta Grande Hydroelectric Power Plant is important for bird conservation. Additional inventories, adequate management plans and public policies aimed the preserving species are needed for more effective conservation of the biodiversity of the studied region.
... Once established, these pioneering bird populations in fragments and second growth may be subject to source-sink dynamics where vulnerable species periodically perish and are subsequently replaced by individuals from higher quality habitats with higher survival and reproductive surpluses (Sodhi et al. 2011). Clearly, the transition of Amazonian forest fragments from depauperate patches to potential sources may principally depend on the condition of the surrounding matrix (Renjifo 2001;Ewers and Didham 2006;Stouffer and Bierregaard 2007;Kennedy et al. 2010). The dynamic role of a developing matrix revealed at the BDFFP suggests that bird survival in fragments is likely mediated by the matrix as well. ...
Article
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Background Vast areas of lowland neotropical forest have regenerated after initially being cleared for agricultural purposes. The ecological value of regenerating second growth to forest-dwelling birds may largely depend on the age of the forest, associated vegetative structure, and when it is capable of sustaining avian demographics similar to those found in pristine forest. Methods To determine the influence of second growth age on bird demography, we estimated the annual survival of six central Amazonian bird species residing in pristine forest, a single 100 and a single 10 ha forest fragment, taking into consideration age of the surrounding matrix (i.e. regenerating forest adjacent to each fragment) as an explanatory variable. Results Study species exhibited three responses: arboreal, flocking and ant-following insectivores ( Willisornis poecilinotus , Thamnomanes ardesiacus and Pithys albifrons ) showed declines in survival associated with fragmentation followed by an increase in survival after 5 years of matrix regeneration. Conversely, Percnostola rufifrons , a gap-specialist, showed elevated survival in response to fragmentation followed by a decline after 5 years of regeneration. Lastly, facultative flocking and frugivore species ( Glyphorynchus spirurus and Dixiphia pipra , respectively) showed no response to adjacent clearing and subsequent regeneration. Conclusions Our results in association with previous studies confirm that the value of regenerating forest surrounding habitat patches is dependent on two factors: ecological guild of the species in question and second growth age. Given the rapid increase in survival following succession, we suggest that the ecological value of young tropical forest should not be based solely on a contemporary snapshot, but rather, on the future value of mature second growth as well.
... We used nonmetric multidimensional scaling (NMDS) to describe the variation in the composition of farm bird communities between farming systems within each Bird Conservation Region (Kennedy et al. 2010). The NMDS was performed in the vegan package of program R version 3.4.3 ...
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Agricultural intensification is a leading threat to bird conservation. Highly diversified farming systems that integrate livestock and crop production might promote a diversity of habitats useful to native birds foraging across otherwise-simplified landscapes. At the same time, these features might be attractive to nonnative birds linked to a broad range of disservices to both crop and livestock production. We evaluated the influence of crop-livestock integration on wild bird richness and density along a north-south transect spanning the U.S. West Coast. We surveyed birds on 52 farms that grew primarily mixed vegetables and fruits alone or integrated livestock into production. Crop-livestock systems harbored higher native bird density and richness relative to crop-only farms, a benefit more pronounced on farms embedded in nonnatural landscapes. Crop-livestock systems bolstered native insectivores linked to the suppression of agricultural pest insects but did not bolster native granivores that may be more likely to damage crops. Crop-livestock systems also significantly increased the density of nonnative birds, primarily European Starlings (Sturnus vulgaris) and House Sparrows (Passer domesticus) that may compete with native birds for resources. Models supported a small, positive correlation between nonnative density and overall native bird density as well as between nonnative density and native granivore density. Relative to crop-only farms, on average , crop-livestock systems exhibited 1.5 times higher patch richness, 2.4 times higher density of farm structures, 7.3 times smaller field sizes, 2.4 times greater integration of woody crops, and 5.3 times greater integration of pasture/hay habitat on farm. Wild birds may have responded to this habitat diversity and/or associated food resources. Individual farm factors had significantly lower predictive power than farming system alone (change in C statistic information criterion (DCIC) = 80.2), suggesting crop-livestock systems may impact wild birds through a suite of factors that change with system conversion. Collectively, our findings suggest that farms that integrate livestock and crop production can attract robust native bird communities , especially within landscapes devoted to intensified food production. However, additional work is needed to demonstrate persistent farm bird communities through time, eco-physiological benefits to birds foraging on these farms, and net effects of both native and non-native wild birds in agroecosystems.
... We used nonmetric multidimensional scaling (NMDS) to describe the variation in the composition of farm bird communities between farming systems within each Bird Conservation Region (Kennedy et al. 2010). The NMDS was performed in the vegan package of program R version 3.4.3 ...
Article
Full-text available
Agricultural intensification is a leading threat to bird conservation. Highly diversified farming systems that integrate livestock and crop production might promote a diversity of habitats useful to native birds foraging across otherwise‐simplified landscapes. At the same time, these features might be attractive to nonnative birds linked to a broad range of disservices to both crop and livestock production. We evaluated the influence of crop–livestock integration on wild bird richness and density along a north‐south transect spanning the U.S. West Coast. We surveyed birds on 52 farms that grew primarily mixed vegetables and fruits alone or integrated livestock into production. Crop–livestock systems harbored higher native bird density and richness relative to crop‐only farms, a benefit more pronounced on farms embedded in nonnatural landscapes. Crop–livestock systems bolstered native insectivores linked to the suppression of agricultural pest insects but did not bolster native granivores that may be more likely to damage crops. Crop–livestock systems also significantly increased the density of nonnative birds, primarily European Starlings (Sturnus vulgaris) and House Sparrows (Passer domesticus) that may compete with native birds for resources. Models supported a small, positive correlation between nonnative density and overall native bird density as well as between nonnative density and native granivore density. Relative to crop‐only farms, on average, crop–livestock systems exhibited 1.5 times higher patch richness, 2.4 times higher density of farm structures, 7.3 times smaller field sizes, 2.4 times greater integration of woody crops, and 5.3 times greater integration of pasture/hay habitat on farm. Wild birds may have responded to this habitat diversity and/or associated food resources. Individual farm factors had significantly lower predictive power than farming system alone (change in C statistic information criterion (ΔCIC) = 80.2), suggesting crop–livestock systems may impact wild birds through a suite of factors that change with system conversion. Collectively, our findings suggest that farms that integrate livestock and crop production can attract robust native bird communities, especially within landscapes devoted to intensified food production. However, additional work is needed to demonstrate persistent farm bird communities through time, ecophysiological benefits to birds foraging on these farms, and net effects of both native and nonnative wild birds in agroecosystems.
... The mechanisms by which urbanization affects forest bird species include reduced movement success, altered resource availability, and increased disturbance [12]. More intense urbanization increases the effective isolation of forest patches [13,14] and likely increases dispersal mortality by means of collisions with buildings and vehicles, and predation by domestic cats [15,16]. ...
Article
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As humans continue moving to urban areas, there is a growing need to understand the effects of urban intensification on native wildlife populations. Forest species in remnant habitat are particularly vulnerable to urban intensification, but the mechanisms behind these effects are poorly understood. An understanding of how species traits, as proxies for mechanisms, mediate the effects of urban intensification on forest species can help fill this knowledge gap. Using a large point count dataset from the Second Pennsylvania Breeding Bird Atlas, we tested for the effects of species traits on the magnitude and spatial scale of the responses of 58 forest bird species to urbanization intensity in landscapes surrounding count locations. Average urbanization intensity effect size across species was -0.36 ± 0.49 (SE) and average scale of effect of urbanization intensity was 4.87 ± 5.95 km. Resident forest bird species that are granivorous or frugivorous, cavity-nesting, and have larger clutch sizes and more fledglings per clutch had more positive associations with increasing urbanization intensity in landscapes. In addition, the effect of urbanization intensity on forest birds manifested most strongly at larger spatial scales for granivorous, frugivorous, or omnivorous species that are cavity-nesting, have larger clutch sizes and longer wingspans, and flock in larger numbers. To our knowledge, the present study represents the first direct tests of the effects of species traits on both the magnitude and spatial scale of the effect of urbanization on forest birds, as well as the first evidence that migratory status, clutch size, wingspan, and fledglings per clutch are important determinants of the responses of forest birds to urbanization. We discuss the possible mechanisms underlying our results and their implications for forest bird conservation in urbanizing landscapes.
