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Common names, scientific names, families, origin (native or exotic), and tolerance to exploit urbanized areas (according to Litteral & Wu 2012) of birds observed during the study period in Curitiba city, southern Brazil.

Common names, scientific names, families, origin (native or exotic), and tolerance to exploit urbanized areas (according to Litteral & Wu 2012) of birds observed during the study period in Curitiba city, southern Brazil.

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This paper compares the proportion of urban tolerant birds in the urban avian community and the amount of built-up areas, mostly impervious surface, as indicators of urbanization on patterns of bird species richness in a southern Brazilian city. From September to December 2013 (breeding season), bird surveys were conducted in 120 squares of 100 ha...

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... families Icteridae and Picidae can also be highlighted because of their representativeness (5 species each) in the surveys. Among the 102 birds identified, 13 were considered urban tolerant species, including three nonnatives (Rock Dove, Common Waxbill, and House Sparrow) ( Table 1). Effects of urbanization on the avian community in a southern Brazilian city Abilhoa & Amorin not statistical different between low and intermediate urbanized sites (P > 0.05). ...
Context 2
... families Icteridae and Picidae can also be highlighted because of their representativeness (5 species each) in the surveys. Among the 102 birds identified, 13 were considered urban tolerant species, including three nonnatives (Rock Dove, Common Waxbill, and House Sparrow) ( Table 1). Effects of urbanization on the avian community in a southern Brazilian city Abilhoa & Amorin not statistical different between low and intermediate urbanized sites (P > 0.05). ...

