Bird species richness across a Northern Andean city: Effects of size, shape, land cover, and vegetation of urban green spaces

https://doi.org/10.1016/j.ufug.2021.127243Get rights and content

Highlights

  • Larger and more regular-shaped green areas increased bird species richness.

  • Less impervious surfaces and more grass-shrubs increased bird species richness.

  • Introduced trees’ dominance decreased bird species richness.

Abstract

Cities are human-dominated ecosystems where landscape transformation decreases biodiversity, a conservation concern when urbanization sprawls into biodiversity hotspots with high endemism. We aimed to evaluate the effects of site-specific features such as size and shape of green spaces, land cover, and vegetation on bird species richness in Medellín, Colombia, a city of Northern Andes (n = 44 urban green spaces sampled from February 2018 to February 2019). We found 255 plant species: 23 % of trees and 41 % of understory were native sensu stricto (local origin); most native species and individuals were in green spaces lacking vegetation management. Bird species richness (25.80 ± 8.05 resident species per sampling point; 83 resident species overall) increased towards larger and more regular-shaped urban green spaces (squared or rounded), with less percentage of impervious surfaces and more of grass–shrubs, and less influence of introduced trees in habitat structure (i.e. less crown coverage, basal area, and average height). Bird species richness also increased when richness or abundance of native understory vegetation sensu lato (local or regional origin) increased, but introduced trees dominance represented higher and most significant effects to explain bird species richness. Increasing edge effects across urban green spaces and human-related habitat transformation favoring non-native vegetation might represent significant constraints for enhancing local biodiversity in highly developed Andean cities.

Introduction

Cities reflect modern human life and its impacts on the planet. Besides topography and climate, human dynamics influence the composition and structure of cities, where natural landscapes are transformed into novel ecosystems with reduced and structurally simple green spaces (Aronson et al., 2017; Paz Silva et al., 2015; Shih, 2018). Non-native introduced vegetation dominates urban green spaces (Nielsen et al., 2013), which are mainly managed to improve public health and social interaction (Dooling et al., 2006; McDonnell, 2011; Wolch et al., 2014). Although some bird species benefit from non-native vegetation in cities that offer novel resources (Chace and Walsh, 2006; Jasmani et al., 2017), planted or naturalized vegetation has limited contribution in maintaining local biodiversity (Aronson et al., 2017; Chong et al., 2014).

Recent thinking in urban planning includes biodiversity conservation as a key factor to make cities sustainable (Botzat et al., 2016; Puppim De Oliveira et al., 2011; Threlfall and Kendal, 2018), but decision-makers might fail to implement better practices without ecological studies, as responses to urbanization depend on city characteristics and surrounding landscape (Aronson et al., 2014; Kowarik, 2011; Mcdonald et al., 2009). This is particularly challenging when cities are located in biodiversity hotspots with high endemism and species turnover such as the Tropical Andes (Cincotta et al., 2000; Rahbek et al., 2019), where urban bird studies are mainly species lists that have limited use in biodiversity conservation (Ortega-Álvarez and Macgregor-Fors, 2011).

Birds are well-known bioindicators in urban ecosystems (Macgregor-Fors et al., 2015; Marzluff et al., 2001; Mckinney, 2008) as alpha biodiversity measurements like species richness respond to green space features at local scales (Marzluff et al., 2001; Mckinney, 2008; Tryjanowski et al., 2017): larger and more regular-shaped urban green spaces (e.g. squared, rounded) are richer because they promote species persistence due to species–area relationships (Beninde et al., 2015; Fernández-Juricic and Jokimäki, 2001; Nielsen et al., 2013); they also mitigate urban environmental pressures and edge effects (Fernández-Juricic, 2004), whereas smaller and less regular-shaped green spaces may act as ecological traps for most sensitive taxa (Lepczyk et al., 2017), increasing risks of local extinction that reduce bird species richness.

The problem in highly developed Latin American cities is that green spaces are surrounded by impervious surfaces, making it difficult to manage the area and shape features of individual green spaces (Leveau et al., 2017; Ortega-Álvarez and MacGregor-Fors, 2009; Paz Silva et al., 2015). Therefore, most populated cities in the Northern Andes focus urban planning on ecological connectivity frameworks to mitigate the effect of habitat loss and fragmentation (Andrade et al., 2013), but local governments also might enhance plant richness and abundance to increase vegetation complexity structure, which is supposed to promote habitat heterogeneity and local biodiversity (Collas et al., 2017; Roy et al., 2012).