... We used non-metric multi-dimensional scaling (NMDS) to separately describe the variation in the composition of dung beetle and fly communities in conventional, organic, and integrated farming systems (per Kennedy et al., 2010). NMDS is a nonparametric ordination technique effective for graphically depicting multivariate relationships in ecological data, via maximizing the rank correlation between calculated distances in an original matrix and distances in reduced ordination space (Clarke, 1993). ...
... land-use diversity), have received increasing research attention due to their interplay with overall forest amount in maintaining native biodiversity (Driscoll et al. 2013) and promoting land-use multifunctionality (van der Plas et al. 2019). In fragmented forest landscapes, for instance, avian extinction thresholds depend on the predominant matrix type (Boesing et al. 2018b), which may induce selective filtering of species traits (Kennedy et al. 2010(Kennedy et al. , 2017. Some recent studies argue that matrix effects should be a key factor compensating for potentially negative landscape level effects of fragmentation per se (i.e. ...
Article
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Land use intensification drives biodiversity loss worldwide. In heterogeneous landscape mosaics, both overall forest area and anthropogenic matrix structure induce changes in biological communities in primary habitat remnants. However, community changes via cross‐habitat spillover processes along forest‐matrix interfaces remain poorly understood. Moreover, information on how landscape attributes affect spillover processes across habitat boundaries are embryonic. Here, we quantify avian α and β‐diversity (as proxies of spillover rates) across two dominant types of forest‐matrix interfaces (forest‐pasture and forest‐eucalyptus plantation) within the Atlantic Forest biodiversity hotspot in southeast Brazil. We also assess the effects of anthropogenic matrix type and landscape attributes (forest cover, edge density and land‐use diversity) on bird taxonomic and functional β‐diversity across forest‐matrix boundaries. Alpha taxonomic richness was higher in forest edges than within both matrix types, but between matrix types, it was higher in pastures than in eucalyptus plantations. Although significantly higher in forests edges than in the adjacent eucalyptus, bird functional richness did not differ between forest edges and adjacent pastures. Community changes (β‐diversity) related to species and functional replacements (turnover component) were higher across forest‐pasture boundaries, whereas changes related to species and functional loss (nested component) were higher across forest‐eucalyptus boundaries. Forest edges adjacent to eucalyptus had significant higher species and functional replacements than forest edges adjacent to pastures. Forest cover negatively influenced functional β‐diversity across both forest‐pasture and forest‐eucalyptus interfaces. We show the importance of matrix type and the structure of surrounding landscapes (mainly forest cover) on rates of bird assemblage spillover across forest‐matrix boundaries, which has profound implications to biological fluxes, ecosystem functioning and land‐use management in human‐modified landscapes. This article is protected by copyright. All rights reserved.
... Human-modified environments can influence species by changing the abiotic environment, providing foraging and other resources (Kennedy et al., 2010), or influencing the ability of animals to move through landscapes (Driscoll et al., 2013). Land cover that is perceived as the matrix (and therefore inhospitable) for some species might in fact be suitable habitat for other species Kennedy et al., 2011). ...
Article
Improved management of human-modified landscapes must be part of global efforts to combat biodiversity loss. We aimed to identify which land management types and environmental factors influenced the use of grazing landscapes by frogs. We surveyed frog assemblages in remnant vegetation, four different paddock types (pasture, linear planting, coarse woody debris addition and fence), and two grazing regimes (continuous and rotational). Frogs were surveyed using pitfall and funnel traps in twelve grazing farms in south-eastern Australia. We found that grazed agricultural landscapes provide important habitats for a variety of species of frogs and that frog assemblages were influenced by both farm management type and environmental variables, and their interactions. Total frog abundance increased with proximity to water more strongly in remnants compared to paddocks. This difference in response may be due to different traits and behaviours of frogs in remnants compared to frogs in open paddocks. Rare frog species richness and abundance of a common species (Limnodynastes tasmaniensis) increased with taller ground cover in remnants but no such relationship occurred in paddocks. Different types of predation risk in remnants compared to paddocks may result in greater ground cover shelter requirements in remnants, as vegetation structure can strongly influence predation. Total frog species richness increased more rapidly with higher rainfall in continuously grazed versus rotationally grazed farms. Higher rainfall was associated with taller ground cover. Continuously grazed farms had shorter average ground cover than rotationally grazed farms and the increased ground cover height associated with more rain may bring ground cover to a height better able to provide shelter and reduce desiccation risk for frogs. Our study highlights the importance of both land management practices and environmental conditions and their interaction in shaping frog assemblages. Improved frog biodiversity conservation may be achieved in grazing landscapes by retaining patches of remnant vegetation, maintaining water bodies such as farm dams, and maintaining tall ground cover within vegetation remnants.
... Dietary guilds in particular often exhibit variable responses to agricultural land-use change (Fig. 4). Birds, frugivores, insectivores, and nectarivores tend to decline while carnivores and granivores increase in agriculture [121,122]. Almost all dietary guilds exhibit declines in response to agricultural land-use change in the limited number of studies on mammals [123]. Studies measuring diet breadth of invertebrates found no patterns in responses of generalists, but a general trend of declines in specialist invertebrates over gradients of agriculture [124]. ...
Article
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Purpose of Review Countryside biogeography seeks to explain the distribution of wildlife in human-dominated landscapes. We review the theoretical and empirical progress towards this goal, assessing what forces control the presence, abundance, and richness of species in anthropogenic and natural habitats, based on characteristics of the landscape and the species themselves. Recent Findings Recent modifications of species-area relationships that incorporate multiple habitat types have improved understanding of species diversity in countryside landscapes. Attempts to understand why species affiliate with human-modified habitats have been met with only partial success. Though traits frequently explain associations with human-modified habitats within studies, explanatory traits are only rarely shared between studies, regions, or taxa. Nonetheless, greater attention to the regional and climatological context of countryside landscapes has uncovered that (i) species that associate with human-modified habitats within landscapes tend to occur primarily in warm and/or dry biomes at regional scales and (ii) species that rely exclusively on human-modified habitats in cool or wet regions may be restricted to natural habitats in warm or dry regions. Summary There remains a pressing need to determine how biodiversity can best be supported within landscapes to preserve nature and maximize ecosystem service benefits for humans. Future work in countryside biogeography must identify how land-use change interacts with other global stressors (e.g., climate change), determine how extinction debt and population sinks influence diversity, quantify the cascading effects of community changes on ecosystem services, and elucidate the evolutionary history and origins of species that today dwell in the countryside.
... In particular, using a historically fragmented system allows us to avoid erroneous conclusions due to delayed effects of fragmentation on biodiversity over time and extinction debt (Tilman et al. 1994, Ewers and Didham 2006, Fletcher et al. 2018. The relatively homogeneous matrix surrounding k ıpuka eliminates the need to incorporate the well-known effects of differential landscape resistance (Ricketts 2001, Kennedy et al. 2010) into our analyses. Prior work in the k ıpuka landscape has demonstrated a canonical log-log species-area relationship for forest birds (Flaspohler et al. 2010), as well as correlations between k ıpuka area, connectivity, and soil fungal diversity and composition (Vannette et al. 2016). ...
