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Table 2 in Remarks on Hymenoptera on urban green roofs in Belgium
<p>Table 2. Hymenoptera species occurring on min. three roofs in Belgium (2020-21). Species which are probably migratory are marked in red.</p><table><thead><tr><th>Infraorder</th><th>Superfamily - Family</th><th>Absolute numbers</th><th>Species identified</th></tr></thead><tbody><tr><th>Aculeata</th><td></td><td><i>7879</i></td><td><i>79</i></td></tr><tr><th></th><td><b>Apoidea</b></td><td><b>773</b></td><td><b>52</b></td></tr><tr><th></th><td>Andrenidae Apidae Colletidae Crabronidae Halictidae Megachilidae Melittidae</td><td>169 190 97 21 253 36 7</td><td>9 6 6 11 11 8 1</td></tr><tr><th></th><td><b>Chrysidoidea</b></td><td><b>25</b></td><td><b>4</b></td></tr><tr><th></th><td>Chrysididae Dryinidae</td><td>1 24</td><td>1 3</td></tr><tr><th></th><td><b>Evanioidea</b></td><td><b>1</b></td><td><b>1</b></td></tr><tr><th></th><td>Gasteruptiidae</td><td>1</td><td>1</td></tr><tr><th></th><td><b>Formicoidea</b></td><td><b>6989</b></td><td><b>16</b></td></tr><tr><th></th><td>Formicidae</td><td>6989</td><td>16</td></tr><tr><th></th><td><b>Vespoidea</b></td><td><b>91</b></td><td><b>6</b></td></tr><tr><th></th><td>Pompilidae Vespidae</td><td>3 88</td><td>3 3</td></tr><tr><th>Parasitica</th><td></td><td><i>2200</i></td><td><i>37</i></td></tr><tr><th></th><td><b>Ceraphronoidea</b></td><td><b>240</b></td><td></td></tr><tr><th></th><td>Ceraphronidae Megaspilidae</td><td>233 6</td><td></td></tr><tr><th></th><td><b>Chalcidoidea</b></td><td><b>22</b></td><td><b>1</b></td></tr><tr><th></th><td>Aphelinidae Encyrtidae Eurytomidae Pteromalidae</td><td>2 2 2 3</td><td>1</td></tr><tr><th></th><td><b>Cynipoidea</b></td><td><b>10</b></td><td><b>1</b></td></tr><tr><th></th><td>Figitidae</td><td>9</td><td>1</td></tr><tr><th></th><td><b>Diaprioidea</b></td><td><b>89</b></td><td><b>1</b></td></tr><tr><th></th><td>Diapriidae</td><td>89</td><td>1</td></tr><tr><th></th><td><b>Ichneumonoidea</b></td><td><b>442</b></td><td><b>31</b></td></tr><tr><th></th><td>Braconidae</td><td>228</td><td>14</td></tr><tr><th></th><td>Ichneumonidae</td><td>214</td><td>17</td></tr><tr><th></th><td><b>Mymaridae / Mymarommatidae indet.</b></td><td><b>1245</b></td><td></td></tr><tr><th></th><td><b>Platygastroidea</b></td><td><b>147</b></td><td></td></tr><tr><th></th><td>Platygastridae Scelionidae</td><td>49 49</td><td></td></tr><tr><th></th><td><b>Proctotrupoidea</b></td><td><b>5</b></td><td><b>3</b></td></tr><tr><th></th><td>Proctotrupidae</td><td>5</td><td>3</td></tr><tr><th>Symphyta</th><td></td><td><i>6</i></td><td><i>3</i></td></tr><tr><th></th><td><b>Tenthredinoidea</b></td><td><b>6</b></td><td><b>3</b></td></tr><tr><th></th><td>Tenthredinidae</td><td>6</td><td>3</td></tr><tr><th></th><td></td><td>10.085</td><td>119</td></tr></tbody></table>
Table 1 in Remarks on Hymenoptera on urban green roofs in Belgium