Managing site-specific features related to vegetation is an effective alternative to promote local biodiversity in small green spaces (Fernández-Juricic and Jokimäki, 2001; Morelli et al., 2017). Enhancing tree or understory species richness might increase bird species richness (Ferenc et al., 2014; Nielsen et al., 2013; Paker et al., 2014), as well as habitat heterogeneity, especially when this is driven by native vegetation and natural regeneration (Chace and Walsh, 2006; Fontana et al., 2011; Matthies et al., 2017; Threlfall et al., 2017; Yang et al., 2015). Thus, less human-managed urban green spaces resembling natural habitats of city surroundings usually increase local bird species richness via colonization of less tolerant species to urbanization (Callaghan et al., 2019; Fernández-Juricic, 2004; Marzluff, 2005).

Here, we present one of the first studies that evaluate effects of site-specific features on local bird diversity (response variable) in urban ecosystems of the Northern Andes, a region with growing urbanization–biodiversity conflicts (Bax and Francesconi, 2019). We performed an exploratory analysis expecting that, besides area and shape features, urban green spaces dominated by native understory and native tree species would increase bird species richness. We focused on a response variable and several predictors that could be easily accessible to urban planners, and thus, prone to be included in green space local management and biodiversity monitoring.

Section snippets

Study area

The municipality of Medellín is located along the Aburrá Valley in Colombian Central Andes (6° 15′ N, 75° 34′ W; Fig. 1), in the Tropical Andes biodiversity hotspot (Myers et al., 2000): 445 bird species and 2603 vascular plant species have been reported in the municipality between ca. 1450 and 3000 m a. s. l. (Alcaldía de Medellín, 2015). This hotspot with a high level of endemism is driven by the Andean uplift and the derived biogeographical complexity of Northwestern South America (Brumfield

Results

Urban green spaces ranged between 0.11 and 103.73 ha of size (9.44 ± 24.17 on average), and between 0.005 and 0.124 m−1 of perimeter/area ratio (0.059 ± 0.029), across a landscape with significant variation in percentage of trees, grass–shrubs, and impervious surfaces (Kruskal–Wallis test: F-value = 18.86, p-value <0.001). We found land cover differences particularly when comparing impervious surfaces (44.31 % ±23.83) with trees (25.85 % ±14.69; Wilcoxon rank sum test: adjusted p-value <0.001)

Discussion

Several studies have suggested that native vegetation can mitigate the negative effects of urbanization on local bird diversity (e.g. Chace and Walsh, 2006; Chong et al., 2014; Dale, 2018; Threlfall et al., 2017); thus, although we expected that bird species richness would respond to species–area relationships (Beninde et al., 2015; Fernández-Juricic and Jokimäki, 2001; Nielsen et al., 2013), we also expected that it would respond to richness or abundance of native trees and understory.

Conclusions

In a highly developed Andean city, features that best explained bird species richness across urban green spaces were size and shape of urban green spaces, percentage of impervious surfaces and grass–shrubs (artificial coverage and incipient natural regeneration, respectively), and dominance of introduced trees in habitat structure. The effect of features such as species richness or abundance of native trees and understory had lower effects on bird species richness, mainly due to their low

CRediT authorship contribution statement

Jaime A. Garizábal-Carmona: Conceptualization, Sampling design, Data acquisition- Curation- Analysis, Data interpretation, Writing- Original draft preparation, Visualization, Investigation. N. J Mancera-Rodríguez: Supervision, Validation, Writing- Reviewing and Editing

Funding

This research did not receive any specific grant from funding agencies in the public, commercial, or not-for-profit sectors.

Declaration of Competing Interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Acknowledgements

We thank the University of Antioquia Herbarium (HUA) and all their staff, especially Wilson Renfijo, Ricardo Callejas, Felipe Cardona, Álvaro Roldán, and Heriberto David. We also thank Paula Morales, Tomás Hinestroza, Samuel Monsalve, Andrés Mercado, Deysi Carmona, Wilson Rodríguez, Manuel Bernal, and Luisa Arboleda for supporting vegetation assessments, Natalia Ruiz and Luz Morales for GIS support, Victor Martínez-Arias for statistical support. We thank Benjamin Low and Amanda Colón for

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