Article
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Habitat fragmentation resulting in habitat loss and increased isolation is a dominant driver of global species declines. Habitat isolation and connectivity vary across scales, and understanding how connectivity affects biodiversity can be challenging because the relevant scale depends on the taxa involved. A multiscale analysis can provide insight in biodiversity patterns across spatial scale when information on dispersal ability is not available, in particular for community‐level studies focusing on multiple taxa. In this study, we examine the relationship between arthropod diversity, patch area, and connectivity using a multiscale approach. We make use of a natural experiment on Hawai‘i Island, where historic volcanic activity has transformed contiguous native forests to lava matrix and discrete forest patches. This landscape of patches has persisted for 150 yr, and we selected 10,000 ha consisting of 863 patches to analyze landscape connectivity using a graph theory approach. We collected arthropod samples from Metrosideros polymorpha tree canopies in 34 forest patches during multiple years. We analyzed the relationship of arthropod diversity with area, as well as with connectivity across increasing scales, or dispersal threshold distances. In contrast to well‐established ecological theory as well as prior work on birds and fungi in this system, we did not find support for a canonical species–area relationship. Next, we calculated connectivity across spatial scales and found lower Shannon diversity with higher connectivity at small scales, but no effect at increased dispersal threshold distances. We examined the landscape structure and found all habitat patches connected into three subnetworks at a 350 m threshold distance. All patches were connected at 700 m threshold distance, indicating structural dispersal limitation only at small scales. Our findings suggest that canopy arthropods are not dispersal limited at scales shown to impact both soil fungi and birds in this system. Instead, Hawaiian canopy arthropods may perceive the landscape as a connected area where discrete forest patches and the early‐successional matrix contribute resources that vary spatially with regard to habitat quality. We argue for the utility of multiscale approaches, and the importance of examining maintenance of biodiversity in fragmented landscapes that persist for hundreds of years.
... Individuals have also been recorded in other parts of North America, including Louisiana andOhio (McLean et al. 1995, Remsen &Sweet 2008). They are found in a range of habitats (Giner & Strahl 1988, Beltzer et al. 2009) but typically do well in disturbed, human and agricultural areas (Souza 1995, Ridgely & Greenfield 2001a, Kennedy et al. 2010. ...
Article
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The smooth-billed ani (Crotophaga ani) is a widespread introduced bird species in the biologically important archipelago of Galápagos. Many scientists and local people consider it to be a damaging invasive, and it is possible that it impacts native species and ecosystems via multiple mechanisms. However, evidence for this is largely anecdotal and research on smooth-billed anis in Galápagos is limited. Despite this, there have been repeated attempts to control or eradicate the population over the past few decades, all without long-term success. These attempts continue, but no official plan of action regarding this species currently exists. This review brings together all available information on smooth-billed anis in Galápagos. We use both published and unpublished research to answer the following questions: 1. What is known about the history of the smooth-billed anis' introduction to Galápagos? 2. What are the possible impacts of smooth-billed anis in Galápagos? 3. What attempts have been undertaken to control or eradicate smooth-billed anis in Galápagos and what were their outcomes? In answering these questions, we highlight numerous knowledge gaps, in both the current understanding of the impacts of this introduced species and the effectiveness of potential control or eradication methods. We find an urgent need for further research before considered, resource-efficient decisions can be made regarding smooth-billed anis in Galápagos.
... species with low reproduction, low dispersal ability and specialist host plant requirements have been shown to be most sensitive to habitat loss (Ö ckinger et al. 2010). Species traits have also been linked to different matrix response for many species groups, from plants to birds (Davies et al. 2000;Dupré and Ehrlén 2002;Pöyry et al. 2009;Kennedy et al. 2010). Strategies aimed to mitigate and counteract the negative effects of agricultural intensification on biodiversity have been implemented in several countries across Europe since the 1970s, but the problems still faced by conservationists and policy makers are to understand how species respond to habitat changes, where to target conservation and how large areas that should be protected (Franklin 1993;Green et al. 2005;Broughton et al. 2014;Botham et al. 2015). ...
Article
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Context Loss and fragmentation of semi-natural grasslands has critically affected many butterfly species in Europe. Habitat area and isolation can have strong effects on the local biodiversity but species may also be strongly affected by the surrounding matrix. Objectives We explored how different land cover types in the landscape explained the occurrence of butterfly species in semi-natural grasslands. Methods Using data from 476 semi-natural grasslands in Sweden, we analysed the effect of matrix composition on species richness and occurrence. Additionally, we analysed at which spatial scales butterflies responded to matrix types (forests, semi-natural grasslands, arable land and water). Results Forest cover showed the strongest positive effect on species richness, followed by semi-natural grasslands. Forest also had a positive effect on red-listed species at local scales. Responses to matrix composition were highly species-specific. The majority of the 30 most common species showed strong positive responses to the amount of forest cover within 200–500 m. There was a smaller group of species showing a positive response to arable land cover within 500–2000 m. Thirteen species showed positive responses to the amount of semi-natural grasslands, generally at larger scales (10–30 km). Conclusions Our study showed that surrounding forest is beneficial for many grassland butterfly species and that forests might mitigate the negative effects of habitat loss caused by agricultural intensification. Also, semi-natural grasslands were an important factor for species richness at larger spatial scales, indicating that a landscape consisting mainly of supporting habitats (i.e. forests) are insufficient to sustain a rich butterfly fauna.
... Many tropical birds also defend territories throughout the year rather than just in the breeding season (Stutchbury and Morton, 2001). Therefore, we believe that the resident forest raptor community may show low species turnover due to the species' (Antongiovanni and Metzger, 2005;Gobeil and Villard, 2002;Kennedy et al., 2010;Renjifo, 2001). ...
Conference Paper
The response of birds to hurricane disturbance may differ among functional groups, but little is known regarding the response of birds of prey to these disturbances. We aimed to evaluate the influence of Hurricane Patricia on the diversity of diurnal raptors in tropical dry forest in Mexico. We conducted raptor surveys at 13 sites located within the eyewall radius of maximum hurricane winds along the hurricane’s path, and 16 sites outside this area. We compared density and species richness among four habitats of deciduous and semi-deciduous forest, mangroves and agricultural fields, within the hurricane eyewall and outside the eyewall. We observed a reduction in raptor density in forests within the eyewall. Raptor density was significantly lower in deciduous forests within the eyewall compared to deciduous forests outside this area. Species richness was similar among habitats and conditions, but mangroves within the eyewall had significant higher species richness compared to mangroves outside this area. We found a significant increase in species evenness, and decrease in similarity of raptor communities in mangroves and deciduous forests within the eyewall, compared to mangroves outside the eyewall. Reduced density of raptors in forest within the path of the hurricane probably reflects the impact of winds on forest structure, whereas the increase in evenness and species richness in mangroves within the hurricane eyewall suggests that these habitats could provide refuge for raptors following hurricanes. Our results highlight the importance of maintaining landscape heterogeneity to provide alternate habitats for wildlife communities and facilitate their resilience following major disturbances.
... Forest fragmentation is widely recognised as a pervasive and lasting threat to biodiversity and ecosystem functioning as forest fragments are subject to the combined detrimental effects of core area reduction, edge proliferation, and isolation (Haddad et al., 2015). Nevertheless, the quality of the matrix surrounding forest fragments plays a major role in determining the severity of fragmentation (Kennedy, Marra, Fagan, & Neel, 2010). Old-growth forest fragments surrounded by secondary forests favour species that exploit matrix resources (Blake & Loiselle, 2001), are less affected by edge effects (Laurance et al., 2011), and are more permeable, ensuring species movements among forest fragments (Powell, Stouffer, & Johnson, 2013). ...
