Assessing ecological interactions in urban areas using citizen science data: Insights from hummingbird–plant meta-networks in a tropical megacity
Introduction
Urbanization is one of the major threats to biodiversity worldwide (Maxwell et al., 2016). The rapid sprawl and densification of urban centers has negative effects on local biotas through the novel ecological and evolutionary pressures imposed by the combination of multiple environmental factors such as habitat loss, pollution, climate change, and expansion of invasive species (Johnson and Munshi-South, 2017), which can act as ecological filters of biotic communities (Aronson et al., 2014, Spotswood et al., 2021). Yet urban scenarios span a wide range of environmental heterogeneity and greenspaces which can provide valuable refuges for native biodiversity, even rare and threatened species (Spotswood et al., 2021).
Urban greenspaces comprise private and public green areas (e.g., parks, public walkways, green roofs, gardens, forest remnants, lawns) of different sizes and forms immersed in the urban matrix (Peschardt et al., 2012) representing a critical habitat for many pollinator species (Silva et al., 2021, Theodorou et al., 2016). A growing body of evidence suggests that urbanization can generate positive, negative, as well as neutral impacts on the structure of plant-pollination interactions (Maruyama et al., 2021, Silva et al., 2021, Wenzel et al., 2020). However, the negative effects of urbanization on these interactions remain controversial (Wenzel et al., 2020). Some studies document decreases in pollinator richness and abundance along urbanization gradients (Wenzel et al., 2020), while others report a significant increase of both richness of plants and pollinators at moderate urbanization intensities (Baldock et al., 2015, Theodorou et al., 2016). Yet, most of the research has been conducted in Palearctic and Nearctic cities with insects as pollinators, while the knowledge of plant-pollinator interactions in tropical cities is substantially underrepresented (Maruyama et al., 2021, Silva et al., 2021, Wenzel et al., 2020).
Among vertebrates, hummingbirds and bats are the main pollinators of American floras (National Research Council, 2007, Stiles, 1981). Hummingbirds are an emblematic group of birds highly specialized on nectar consumption which pollinate a high proportion of plants (Bawa, 1990, Dalsgaard et al., 2021, Rodríguez-Flores et al., 2019, Stiles, 1981). The hummingbird-plant interaction represents a classic example of coevolution and has been widely used as system model to disentangle the ecological and historical factors that drives niche partitioning and community structure in highly diverse regions (Cotton, 2008, Dalsgaard et al., 2021, Stiles, 1981, Vizentin-Bugoni et al., 2014).
The study of hummingbird-plant interaction has focused mainly in natural areas (Dalsgaard et al., 2021, Sonne et al., 2019, Vizentin-Bugoni et al., 2014), while disturbed areas such as agricultural and urban settings are relatively recent. Hummingbird-plant networks from urban areas are characterized by high levels of generalization due to the dominance of a few hummingbird species, often territorial and dominant, as well as the importance of introduced plant species on network structure (Bustamante-Castillo et al., 2020, Diaz-Infante et al., 2020, Maruyama et al., 2019, Maruyama et al., 2016, Morrison and Mendenhall, 2020, Vitorino et al., 2021). Nonetheless, studies from several cities are needed to identify the patterns that determine the high degree of generalization and the relative contribution of different urban greenspaces on network structuring (Maruyama et al., 2021).
Traditionally, plant-hummingbird interaction has been studied through zoo-centric approaches (i.e., focus on the hummingbird activity recording the visited plants) including analysis of pollen loads samples (Morrison and Mendenhall, 2020, Ramírez-Burbano et al., 2017), or novel methods as DNA metabarcoding of fecal samples (Hazlehurst et al., 2021); as well as phyto-centric (i.e., focused on individual plant species to document which hummingbirds use the plants through video-cameras or focal observations (Arizmendi, 2001; Cotton, 2008; Stiles, 1981; Vizentin-Bugoni et al., 2016)). An alternative methodology that has yet to be used to record interactions is citizen science. Currently, a vast amount of information is available on social networks and citizen science platforms which could be useful to analyze the structure of ecological networks. Because of the expansion of social networks, projects that use citizen science have increased significantly in recent years (Callaghan et al., 2019a, Callaghan et al., 2020, La Sorte and Somveille, 2020). Social networks (i.e., Facebook, Twitter, Instagram) together with those focused on citizen science (i.e., eBird, Xenocanto, iNaturalist), have been of great importance in studies of species distribution, diversity patterns, geographic variation, expansion of invasive species, population trends, migration patterns and behavior (Callaghan et al., 2021, Leong and Trautwein, 2019). These studies represent a great value to urban practitioners and society due to the educational opportunities that contribute to scientific knowledge by collecting a large amount of information and making it available to the public (Callaghan et al., 2019a). One of these platforms is iNaturalist, which contains around 24 million observations of global biodiversity and has been an important source of data to answer multiple questions in urban and general ecology (Leong and Trautwein, 2019).