<p>Table 1. Overview of the roofs with their reference name, age, surface area, height above ground level and dominant vegetation.</p><table><thead><tr><th>Name roof</th><th>Reference</th><th>Location</th><th>Age (y)</th><th>Surface (m²)</th><th>Height (m)</th><th><b>Dominant vegetation</b></th></tr></thead><tbody><tr><th>OCMW Arena</th><td>ARENA</td><td>Deurne (N51.199°, E4.459°)</td><td>13</td><td>72</td><td>6</td><td>Sedum</td></tr><tr><th>Atlas</th><td>ATLAS</td><td>Antwerpen (N51.130°, E4.253°)</td><td>8</td><td>320</td><td>8</td><td><i>Sedum, herbs and</i> <i>grasses</i></td></tr><tr><th>Administrative centre Den Bell</th><td>BELL</td><td>Antwerpen (N51.205°, E4.399°)</td><td>12</td><td>85</td><td>21</td><td><i>Sedum</i></td></tr><tr><th>Boekenberg park 1</th><td>BOEK 1</td><td>Deurne (N51.197°, E4.463°)</td><td>14</td><td>108</td><td>5</td><td><i>Sedum, herbs and</i> <i>grasses</i></td></tr><tr><th>Boekenberg park 2</th><td>BOEK 2</td><td>Deurne (N51.197°, E4.462)</td><td>14</td><td>85</td><td>4</td><td><i>Sedum, herbs and</i> grasses</td></tr><tr><th>Brandweer</th><td>BRA</td><td>Antwerpen (N51.251°, E4.418°)</td><td>12</td><td>777</td><td>17</td><td><i>Sedum, herbs and</i> grasses</td></tr><tr><th>District</th><td>DIS</td><td>Wilrijk (N51.169°, E4.394°)</td><td>13</td><td>320</td><td>9</td><td><i>Sedum, herbs and</i> <i>grasses</i></td></tr><tr><th>Ecohuis 1</th><td>ECO 1</td><td>Borgerhout (N51.125°, E4.260°)</td><td>3</td><td>35</td><td>12</td><td><i>Sedum</i></td></tr><tr><th>Ecohuis 2</th><td>ECO 2</td><td>Borgerhout (N51.125°, E4.260°)</td><td>3</td><td>8</td><td>12</td><td><i>Sedum, herbs and</i> <i>grasses</i></td></tr><tr><th>Ellerman</th><td>ELL</td><td>Antwerpen (N51.230°, E4.415°)</td><td>6</td><td>312</td><td>9</td><td><i>Sedum, herbs and</i> <i>grasses</i></td></tr><tr><th>Hardenvoort</th><td>HARD</td><td>Antwerpen (N51.135°, E4.251°)</td><td>5</td><td>630</td><td>20</td><td><i>Sedum, herbs and</i> <i>grasses</i></td></tr><tr><th>Urban childcare centre Strandloper</th><td>IGLO</td><td>Antwerpen (N51.225°, E4.380°)</td><td>9</td><td>896</td><td>5</td><td><i>Sedum</i></td></tr><tr><th>Middelheim 1 Middelheim 2 Onyx</th><td>MID 1 MID 2 ONYX</td><td>Antwerpen (N51.184°, E4.420°) Antwerpen (N51.184°, E4.419°) Berchem (N51.193°, E4.417°)</td><td>7 7 7</td><td>260 45 708</td><td>10 10 23</td><td><i>Sedum</i> <i>Sedum</i> <i>Sedum</i></td></tr><tr><th>Plantin Moretus museum</th><td>PM</td><td>Antwerpen (N51.218°, E4.398°)</td><td>5</td><td>84</td><td>15</td><td><i>Sedum</i></td></tr><tr><th>Recycling park Berchem</th><td>RPBer</td><td>Berchem (N51.194°, E4.439°)</td><td>7</td><td>154</td><td>4</td><td><i>Sedum</i></td></tr><tr><th>Recycling park Deurne</th><td>RPDeu</td><td>Deurne (N51.237°, E4.457°)</td><td>7</td><td>142</td><td>4</td><td><i>Sedum</i></td></tr><tr><th>Recycling park Wilrijk</th><td>RPWil</td><td>Wilrijk (N51.160°, E4.390°)</td><td>7</td><td>164</td><td>4</td><td><i>Sedum, herbs and</i> <i>grasses</i></td></tr><tr><th>Red Star Line museum</th><td>RSL</td><td>Antwerpen (N51.135°, E4.241°)</td><td>10</td><td>408</td><td>10</td><td><i>Sedum</i></td></tr></tbody></table>
Dataset for AR article: New particle formation dynamics in the central Andes: contrasting urban and mountaintop environments
<p>Dataset for Article New particle formation dynamics in the central Andes:<br>contrasting urban and mountaintop environments (Aliaga et al. 2024; Aerosol research)</p> <p>It contains four key data files with clustered model output and measurement data from FLEXPART simulations and in situ observations. Details on each file are provided below:</p> <p>1. flx_clust20_alto.nc</p> <p> - Description: Contains clustered output from FLEXPART simulations at EAC site .</p> <p><br>2. flx_clust20_chc.nc</p> <p> - Description: Stores the clustered output from FLEXPART simulations at the CHC site.</p> <p><br>3. particle_number_size_dist.nc</p> <p> - Description: Provides particle number concentrations measured at CHC and EAC sites, utilizing instruments NAIS and DMPS.</p> <p><br>4. hourly_data.nc</p> <p> - Description: dataset with all relevant parameters, including meteorological variables, cloud fraction, chemical composition, and particle concentration across various sizes.</p> <p> </p>