Article
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Aim We assessed patterns of avian species loss and the role of morpho‐ecological traits in explaining species vulnerability to forest fragmentation in an anthropogenic island system. We also contrasted observed and detectability‐corrected estimates of island occupancy, which are often used to infer species vulnerability. Location Tucuruí Hydroelectric Reservoir, eastern Brazilian Amazonia. Methods We surveyed forest birds within 36 islands (3.4–2,551.5 ha) after 22 years of post‐isolation history. We applied species–area relationships to assess differential patterns of species loss among three data sets: all species, forest specialists and habitat generalists. After controlling for phylogenetic non‐independence, we used observed and detectability‐corrected estimates of island occupancy separately to build competing models as a function of species traits. The magnitude of the difference between these estimates of island occupancy was contrasted against species detectability. Results The rate of species loss as a function of island area reduction was higher for forest specialists than for habitat generalists. Accounting for the area effect, forest fragmentation did not affect the overall number of species regardless of the data set. Only the interactive model including natural abundance, habitat breadth and geographic range size was strongly supported for both estimates of island occupancy. For 30 species with detection probabilities below 30%, detectability‐corrected estimates were at least tenfold higher than those observed. Conversely, differences between estimates were negligible or non‐existent for all 31 species with detection probabilities exceeding 45.5%. Main conclusions Predicted decay of avian species richness induced by forest loss is affected by the degree of habitat specialisation of the species under consideration, and may be unrelated to forest fragmentation per se. Natural abundance was the main predictor of species island occupancy, although habitat breadth and geographic range size also played a role. We caution against using occupancy models for low‐detectability species, because overestimates of island occupancy reduce the power of species‐level predictions of vulnerability.
... Most studies (71%) comparing bird numbers among sites with different urbanization intensities were located within the urban matrix (Varela-Contador 2003; Leveau and Leveau 2004;MacGregor-Fors et al. 2010a;Silva et al. 2016); yet, others were conducted in urban greenspaces (Toledo 2007;Suarez-Rubio and Thomlinson 2009;Carbó-Ramírez and Zuria 2011;González-Oreja et al. 2012). Fewer studies compared bird abundances among urbanization intensity scenarios, for instance: (i) between urban greenspaces and nonurban areas (Carvalho and Marini 2007;Kennedy et al. 2010;Chávez-Zichinelli et al. 2013); (ii) at increasing distances from urban settlements (Thornton et al. 2012;Lozano and Malo 2013); (iii) and in urban wetlands (Villaneda-Rey and Rosselli 2011; Rosselli and Stiles 2012). Although most of the studies were performed in a single urban area, a couple of studies were conducted in three or more cities (Thornton et al. 2012;Campbell 2014). ...
Chapter
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We here provide a general overview of the study of bird abundance, demography, and populations in urban environments with special attention on those from Latin America. We found that studies focused on bird abundance and demography were more common in Argentina, Brazil, and Mexico. We classified those species taken into account in four or more studies according to their response to urbanization. In general, specialist birds are negatively related with urbanization, whereas two invasive exotics, the Rock Pigeon (Columba livia) and House Sparrow (Passer domesticus), are present in most of the reviewed urbanized areas along Latin America. Although scarce, studies of bird demography revealed, in general, higher bird survival in urban environments, possibly due to lower predator density. However, anthropogenic causes have been identified to affect bird populations in urban areas (e.g., window and vehicle collisions, nest predation, predation by domestic cats and dogs). Future studies will importantly add to our knowledge of urban bird ecology in Latin America by continuing to quantify bird numbers and assess demography patterns, as well as identifying the factors that mold them. Birds, as highly informative and charismatic bioindicators, could play a crucial role in adding evidence-based knowledge for decision-makers to take action in building bird-friendly and livable cities.
... Ricketts, 2001;Revilla et al., 2004), by modifying resource availability (Grundel & Pavlovic, 2007) and by increasing edge effects (Saunders et al., 1991). The impact of the landscape matrix may be different depending on anthropogenic disturbance, amount and configuration of natural patches (Kennedy et al., 2010). Moreover, communities occur on gradients of environmental variables and these interactions (e.g. ...
Article
Different processes drive spatial variation in community composition. Standard measures of composition are useful in species‐based conservation and ecology, but they may be less informative in the context of evolutionary history and functional diversity. Functional and phylogenetic approaches are increasingly used to test mechanisms driving biodiversity patterns. We studied 28 families of flies (Diptera) with a range of functional characteristics in three wetland classes (bogs, swamps, marshes) in Quebec, Canada. We examined taxonomic, phylogenetic and functional structure of communities and assessed whether rarity is deterministic or stochastic. Beta‐ and phylobeta‐diversity were also examined for relatedness to local environmental conditions, patch area, and/or surrounding landscape. Phylogenetic community structure analyses had high value and complementarity to standard measures. Environmental filtering acted on bog communities during assembly, as they emerged from a slow peat accumulation process and the plant composition is characteristic as few species can survive in these acidic and low nutrient conditions. Subsequently, community assembly happened randomly. Neutral processes of community assembly are more important in marshes and swamps, as dispersal limitation explained species abundance dynamics of small and common Diptera species. The assembly of marsh communities is a balance between neutral processes and environmental filtering, while assembly in swamps can be seen as neutral. Clustering increased with environmental extremes, indicating environmental filtering. Rare species tended to be less closely related to common species. They have unique habitat requirements, and the high diversity is maintained by temporal turnover of species with similar traits filtered by the environment.
... The significance of matrix or land type near wildlife habitats has been recognized globally (Deikumah, McAlpine, & Maron, 2014;Kennedy, Marra, Fagan, & Neel, 2010;Ruiz-Guerra, Renton, & Dirzo, 2012). A matrix can be a major source of feeding and breeding site for wildlife (Antongiovanni & Metzger, 2005); a link permitting movement of wildlife between habitats (Devictor & Jiguet, 2007) and a temporary or permanent habitat for some species (Cline & Hunter, 2016). ...
Article
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The conservation of biodiversity within tropical forest regions does not lie only in the maintenance of natural forest areas, but on conservation strategies directed toward agricultural land types within which they are embedded. This study investigated variations in bird assemblages of different functional groups of forest-dependent birds in three agricultural land types, relative to distance from the interior of 34 tropical forest patches of varying sizes. Point counts were used to sample birds at each study site visited. Data from counts were used to estimate species richness, species evenness, and Simpson's diversity of birds. Mean species richness, evenness, and diversity were modeled as responses and as a function of agricultural land type, distance from the forest interior and three site-scale vegetation covariates (density of large trees, fruiting trees, and patch size) using generalized linear mixed-effect models. Mean observed species richness of birds varied significantly within habitat types. Mean observed species richness was highest in forest interior sites while sites located in farm centers recorded the lowest mean species richness. Species richness of forest specialists was strongly influenced by the type of agricultural land use. Fallow lands, density of large trees, and patch size strongly positively influenced forest specialists. Insectivorous and frugivorous birds were more species-rich in fallow lands while monoculture plantations favored nectarivorous birds. Our results suggest that poor agricultural practices can lead to population declines of forest-dependent birds particularly specialist species. Conservation actions should include proper land use management that ensures heterogeneity through retention of native tree species on farms in tropical forest-agriculture landscapes.
... De récents travaux ont montré qu'une interaction entre les différents éléments du paysage existe et que la nature de la matrice influence les assemblages d'espèces dans les fragments (Rodewald & Yahner 2001, Kennedy et al. 2010. ...