Assessing plant-hummingbird interaction in big cities requires a high effort to generate data at spatial and temporal scales. Particularly during the COVID-19 outbreak, because of the containment measures, many citizens started to collect and publish information about plants and animals in their neighborhoods areas. Therefore, in this study we used the information available on two popular citizen science platforms (iNaturalist and eBird) to assess the plant-hummingbird network structure in Mexico City. First, we contrasted the structure of hummingbird-plant networks across different urban greenspaces (natural protected areas, urban parks, urban gardens, and street trees areas), and then quantified plant species importance to network structure according to plant origin, life form, and pollination syndrome. Based on previous findings highlighting the impoverishment of nectar-feeding bird assemblages in urban areas as well as the dominance of alien plant species (Aronson et al., 2014, Pauw and Louw, 2012; Puga–Caballero et al., 2020), we expected to find a high generalization of hummingbird-plant networks in urban greenspaces with less vegetation cover. Moreover, due to the behavioral flexibility of hummingbirds in urban settings (Greig et al., 2017) and the inclusion of exotic plant species as feeding resources (Diaz-Infante et al., 2020, Maruyama et al., 2019, Mendonça and Anjos, 2005) we expected that alien plant species would have an important role for network structuring across urban green areas.
Section snippets
Study area
This study was carried out at Mexico City (19°26′N 99°8′W), one of the most populated megacities of the world with ~23 millions of residents. The city encompassed 59 adjacent municipalities of the Metropolitan Area of the Valley of Mexico (Mexico and Hidalgo states), a mountain basin between 2350 and 3500 m. als, located along the Trans-Mexican Volcanic Belt biogeographic province in central Mexico (CONABIO and SEDEMA, 2016). Mexico City has been recognized as an important conservation area due
Results
The hummingbird-plant network in Mexico City was composed of 17 hummingbird and 84 plant species (6% of plants were identified to genus level), encompassing a total of 742 interactions and 171 unique interactions (Fig. 1; Table S1). As revealed by sample coverage estimation, this dataset was representative of both hummingbird (Ĉn = 99.2%) and plant assemblages (Ĉn = 92.1%), as well of their interactions (Ĉn = 80.7%; Fig. S1). We found a positive and significant association between the number of
Discussion
Different studies have shown that the heterogeneity of urban greenspaces can buffer the negative effects of urbanization on biodiversity by increasing regional connectivity and providing refuges for native species (Spotswood et al., 2021). Yet, little attention has been paid to the impacts of urbanization on the structure of ecological networks in tropical cities (Silva et al., 2021). In this study we used citizen science data to explore the structure of hummingbird-plant networks across
Conclusions
In summary, our study provided evidence of the generalization of hummingbird-plant networks across urban greenspaces supporting the loss of specialization of plant-pollinators networks in urban areas. Introduced species and non-ornithophilous plants were important for hummingbirds, suggesting a potential integration of alien plants with no specialized bird pollination traits into ecological networks. Moreover, our results evidenced that citizen science represents a valuable source of data to
CRediT authorship contribution statement
Oscar H. Marín-Gómez: Conceptualization, Formal analysis, Investigation, Methodology, Writing – original draft, Writing – review & editing, Project administration. Claudia Rodriguez Flores: Methodology, Writing – review & editing. María del Coro Arizmendi: Conceptualization, Funding acquisition, Supervision, Writing – review & editing, Project administration.
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
This research was supported by Universidad Nacional Autónoma de México through the postdoctoral grant awarded by the Dirección General de Asuntos del Personal Académico (DGAPA) for the research carried out at the Facultad de Estudios Superiores Iztacala, and the financial support to by the Programa de Apoyo a Proyectos de Investigación e Innovación Tecnológica (IN221920). We are most grateful to Alexis López Hernández for some plant identifications, and to Margarita López García for English
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