More trees and fewer roads: the importance of local and landscape features for insectivorous bats in open urban green spaces Article Swipe
YOU?
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· 2024
· Open Access
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· DOI: https://doi.org/10.1071/wr23079
Context Urbanisation poses new challenges for wildlife worldwide, and recent research suggests that urban parks, although highly modified, may act as important refuges. Insectivorous bats can persist in urban landscapes and play an important role in keeping insect populations in balance. Previous research on use of urban landscapes by these bats has often focused on patches of remnant bushland within cities, but their use of highly modified open spaces is not well understood. Aims We aimed to determine the use of open green spaces (e.g. open parks, sports ovals) by insectivorous bats in Melbourne, Australia and to identify landscape factors that influence their presence and activity level. Methods We conducted passive acoustic surveys at 35 sites across greater Melbourne. Once species were identified from the echolocation call data, we modelled species richness, total activity and activity of individual species against landscape and weather variables, using Generalised Linear Mixed Models and Generalised Additive Mixed Models. Key results Across 557 detector nights, we identified at least 11 of the 17 species recorded to occur in Melbourne. Both species richness and activity were greater in areas with more nearby trees and lesser in areas with more roads. There were weaker species-specific relationships between bat activity and both distance to the nearest water source and Normalised Difference Vegetation Index. Species richness and activity levels were lower on nights with a lower temperature at dusk, higher rainfall and stronger wind. Conclusions Our results show that multiple bat species consistently use Melbourne’s open green spaces, highlighting the potential habitat value of these areas, especially those surrounded by high tree densities and fewer roads. Implications Insectivorous bats play important roles within ecosystems and bring benefits to human society. To encourage the diversity and activity of insectivorous bats in urban landscapes, we recommend retaining and increasing indigenous vegetation surrounding open areas in urban parks, as well as more strategic planning of new urban parks that further increases tree density in cities.
Related Topics
- Type
- article
- Language
- en
- Landing Page
- https://doi.org/10.1071/wr23079
- https://www.publish.csiro.au/wr/pdf/WR23079
- OA Status
- hybrid
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- OpenAlex ID
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Raw OpenAlex JSON
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https://openalex.org/W4394844248Canonical identifier for this work in OpenAlex
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https://doi.org/10.1071/wr23079Digital Object Identifier
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More trees and fewer roads: the importance of local and landscape features for insectivorous bats in open urban green spacesWork title
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articleOpenAlex work type
- Language
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enPrimary language
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2024Year of publication
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2024-04-15Full publication date if available
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Mariah J Callas, Linda F. Lumsden, Anthony R. Rendall, Kaori YokochiList of authors in order
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https://doi.org/10.1071/wr23079Publisher landing page
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https://www.publish.csiro.au/wr/pdf/WR23079Direct link to full text PDF
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YesWhether a free full text is available
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hybridOpen access status per OpenAlex
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https://www.publish.csiro.au/wr/pdf/WR23079Direct OA link when available
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Species richness, Geography, Insectivore, Ecology, Context (archaeology), Habitat, Wildlife, Urbanization, Biodiversity, Human echolocation, Biology, Neuroscience, ArchaeologyTop concepts (fields/topics) attached by OpenAlex
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6Total citation count in OpenAlex
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2025: 5, 2024: 1Per-year citation counts (last 5 years)
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10Other works algorithmically related by OpenAlex
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| abstract_inverted_index.green | 82, 247 |
| abstract_inverted_index.human | 279 |
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| abstract_inverted_index.lower | 221, 226 |
| abstract_inverted_index.occur | 171 |
| abstract_inverted_index.often | 52 |
| abstract_inverted_index.parks | 315 |
| abstract_inverted_index.poses | 2 |
| abstract_inverted_index.roles | 272 |
| abstract_inverted_index.sites | 115 |
| abstract_inverted_index.their | 62, 102 |
| abstract_inverted_index.these | 49, 255 |
| abstract_inverted_index.those | 258 |
| abstract_inverted_index.total | 132 |
| abstract_inverted_index.trees | 186 |
| abstract_inverted_index.urban | 13, 28, 46, 291, 304, 314 |
| abstract_inverted_index.using | 144 |
| abstract_inverted_index.value | 253 |
| abstract_inverted_index.water | 208 |
| abstract_inverted_index.wind. | 234 |
| abstract_inverted_index.Across | 156 |
| abstract_inverted_index.Index. | 214 |
| abstract_inverted_index.Linear | 146 |
| abstract_inverted_index.Models | 148 |