Thesis
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L’objectif de la première partie de ma thèse était de déterminer les effets de la perte d’habitat, sa configuration et la composition du paysage sur certains patrons biologiques, notamment la richesse totale des oiseaux nicheurs, celle des différentes guildes et l’occurrence de cinq espèces cibles. Mes résultats ont montré que ces trois processus étaient impliqués à différents degrés. A l’échelle des communautés, la richesse spécifique totale des oiseaux nicheurs était plus fortement corrélée à la quantité de maquis haut et à la longueur de la lisière dans le paysage qu’à la réduction de la proportion de forêt. En effet, les forêts continues abritent moins d’espèces d’oiseaux nicheurs que les fragments (de 2 à 80 ha). Cependant, l’examen de la composition des assemblages d’espèces a montré une différence entre les massifs de vieilles forêts matures et les fragments. Les oiseaux cavicoles étant les espèces les plus dépendantes des grands arbres comme substrat de nidification n’étaient pas toujours absents des fragments. Certes, leur probabilité d’occurrence diminuait mais sous certaines conditions, elles pouvaient persister dans les fragments en complétant leurs besoins (ex. le Pic épeiche et le Pic de Levaillant) par des ressources trouvées dans le maquis haut ou en utilisant plusieurs fragments de forêts rapprochés pour supplémenter leurs besoins, le cas du Pic épeichette. Par contre, les espèces inféodées à une strate de végétation buissonnante profitaient de la dégradation de la forêt, par exemple par l’abattage des grands arbres, pour occuper les stations perturbées où les buissons prolifèrent. Toutefois, elles étaient totalement absentes des sites localisés à l’intérieur de la forêt, où la densité des grands arbres est très élevée et le sous-bois est absent. Le faible nombre d’espèces d’oiseaux spécialistes des forêts dans notre avifaune régionale serait aussi à l’origine de la faible richesse de l’assemblage d’oiseaux des vieilles forêts. Cet assemblage d’espèces est plus homogène et composé de plus d’espèces spécialistes que celui des fragments. A l’échelle des guildes, les nicheurs cavicoles (Fig.1) montraient une réponse positive à la quantité de forêt et à sa configuration (ex. indice de proximité) dans le paysage. Par contre, ils ont montré une réponse négative à la quantité de maquis haut. Cependant, la guilde des nicheurs en sous-bois n’a répondu significativement qu’à la perte de la forêt et à la composition du paysage. Quant à eux, les oiseaux nicheurs de la canopée n’ont montré aucune réponse significative à ces trois processus. A une échelle plus fine, celle des espèces, la réponse à la perte de forêt, sa configuration et la composition du paysage était variable. Par exemple, l’occurrence du Pic épeichette était prédite par la configuration de la forêt tandis que celles du Pic de Levaillant et du Pic épeiche répondaient plutôt à la composition du paysage. L’occurrence du Grimpereau des jardins et du Gobemouche de l’Atlas, quant à elle, était liée à la quantité de forêt à l’échelle locale et celle du paysage. La réponse positive du Pic épeiche et du Pic de Levaillant à la matrice suggère que cette dernière n’est pas complètement hostile. Nous devons donc tenir compte d’une possible complémentation à partir de la matrice chez certaines espèces (fig.2). Le maquis haut joue ainsi un rôle qui ne devrait pas être négligé dans le développement des cibles de la conservation. Toutefois, la réponse négative du Pic épeichette, du Grimpereau des jardins et du Gobemouche de l’Atlas envers le maquis haut ne devrait pas être sous-estimée non plus (fig.2). Par rapport au maquis haut, le maquis bas a un effet négatif sur l’occurrence de toutes les espèces cavicoles. Seules quelques espèces de fauvettes comme la Fauvette pitchou, à lunette, passerinette et grisette ont montré une affinité pour la végétation buissonnante basse et dense. Ces deux types de maquis partagent plusieurs espèces végétales. La différence est principalement due à la hauteur de la végétation et la présence de certains pieds d’arbres isolés dans le maquis haut. L’amélioration du maquis bas par la plantation des arbres et la réduction du pâturage qui exerce une pression continue sur ce milieu atténuerait le contraste du paysage. La présence d’effets de lisière et de la proximité de la forêt (fragmentation au sens strict) d’intensité variable selon les guildes devrait être prise en considération. Par exemple, dans le cas du Pic épeichette, la seule espèce qui a répondu significativement à l’indice de proximité, planter de petites parcelles de forêt dans le maquis (marche-pieds), même si les densités des arbres ne soient pas élevées, devrait améliorer la connectivité structurale et aider cette espèce à persister dans les fragments d’habitat isolés. Le deuxième volet de ma thèse avait pour objectif de contribuer au développement d’outils nécessaires à la conservation des forêts de chênes du nord-ouest tunisien en se focalisant sur la réponse des espèces les plus sensibles à la dégradation de l’habitat forestier à l’échelle locale. Par dégradation, je référais à la collecte de bois mort, à l’abattage des grands arbres et au pâturage par le bétail. Je me suis basé sur la notion des seuils écologiques pour quantifier les besoins des espèces d’oiseaux les plus exigeants termes d’habitat forestiers. Les valeurs obtenues m’ont permis de proposer aux gestionnaires des valeurs pratiques qui pourraient être utilisées comme référence pour l’identification et la gestion des parcelles forestières. Ainsi, les seuils de 650 tiges ha-1 d'arbres (dhp >30 cm), 207 tiges ha-1 de chicots (fig.3), 213 tiges ha-1 de bois mort par terre et une canopée maintenue à 75 % devrait être respectés lors de l’application d’un éventuel traitement sylvicole. Ces chiffres correspondaient aux seuils les plus élevés des différentes espèces cibles notamment (le Pic épeiche, Pic de Levaillant, Pic épeichette, le Gobe mouche de l’Atlas et Grimpereau des jardins) assurant une détectabilité de 0,9. Les parcelles forestières ayant des valeurs plus élevées que ces dernières pourraient être exploitées tout en respectant les besoins des espèces les plus sensibles. Les seuils de nidification peuvent être plus élevés que ceux liés à la simple occurrence des espèces. Je me suis donc intéressé aux choix de la réponse biologique pour exprimer les seuils. Est-il plus prudent de se fier aux besoins de nidification plutôt qu’à ceux liés à la simple occurrence ? Cette question a été abordée à travers la modélisation de l’habitat de nidification de deux espèces de pic notamment le Pic épeiche et le Pic de Levaillant. Bien que ces deux espèces, préfèrent le bois mort et les grands arbres dhp > 40 cm comme substrat de nidification (fig.5), j’ai trouvé une différence concernant la quantité de ces éléments. Le Pic épeiche est plus exigent que le Pic de Levaillant dans la sélection de la zone de nidification. En effet, les sites de nidification ont une densité plus importante de grands arbres que les sites où l’espèce a été simplement détectée. Par conte aucune différence entre les deux types de sites n’a été trouvée chez le Pic de Levaillant. Ce résultat complique la tâche des gestionnaires dans la mesure où on ne peut pas vraiment trancher. D’une part, les seuils de nidification ne sont pas toujours plus élevés que ceux liés à l’occurrence (cas du Pic de Levaillant) et d’autre part, on doit en tenir compte puis qu’une différence a été trouvée. Cette tâche pourrait être plus complexe si on s’intéresse à d’autres paramètres biologiques comme le succès reproducteur. En tenant compte de l’effort déployé pour la mesure des différents paramètres biologiques et du choix de l’espèce cible, je pense que se fier aux besoins de nidification des espèces cibles serait plus sécuritaire pour la conservation des écosystèmes forestiers. J’encourage aussi l’utilisation de plusieurs espèces sensibles plutôt qu’une seule espèce afin de minimiser le risque de sous-estimer les besoins des espèces les plus sensibles.
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We evaluated the conditions under which patch size effects are important determinants of local population density for animals living in patchy landscapes. This information was used to predict when patch size effects will be expected to occur following habitat loss and fragmentation. Using meta-analysis, we quantitatively reviewed the results of 25 published studies that tested for a relationship between patch size and population density. Patch size effects were strong for edge and interior species (negative and positive patch size effects, respectively), but negligible for generalist species that use both edge and interior habitat. We found significant differences in mean patch size effects between migratory and residential species, between herbivores and carnivores, and among taxonomic groups. We found no evidence that patch size effects were related to landscape characteristics such as the proportion of landscape covered by habitat, median patch size, or the scale at which a study was conducted. However, species in the Western Hemisphere tended to have larger absolute effect sizes, and eastern species tended to be more variable in their response. For landscapes undergoing habitat loss and fragmentation, our results predict the following: (1) among generalist species that use both the edge and the interior of a habitat patch, the decline in population size associated with habitat destruction should be accounted for by pure habitat loss alone; (2) for interior species, the decline in population size associated with habitat fragmentation per se will be greater than that predicted from pure habitat loss alone; (3) for edge species, the decline in population size will be less than that predicted by pure habitat loss alone; (4) these relative effects will not be influenced by the extent of habitat loss, but they will be affected by the pattern of habitat when large or small patches are preferentially removed; and (5) as loss and fragmentation increase within a landscape, migratory species will generally suffer less of a decline in population size than resident species.