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... For instance, birds are known for their movements between forested patches, depending on the characteristics of the surrounding matrix and the distance between patches (Marini 2010). Some A. angustifolia dispersers have been observed in altered environments, including P. frontalis (Silva et al. 2014), A. pretrei (Torres 2020), P. maximiliani, and Cyanocorax chrysops (Vieillot) (Abilhoa and Amorin 2017). On the other hand, mammals tend to be more susceptible to fragmentation, and while certain species can persist in fragmented areas, such as small rodents, N. nasua, Didelphis albiventris (Lund), Sapajus nigritus (Goldfuss), and Hydrochoerus hydrochaeris (L.) (DeMattia et al. 2006;Almeida et al. 2008;Hendges et al. 2017;Rocha et al. 2022), others cannot. ...
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... With the results obtained, we understand that the landscape structures explain high values for the ADI, H and NDSI in more conserved areas (Abilhoa & Amorin, 2017;Blair, 1996;Filloy et al., 2019). We expected this result since areas with intense urbanization show a decrease in diversity and species richness compared with natural areas. ...
... According to our results, urban areas that have native areas or that are close to them tend to generate higher values for the indices ADI, H and NDSI. These results may be an indication that the closer to natural areas, the greater the species diversity (Fuller et al., 2015;Machado et al., 2017;Mammides et al., 2017), which is in line with the results of other studies in different parts of the globe, which have analysed how areas of greater and lesser vegetation cover influence bird richness, diversity and abundance (Abilhoa & Amorin, 2017;Blair, 1996;Clergeau et al., 1998;Joo et al., 2011). In a study in England, for instance, it was shown that urban areas with a large vegetation cover, including parks with native areas and private gardens, tend to have more bird species and the number of individuals (Mason, 2006). ...
... Both Donaldson et al. (2007) and Burton (2007) pointed out that some species prefer urbanized places because food or vegetation cover for refuge or nesting are more available. In this sense, most bird species in urban environments have developed greater ecological plasticity, which makes them more tolerant to environmental changes (Abilhoa and Amorin 2017). However, undeveloped areas in the lagoon may represent refuges and breeding niches for sensitive species, particularly during the migration and wintering period, given the location of the wetland (Berlanga et al. 2019). ...
... We observed that the richness of bird species decreased with the proximity to streets and the increase of urbanization adjacent to the sampling sites, which is consistent with what was reported by Abilhoa and Amorin (2017). In this study, site 11, located in the northwest area of the lagoon, was distinguished by a high percentage of urbanization (55.0%) and by the lowest number of species (11) and sightings (21). ...
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... On the other hand, urban avoiders are usually migratory, insectivorus, and forest specialists in habitat selection (stenobionts). Urban exploiters are often ecologically flexible generalists (eurobionts) associated with 'open' habitats (Chace and Walsh, 2006;Marzluff, 2016;Abilhaa and Amorin, 2017;Lepczyk et al., 2017). ...
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Granivores were the most important feeding guild, comprising more than half of all birds in Windhoek. Frugivores (26 %) were more numerous than insectivores (19 %). Birds nesting in trees and/or in shrubs comprised two thirds of all birds. Surprisingly, few differences in the structure of feeding and nesting guilds were recorded among the four urban habitats. Windhoek avifauna is similar in dominance structure to avifauna in other southern African cities and towns, where sparrows, doves/pigeons, bulbuls and mousebirds dominate, and with granivores being the main feeding guild. Species richness declines and bird abundance increases along urban gradient (towards the city centre). Resumen Estructura de los conjuntos de aves reproductoras en la ciudad de Windhoek, Namibia. Se empleó el método del transecto lineal para contar aves en cuatro hábitats urbanizados de la ciudad de Windhoek (Namibia). La mayoría de los recuentos se realizaron entre julio y octubre, en el periodo 2012-2014. Se seleccionaron 12 transectos con una longitud total de 86 km aproximadamente en lugares que representaban los principales hábitats urbanos: zonas residenciales (centro de la ciudad, suburbios en tierras bajas, suburbios en tierras altas y periferia de la ciudad), campos de deporte y una moderna zona industrial. En total se registraron 80 especies de aves (excluidos los visitantes paleárticos). Se calcularon las densidades de población lineales y la dominancia de todas las especies. Seis especies se clasificaron como dominantes: gorrión común, bulbul de ojos rojos, tejedor enmascarado 20 Arxius de Miscel·lània Zoològica, 21 (2023): 19-38 Kopij meridional, paloma reidora, estornino pinto y pájaro ratón dorsiblanco. Su abundancia numérica acumulada comprende el 54,2 % de todas las especies reproductoras. El grupo de especies dominantes varió notablemente entre los distintos transectos. Los granívoros fueron el gremio alimentario más importante, con más de la mitad de todas las aves de Windhoek. Los frugívoros (26 %) resultaron más numerosos que los insectívoros (19 %). Las aves que anidan en árboles y/o arbustos representaron dos terceras partes del total de aves. Sorprendentemente, se registraron pocas diferencias en la estructura de los gremios de alimentación y nidificación entre los cuatro hábitats urbanos. La avifauna de Windhoek presenta una estructura de dominancia similar a la de otras ciudades y pueblos del sur de África, donde dominan los gorriones, las palomas, los bulbules y los pájaros ratones, siendo los granívoros el principal gremio de alimentación. A lo largo del gradiente urbano, la rique-za de especies disminuye y la abundancia de aves aumenta hacia el centro de la ciudad. Palabras clave: Ecología urbana, Densidades de población, Comunidades de aves Resum Estructura dels conjunts d'ocells reproductors a la ciutat de Windhoek, Namíbia. Es va utilitzar el mètode del transsecte lineal per comptar ocells en quatre hàbitats urbanitzats de la ciutat de Windhoek (Namíbia). La majoria dels recomptes es van fer entre juliol i octubre, en el període 2012-2014. Es van seleccionar 12 transsectes amb una longitud total de 86 km aproximadament en llocs que representaven els principals hàbitats urbans: zones residen-cials (centre de la ciutat, suburbis en terres baixes, suburbis en terres altes i perifèria de la ciutat), camps d'esport i una moderna zona industrial. En total es van registrar 80 espècies d'ocells (excloent-ne els visitants paleàrtics). Es van calcular les densitats de població lineals i la dominància de totes les espècies. Sis espècies es van classificar com a dominants: pardal comú, bulbul d'ulls vermells, teixidor emmascarat meridional, colom rialler, estornell comú i ocell ratolí dorsiblanc. L'abundància numérica acumulada d'aquestes espècies com-prèn el 54,2 % de totes les espècies reproductores. El grup d'espècies dominants va variar notablement entre els diferents transsectes. Els granívors van ser el gremi alimentari més important, amb més de la meitat de tots els ocells de Windhoek. Els frugívors (26 %) van ser més nombrosos que els insectívors (19 %). Els ocells que nien en arbres i/o arbustos van representar dues terceres parts del total d'ocells. Sorprenentment, es van registrar poques diferències en l'estructura dels gremis d'alimentació i nidificació entre els quatre hàbitats urbans. L'avifauna de Windhoek presenta una estructura de dominància similar a la d'altres ciutats i pobles del sud d'Àfrica, on dominen els pardals, els coloms, els bulbuls i els ocells ratolins. Els granívors són el principal gremi d'alimentació. Al llarg del gradient urbà, la riquesa d'espècies disminueix i l'abundància d'ocells augmenta cap al centre de la ciutat.
... Although some authors (e.g. Silva, 1995;Abilhoa & Amorin, 2017) consider the species as not tolerant to urbanization (i.e. highly dependent on forest habitats), we found the nest in a highly urbanized area at the UFJF campus. ...
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... In South America, studies about the impact of urbanization on bird assemblages are concentrated in the Pampas region and Northeastern region of Argentina (Leveau and Leveau 2004;Germain 2008;Garaffa et al. 2009;Filloy et al. 2015;Bellocq et al. 2017), in the Rainfall-Valdivian Forest of Chile (Silva et al. 2015(Silva et al. , 2016, in the Atlantic Forest of Brazil (Brummelhaus et al. 2012;Abilhoa and Amorin 2017), and in the Puna of Bolivia (Villegas and Garitano-Zavala 2010). All of these studies reported a significant loss of bird species richness with increased urbanization. ...
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... So, the spatial heterogeneity in a city may also shape patterns of bird richness (Abilhoa & Amorin, 2017;Silva, García, Estay, & Barbosa, 2015). Under this reasoning, our main hypothesis is that the amount of impervious surface would be the main driver of species richness, having negative effects on the richness of all bird functional groups, except for omnivore's species. ...
... Impervious surface is one of the main drivers shaping bird communities in cities, reducing species abundance and richness through direct changes in resources and habitat (Bellocq et al., 2017;Lepczyk et al., 2017b). In our study, impervious surface was responsible for negatively affecting overall bird richness and richness of all functional groups, a result that agrees with previous studies and our hypothesis (Abilhoa & Amorin, 2017;Sacco et al., 2015). We found that impervious surfaces in urban landscapes creates an inhospitable environment for most birds that depend on forest-specific resources, such as trees for woodcreepers (Dendrocolaptidae), and nesting sites for species that depend on cavities in deadwood (Picidae, Ramphastidae, Psittacidae). ...