| abstract_inverted_index.across | 116 |
| abstract_inverted_index.areas, | 256 |
| abstract_inverted_index.higher | 230 |
| abstract_inverted_index.highly | 16, 65 |
| abstract_inverted_index.insect | 37 |
| abstract_inverted_index.lesser | 188 |
| abstract_inverted_index.level. | 106 |
| abstract_inverted_index.levels | 219 |
| abstract_inverted_index.nearby | 185 |
| abstract_inverted_index.nights | 223 |
| abstract_inverted_index.ovals) | 88 |
| abstract_inverted_index.parks, | 14, 86, 305 |
| abstract_inverted_index.recent | 9 |
| abstract_inverted_index.roads. | 193, 266 |
| abstract_inverted_index.source | 209 |
| abstract_inverted_index.spaces | 68, 83 |
| abstract_inverted_index.sports | 87 |
| abstract_inverted_index.weaker | 196 |
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| abstract_inverted_index.Context | 0 |
| abstract_inverted_index.Methods | 107 |
| abstract_inverted_index.Models. | 153 |
| abstract_inverted_index.Species | 215 |
| abstract_inverted_index.against | 139 |
| abstract_inverted_index.between | 199 |
| abstract_inverted_index.cities, | 60 |
| abstract_inverted_index.cities. | 322 |
| abstract_inverted_index.density | 320 |
| abstract_inverted_index.factors | 99 |
| abstract_inverted_index.focused | 53 |
| abstract_inverted_index.further | 317 |
| abstract_inverted_index.greater | 117, 180 |
| abstract_inverted_index.habitat | 252 |
| abstract_inverted_index.keeping | 36 |
| abstract_inverted_index.nearest | 207 |
| abstract_inverted_index.nights, | 159 |
| abstract_inverted_index.passive | 110 |
| abstract_inverted_index.patches | 55 |
| abstract_inverted_index.persist | 26 |
| abstract_inverted_index.remnant | 57 |
| abstract_inverted_index.results | 155, 237 |
| abstract_inverted_index.spaces, | 248 |
| abstract_inverted_index.species | 120, 130, 138, 168, 175, 242 |
| abstract_inverted_index.surveys | 112 |
| abstract_inverted_index.weather | 142 |
| abstract_inverted_index.Additive | 151 |
| abstract_inverted_index.Previous | 41 |
| abstract_inverted_index.acoustic | 111 |
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| abstract_inverted_index.balance. | 40 |
| abstract_inverted_index.benefits | 277 |
| abstract_inverted_index.bushland | 58 |
| abstract_inverted_index.detector | 158 |
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| abstract_inverted_index.identify | 97 |
| abstract_inverted_index.modelled | 129 |
| abstract_inverted_index.modified | 66 |
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| abstract_inverted_index.planning | 311 |
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| abstract_inverted_index.recorded | 169 |
| abstract_inverted_index.refuges. | 22 |
| abstract_inverted_index.research | 10, 42 |
| abstract_inverted_index.richness | 176, 216 |
| abstract_inverted_index.society. | 280 |
| abstract_inverted_index.stronger | 233 |
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| abstract_inverted_index.wildlife | 6 |
| abstract_inverted_index.Australia | 94 |
| abstract_inverted_index.conducted | 109 |
| abstract_inverted_index.densities | 263 |
| abstract_inverted_index.determine | 77 |
| abstract_inverted_index.diversity | 284 |
| abstract_inverted_index.encourage | 282 |
| abstract_inverted_index.important | 21, 33, 271 |
| abstract_inverted_index.increases | 318 |
| abstract_inverted_index.influence | 101 |
| abstract_inverted_index.landscape | 98, 140 |
| abstract_inverted_index.modified, | 17 |
| abstract_inverted_index.potential | 251 |
| abstract_inverted_index.recommend | 294 |
| abstract_inverted_index.retaining | 295 |
| abstract_inverted_index.richness, | 131 |
| abstract_inverted_index.strategic | 310 |
| abstract_inverted_index.Difference | 212 |
| abstract_inverted_index.Melbourne, | 93 |
| abstract_inverted_index.Melbourne. | 118, 173 |
| abstract_inverted_index.Normalised | 211 |
| abstract_inverted_index.Vegetation | 213 |
| abstract_inverted_index.challenges | 4 |
| abstract_inverted_index.ecosystems | 274 |
| abstract_inverted_index.especially | 257 |
| abstract_inverted_index.identified | 122, 161 |
| abstract_inverted_index.increasing | 297 |
| abstract_inverted_index.indigenous | 298 |
| abstract_inverted_index.individual | 137 |
| abstract_inverted_index.landscapes | 29, 47 |
| abstract_inverted_index.surrounded | 259 |
| abstract_inverted_index.variables, | 143 |
| abstract_inverted_index.vegetation | 299 |
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| abstract_inverted_index.Conclusions | 235 |
| abstract_inverted_index.Generalised | 145, 150 |
| abstract_inverted_index.landscapes, | 292 |
| abstract_inverted_index.populations | 38 |
| abstract_inverted_index.surrounding | 300 |
| abstract_inverted_index.temperature | 227 |
| abstract_inverted_index.understood. | 72 |
| abstract_inverted_index.Implications | 267 |
| abstract_inverted_index.Urbanisation | 1 |
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| abstract_inverted_index.echolocation | 125 |
| abstract_inverted_index.highlighting | 249 |
| abstract_inverted_index.Insectivorous | 23, 268 |
| abstract_inverted_index.Melbourne’s | 245 |
| abstract_inverted_index.insectivorous | 90, 288 |
| abstract_inverted_index.relationships | 198 |
| abstract_inverted_index.species-specific | 197 |
| cited_by_percentile_year.max | 98 |
| cited_by_percentile_year.min | 90 |
| corresponding_author_ids | https://openalex.org/A5019908475 |
| countries_distinct_count | 0 |
| institutions_distinct_count | 4 |
| sustainable_development_goals[0].id | https://metadata.un.org/sdg/11 |
| sustainable_development_goals[0].score | 0.7799999713897705 |
| sustainable_development_goals[0].display_name | Sustainable cities and communities |
| citation_normalized_percentile.value | 0.96856126 |
| citation_normalized_percentile.is_in_top_1_percent | False |
| citation_normalized_percentile.is_in_top_10_percent | True |