Article
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The abundance and distribution of corvids (Common Raven, Corvus corax; Hooded Crow, C. corone; Jackdaw, C. monedula; Black-billed Magpie, Pica pica; and European Jay, Garrulus glandarius) were studied across a gradient from a landscape dominated by agricultural land to a landscape dominated by forest in south-central Sweden. The total density and the predation rate on dummy nests increased as the proportion of agricultural land increased. This supports the suggestion that the density of corvids increases as forest becomes fragmented and intermixed with agricultural land, causing an increase in nest predation in small forest fragments. However, the different species responded differently to the proportion of forest in the landscape. The two forest-living corvids, the Jay and Raven, were absent from small forest fragments in a matrix of agricultural land and mainly preyed upon dummy nests inside the large forest fragments. Thus, both of these species were habitat specialists restricted to forests. Three corvids basically inhabit agricultural land, the Hooded Crow, Jackdaw, and Magpie. The Jackdaw and the Magpie showed a strong preference for agricultural land and they mainly preyed upon dummy nests in agricultural land. On the other hand, the density of Hooded Crows was higher in landscapes with a mixture of agricultural land and forest than in landscapes dominated by either agricultural land or forest, indicating a use of both agricultural land and forest. Further, Hooded Crows regularly preyed upon nests in both forest habitat and agricultural land; it is a habitat generalist. Therefore, the Hooded Crow was the most important species in the corvid family, causing increased predation pressure close to forest-farmland edges and in small forest fragments surrounded by agricultural land.
Article
Traditionally, ecologists interested in habitat edges have focused on edge‐related gradients in patterns of species richness or abiotic variables. Here, however, we take a different perspective, attempting to synthesize recent empirical results concerning the effects of habitat edges on population dynamics with contemporary theoretical developments to outline the ways in which species interactions, and the dynamics of the communities in which they are embedded, can be changed by habitat edges. We find a striking convergence between empirical notions of a patch's core area and analytical results from partial differential equation models. A review of both empirical and theoretical studies suggests four general classes of mechanisms through which habitat edges can have similar impacts on dissimilar types of species interactions. Specifically, we focus on edges' roles as dispersal barriers or filters, edges' influences on mortality, edges' involvement in spatial subsidies (in which dispersers' intrapatch impacts are maintained by their activities in other habitats), and edges' roles as generators of novel interactions. For each class of edge‐mediated effects, we provide examples of how one can use spatial modeling to address the relevant questions on these topics, which together form a key link between community dynamics and landscape structure.
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This book had its origin when, about five years ago, an ecologist (MacArthur) and a taxonomist and zoogeographer (Wilson) began a dialogue about common interests in biogeography. The ideas and the language of the two specialties seemed initially so different as to cast doubt on the usefulness of the endeavor. But we had faith in the ultimate unity of population biology, and this book is the result. Now we both call ourselves biogeographers and are unable to see any real distinction between biogeography and ecology.
Article
Riparian areas in western North America have been characterized as centers of avian diversity, yet little is known about the ways that native species in streamside habitats are affected by development nearby. To address this issue, we examined patterns of habitat use by birds during the 1995-1997 breeding seasons at 16 lowland riparian sites representing an urban-to-rural gradient. As development increased, riparian woodlands tended to have fewer native trees and shrubs, less ground and shrub cover, higher tree densities, and greater canopy closure. Bird species richness also declined as urbanization increased in the surrounding landscape. Canonical correspondence analysis (CCA) revealed that measures of settlement intensity best explained variation in habitat use by riparian birds, although some residual variation was accounted for by differences in woodland understory features. Migrant and low-nesting species were associated with lower-than-average levels of development, whereas resident and cavity-nesting species tended to increase with urbanization. In partial CCA analyses, however, local habitat variables explained twice the variation that measures of settlement did; nearly half of all explained variation could be attributed to local and landscape variables simultaneously. For avian guilds based on migratory, nesting, and foraging behavior, regression analyses showed that the best variables for explaining patterns of habitat use were usually those that reflected levels of urbanization, particularly at broad scales. When the effects of local habitat variation were removed, however, the best variables for explaining residual variation in habitat use tended to describe development at relatively fine scales, especially for species that nested or foraged low for insects or seeds. These species were also the most sensitive to human trail use. Our analyses indicated that bird communities and local habitat conditions in riparian areas were both affected by development in the surrounding landscape. It may be possible to mitigate the negative impacts of human settlement on native birds in streamside woodlands by maintaining or restoring vegetation structure and composition, and by imposing limits on human recreational activity in these habitats.
Article
Deforestation in Jamaica, according to the United Nations (FAO/UNEP) and other sources, is occurring at an annual rate of about 3%. The Ministry of Agriculture claims that the national forested area is actually increasing rapidly. A survey of humid tropical forests in Jamaica, carried out by the author in 1986, indicates a 3.3% per annum rate of deforestation for 1980-1986. But, despite significant commercial lumber production, large clear fellings are rare and most modification of the forest is due to expansion of small-scale farming (including Cannabis sativa) and pastoral activity. As uncontrolled deforestation is adversely affecting watersheds and inducing serious flooding, some form of control and management is urgently required.-from Author
Chapter
This chapter discusses butterfly metapopulation dynamics. The metapopulation concept is swiftly spreading into common usage in population and conservation biology. The term “metapopulation” itself is not new, as it was coined by Richard Levins, 25 years ago. It took 20 years before biologists at large began to employ it. The model is based on a generalized incidence function and it provides a simple yet realistic and practical means of modeling real metapopulations. Melitaea cinxia is one of the many European butterflies that have declined during the past decades. More than half of the species not forming local populations failed also to satisfy the second condition, because they have large “mainland” populations. During the past 10 years the metapopulation approach has been applied in several butterfly studies in both North America and Europe. Migration between habitat patches is a key process in metapopulation dynamics. It is not generally agreed that metapopulation dynamics in the sense described in this chapter are often critical for long-term persistence of butterflies and other taxa. It is difficult to disagree about rampant environmental changes, and it is equally clear that many populations have been exterminated because the habitat became unsuitable. Melitaea cinxia may be exceptional, but until a score of other equally comprehensive studies have been completed, there is no reason to rush to a general conclusion.
Book
Discover what you can do with R! Introducing the R system, covering standard regression methods, then tackling more advanced topics, this book guides users through the practical, powerful tools that the R system provides. The emphasis is on hands-on analysis, graphical display, and interpretation of data. The many worked examples, from real-world research, are accompanied by commentary on what is done and why. The companion website has code and datasets, allowing readers to reproduce all analyses, along with solutions to selected exercises and updates. Assuming basic statistical knowledge and some experience with data analysis (but not R), the book is ideal for research scientists, final-year undergraduate or graduate-level students of applied statistics, and practising statisticians. It is both for learning and for reference. This third edition expands upon topics such as Bayesian inference for regression, errors in variables, generalized linear mixed models, and random forests. © Cambridge University Press 2003 and John Maindonald and W. John Braun 2007, 2010.
Article
We sampled understory hummingbirds in Amazonian forest fragments from before isolation through nine yeats after isolation We recorded 377 captures of eight species in five I-ha fragments and four 10-ha fragments. The three species netted before isolation Phaethornis superciliosus, Phaethornis bourcieri, and Thalurania furcata, were nearly equally abundant at that time. After isolation abundance of P. bourcieri and T. furcata did not change, but P. superciliosus became nearly twice as common. Five additional species that were netted only after isolation represented about 10% of the post-isolation sample. The species recorded only after isolation were forest species usually found above the levels of nets;fragments were not colonized by nonforest species. Use of fragments did not differ between 1- and 10-ha fragments. The landscape surrounding the fragments included active cattle pasture, abandoned pasture, and Cecropia-dominated second growth, but this variation had little effect on use of fragments by hummingbirds. The results suggest that these understory hummingbirds can persist in a matric of fragments, secondary growth, and large forest patches. This response is much different than that of the insectivorous birds that dominate the understory bird community at the site, which are much more vulnerable to fragmentation.
Article
Ecological processes near habitat edges often differ from processes away from edges. Yet, the generality of ''edge effects'' has been hotly debated because results vary tremendously. To understand the factors responsible for this variation, we described nest predation and cowbird distribution patterns in forest edge and forest core habitats on 36 randomly selected plots in three states in the midwestern United States. We tested four hypotheses that may explain the variation and mechanisms responsible for edge effects among the 36 plots: (1) the landscape context, (2) the local predator community, (3) the local bird (host-prey) community, and (4) the nest site microhabitat structure. We used artificial nests baited with quail and clay eggs to determine nest predation patterns and predators and used point count surveys to determine cowbird and host abundance in forest edge and forest core habitats. Raccoons, opossums, canids, and birds accounted for most predation of artificial nests. Neither local host abundance nor mean nest concealment of artificial nests significantly influenced nest predation rates in habitat edge or in habitat core. Nest predation was significantly greater in highly fragmented landscapes than in unfragmented landscapes and was significantly higher in edge habitats than in core habitats. However, detection of edge effects varied, depending upon landscape type. Higher predation rates in edge habitats were detected in highly and moderately fragmented landscapes, but not in unfragmented landscapes. Both mammalian and avian predator groups contributed to higher predation rates along edges in highly and moderately fragmented landscapes. Cowbird abundance was significantly related to host abundance, but the effect of hosts varied depending upon habitat type. In edge habitats, cowbird abundance was negatively associated with host abundance in all three landscapes studied. By contrast, cowbird abundance was positively associated with host abundance in core habitats. Once the effects of host abundance were removed, cowbird abundance in core habitat was greater in highly fragmented landscapes than in moderately and unfragmented landscapes, but did not differ between the latter two. In edge habitat, cowbird abundance did not differ between landscapes, but abundance in edges tended to be highest in the highly fragmented landscape and lowest in the unfragmented landscape. Cowbird abundance did not vary between edge and core habitat in any of the landscapes studied. We suggest that the first approximation to predicting the impact of agricultural or permanently managed edges on forest songbird reproductive success is to assess habitat characteristics at the landscape scale. Given geographic location, local factors such as host abundance and predator composition should be assessed.
Article
The dispersal system of the neotropical tree Dunalia arborescens (Solanaceae) was examined in a montane mist forest in Jamaica. A total of 16 species of birds representing 14 genera and eight families were recorded feeding on D. arborescens fruits. The most common species feeding were the stripe-headed tanager (Spindalis zena), greater antillean bullfinch (Loxigilla violacea), and the rufous-throated solitaire (Myadestes genibarbis), accounting for 66 percent of the total visits. Intraspecific encounters dominated actions, and interspecific interactions were minimal, the latter was probably due to a superabundance of food and, to a lesser degree, to differences in foraging and feeding behavior. In general, birds arrived and left the feeding tree as individuals or as groups of several individuals of one species. No mixed species flocks were observed arriving or leaving the fruiting tree. Observations on color-marked individuals and on all species feeding on D. arborescens showed that the amount of fruit dependency varied from almost 100 percent in the stripe-headed tanager and the greater antillean bullfinch to less than 30 percent in the greater antillean elaenia (Elaenia fallax) and the jamaican oriole (Icterus leucopteryx). The birds involved exploited a variety of fruits throughout the year, but at any one time ate fruit of a few species. What determined the diet at any one time depended on the fruiting phenology, commonness of tree, large crop size, and individual preferences. The fruiting period of the different feeding trees in the study area ranged from complete overlap to no overlap; as the number of fruits of one species decreased, the number of another species increased. Staggered fruiting may enable these trees to take advantage of the same bird populations at different times and thus relieve competition for seed dispersers. The high reproductive potential of D. arborescens expressed in the abundance of fruits with many seeds, and the presence of a number of different dispersers of widely different sizes, degree of dependency on fruits and foraging behavior suggest that this tree is opportunistic in nature. It is a species found in forest edges, clearings, and other habitats that are spatially unpredictable. Premium is placed in the dispersal of seeds as widely as possible by the greatest variety of dispersers, because the tree's survival depends upon the rapidity with which it can colonize bare ground and gaps in the primary forest.
Article
To help fill the gap in detailed knowledge of avian community structure in tropical forests, we undertook a census of a 97-ha plot of floodplain forest in Amazonian Peru. The plot was censused over a 3-mo period spanning the 1982 breeding season. The cooperative venture entailed @?12 person-months of effort. Conventional spot-mapping was the principal method used, but several additional methods were required to estimate the numbers of non-territorial and group-living species: direct counts of the members of mixed flocks, saturation mist-netting of the entire plot, opportunistic visual registrations at fruiting trees, determination of the average size of parrot flocks, color banding of colonial icterids, etc. Two hundred forty-five resident species were found to hold territories on the plot, or to occupy all or part of it. Seventy-four additional species were detected as occasional-to-frequent visitors, wanderers from other habitats, or as migrants from both hemispheres. By superimposing territory maps or the areas of occupancy of individual species, we determined that point (alpha) diversities exceeded 160 species in portions of the plot. About 1910 individual birds nested in 100 ha of this floodplain forest, making up a biomass conservatively estimated at 190 kg/km^2. The total number of breeding birds was equivalent to that in many temperate forests, but the biomass was about five times as great. Predominantly terrestrial granivores contributed the largest component of the biomass (39%), followed by largely arboreal frugivores (22%). Considering only insectivores, the biomass (34 kg/km^2) is somewhat less than that in the forest at Hubbard Brook, New Hampshire (40 kg/km^2), although it is greater (55 kg/km^2) if one includes omnivores. The number of insectivores was considerably less than at Hubbard Brook, due to their 60% larger average body size (32 vs. 20 g). Even though a large majority of the species were patchily distributed, the 97-ha plot was found to include 99% of the bird species that regularly occupy mature floodplain forest at Cocha Cashu. The most abundant species occupied territories of 4-5 ha, and 84 species (26%) had population densities of @<1 pair per square kilometre. Of these, 33 (10% of the total community) were judged to be constitutively rare (i.e., having low population densities everywhere), rather than being merely locally rare. Many of these are predicted to be vulnerable to forest fragmentation and disturbance. Comparison of these results with those from other tropical forests proved difficult due to a lack of standardized methodology.
Article
Conversion of land to grow crops, raise animals, obtain timber, and build cities is one of the foundations of human civilization. While land use provides these essential ecosystem goods, it alters a range of other ecosystem functions, such as the provisioning of freshwater, regulation of climate and biogeochemical cycles, and maintenance of soil fertility. It also alters habitat for biological diversity. Balancing the inherent trade-offs between satisfying immediate human needs and maintaining other ecosystem functions requires quantitative knowledge about ecosystem responses to land use. These responses vary according to the type of land-use change and the ecological setting, and have local, short-term as well as global, long-term effects. Land-use decisions ultimately weigh the need to satisfy human demands and the unintended ecosystem responses based on societal values, but ecological knowledge can provide a basis for assessing the trade-offs.
Book
The chapter introduces the idea that the relationships between natural conditions and the outcome of an observation may be deterministic, random, strategic or chaotic, and that numerical ecology addresses the second type of data; it describes the role of numerical ecology among the various phases of an ecological research. The chapter includes discussion of the following topics: spatial structure, spatial dependence, and spatial correlation (independent observations, independent descriptors, linear independence, independent variable of a model, independent samples, origin of spatial structures, tests of significance in the presence of spatial correlation, and classical sampling and spatial structure), statistical testing by permutation (classical tests of significance, permutation tests, alternative types of permutation tests), computer programs and packages, ecological descriptors (i.e. variables: mathematical types of descriptors, and intensive, extensive, additive, and non-additive descriptors), descriptor coding (linear transformation, nonlinear transformations, combining descriptors, ranging and standardization, implicit transformation in association coefficients, normalization, dummy variable coding, and treatment of missing data (delete rows or columns, accommodate algorithms to missing data, estimate missing values). The chapter ends on a description of relevant software implemented in the R language.
Article
Many recent studies have addressed the effects of patch size and isolation on bird communities in highly fragmented landscapes, but the importance of landscape composition in more forested landscapes remains poorly understood. The objectives of our study were (1) to determine the effects of two structurally and temporally distinct disturbance types (agriculture and silviculture) and extent of disturbance (percentage of disturbance within 1.0 km) on avian community structure within forested landscapes, and (2) to investigate underlying mechanisms responsible for associations between landscape composition and avian communities. Differences in microhabitat, microclimate, and nesting success among landscapes were examined as possible mechanisms. Breeding bird communities in central Pennsylvania (USA) were surveyed twice per year during 1997-1999 at 34 sites within contiguous mature forest, which represented a range of disturbance extent (4-59% nonforest cover within 1.0 km). Each site was in a forested landscape containing predominantly agricultural or silvicultural disturbances (n = 17 each). Our results indicate that type of disturbance within landscapes influenced bird community composition and relative abundance more than extent of disturbance. Compared to forests within landscapes disturbed by silviculture, forests within landscapes disturbed by agriculture, irrespective of the extent of disturbance, had fewer forest-associated species, long-distance migrants, forest-canopy and forest-understory-nesting species, and greater numbers of edge-associated species, including avian nest predators and Brown-headed Cowbirds (Molothrus ater). Fewer species and guilds were associated with the extent of disturbance within a landscape or interactions between disturbance type and extent. Abundances of edge-associated species, residents, and forest-canopy nesters increased with increasing amounts of disturbance within forested landscapes. Local variation in microhabitat and microclimate among landscapes did not explain observed differences in avian community structure. However, nesting success was greater and numbers of some avian and small mammalian nest predators were lower in stands within forested landscapes disturbed by silviculture than in forested landscapes disturbed by agriculture. Nesting success was not associated with the extent of a given disturbance type within landscapes. These results demonstrate that, even within forested landscapes, the types of disturbance can influence avian community structure and, thus, should be considered in conservation and forest management plans. In particular, agricultural disturbances within forested landscapes seemed to negatively affect bird communities in adjacent forests more than silvicultural disturbances. Both species richness and abundance of forest-associated species were greater on sites with higher levels of nesting success. Thus, differences in nesting success resulting from altered interactions between nest predators and nesting birds may be an important underlying mechanism of avian community structure and organization at the landscape scale.
Article
Significant changes in land-use practices, combined with increasing levels of fragmentation within the last century, have made the landscape an important and relevant scale for studies of wildlife ecology and management. However, relatively few landscape-level investigations have explicitly addressed characteristics of the landscape matrix. Even fewer studies have examined how specific land uses within the matrix affect wildlife, and most of these confound the amount and type of disturbances within study designs. Recent research demonstrates that land uses can differ markedly in their effects on wildlife in near-by forests or grasslands-even in landscapes with comparable amounts of habitat. In particular, urban or residential development within the matrix can alter diversity or abundance of some species and can depress avian nesting success even in large forest tracts. Simply the presence of certain land uses, such as agricultural openings, within forested regions can negatively impact some animal communities. Collectively, these studies provide strong evidence that land uses within forested and fragmented landscapes are important influences on wildlife populations and communities. Consequently, biologists and managers involved in the design and management of natural areas, parks, reserves, and other public lands should carefully consider types of land uses occurring within or adjacent to their boundaries.
Article
Metapopulation biology is concerned with the dynamic consequences of migration among local populations and the conditions of regional persistence of species with unstable local populations. Well established effects of habitat patch area and isolation on migration, colonization and population extinction have now become integrated with classic metapopulation dynamics. This has led to models that can be used to predict the movement patterns of individuals, the dynamics of species, and the distributional patterns in multispecies communities in real fragmented landscapes.
Article
The pervasive influence of island biogeography theory on forest fragmentation research has often led to a misleading conceptualization of landscapes as areas of forest/habitat and 'non-forest/non-habitat' and an overriding focus on processes within forest remnants at the expense of research in the human-modified matrix. The matrix, however, may be neither uniformly unsuitable as habitat nor serve as a fully-absorbing barrier to the dispersal of forest taxa. In this paper, we present a conceptual model that addresses how forest habitat loss and fragmentation affect biodiversity through reduction of the resource base, subdivision of populations, alterations of species interactions and disturbance regimes, modifications of micro- climate and increases in the presence of invasive species and human pressures on remnants. While we acknowledge the importance of changes associated with the forest remnants themselves (e.g. decreased forest area and increased isolation of forest patches), we stress that the extent, intensity and permanence of alterations to the matrix will have an overriding influence on area and isolation effects and emphasize the potential roles of the matrix as not only a barrier but also as habitat, source and conduit. Our intention is to argue for shifting the examination of forest fragmentation effects away from a patch-based perspective focused on factors such as patch area and distance metrics to a landscape mosaic perspective that recognizes the importance of gradients in habitat conditions.
Article
Aim We analysed presence/absence data for understorey bird species in rain forest fragments sampled from 1979 through 2001. Here we consider extinctions between 1992, when most fragments had been isolated for at least 8 years, and 2001. Our objectives were to determine whether high extinction rates documented soon after isolation continued through up to 20 years after isolation, and to examine fragment size and landscape effects on extinction. Location Biological Dynamics of Forest Fragments Project, near Manaus, Brazil. Methods Through 1992, birds were surveyed with standardized mist net sampling in ten 1- to 100-ha fragments. We repeated the mist net protocol in 2000–01. We also added remote taping of the dawn chorus and tape playback surveys for species captured in 1991–92 but not in 2000–01. Results Between 1992 and 2001, 37 species went extinct in at least one fragment. As expected, extinction rate decreased with increasing fragment size. Over 30% of species went extinct in 1-ha fragments, compared to about 5% in 100-ha fragments. Extinction followed a predictable pattern: most species lost from 100-ha fragments between 1992 and 2001 had already gone extinct in smaller fragments before 1992. Despite extinctions, fragments gained species between 1992 and 2001, apparently due to species moving through the developing second growth matrix. Fragments surrounded by old second growth had lower extinction rates than predicted based on fragment size alone. Main conclusions Sequential extinctions occurred for at least 20 years. Some additional species previously lost from smaller fragments may continue to go extinct in 100-ha fragments. At the same time, species assemblages in 1- and 10-ha fragments mostly reflect second-growth dynamics by 20 years after isolation. High species loss predicted from the first few years after isolation has not occurred, almost certainly because of recolonization.
Article
There is a dire need to predict the vulnerability of tropical forest biotas to habitat fragmentation I tested the efficacy of seven ecological traits (body size Iongeuity, fecundity, trophic level, dietary specialization, natural abundance in rain forest and abundance in the surrounding habitat matrix) for predicting responses of 16 nonflying mammal species to rain forest fragmentation in tropical QueenslaM Australia An ordination analysis revealed that most (84%) of the variation in traits was described by two axes, the first separating rand K‐selected species, and the second discriminating rare species with specialized diets from common species with generalized diets. Using multiple regression analysis, the two ordination axes explained 51.7% of variation in mammal extinction proneness (F = 9.96 P = 0.009). Howem, univariate tests revealed tbat a single trait abundance in the mawas a betterpredictor of vulnerability (r ² = 63.8%, F = 24.69, P < 0.001). Partial correlations demonstrated that once the effects of matrix abundance tuete remove4 no other traits or ordination axes were significant predictors of extinction proneness. These results highlight the importance of tolerance of modijied habitats in determining survival of nonpying mammals in tropical forest fragments. Species tbat traverse or exploit modaxied habitats tend to remain stable or inmase in fragments whereas those tbat avoid these habitats often disappem The implications of these findings for hopical forest conservation are discussed.