Enhanced Ice Nucleation Activity by Metal Elements and Secondary Aerosols in Polluted Urban Atmosphere
Open the record for dataset details and reuse information.
Data from: A game-theoretical model of kleptoparasitic behaviour in an urban gull (Laridae) population.
Kleptoparasitism (food stealing) is a significant behaviour for animals that forage in social groups as it permits some individuals to obtain resources whilst avoiding the costs of searching for their own food. Evolutionary game theory has been used to model kleptoparasitism, with a series of differential equation based compartmental models providing significant theoretical insights into behaviour in kleptoparasitic populations. In this paper we apply this compartmental modelling approach to kleptoparasitic behaviour in a real foraging population of urban gulls (Laridae). Field data was collected on kleptoparasitism and a model developed that incorporated the same kleptoparasitic and defensive strategies available to the study population. Two analyses were conducted: 1. An assessment of whether the density of each behaviour in the population was at an equilibrium. 2. An investigation of whether individual foragers were using Evolutionarily Stable Strategies (ESS) in the correct environmental conditions. The results showed the density of different behaviours in the population could be at an equilibrium at plausible values for handling time and fight duration. Individual foragers used aggressive kleptoparasitic strategies effectively in the correct environmental conditions but some individuals in those same conditions failed to defend food items. This was attributed to the population being composed of three species that differed in competitive ability. These competitive differences influenced the strategies that individuals were able to use. Rather than gulls making poor behavioural decisions these results suggest a more complex three-species model is required to describe the behaviour of this population.
Data from: Cold nights, city lights: artificial light at night reduces photoperiodically induced diapause in urban and rural populations of Aedes albopictus
<p>As the planet becomes increasingly urbanized, it is imperative that we understand the ecological and evolutionary consequences of urbanization on species. One common attribute of urbanization that differs from rural areas is the prevalence of artificial light at night (ALAN). For many species, light is one of the most important and reliable environmental cues, largely governing the timing of daily and seasonal activity patterns. Recently, it has been shown that ALAN can alter behavioral, phenological, and physiological traits in diverse taxa. For temperate insects, diapause is an essential trait for winter survival and commences in response to declining daylight hours in the fall. Diapause is under strong selection pressure in the mosquito, <i>Aedes albopictus</i>; local adaptation and rapid evolution has been observed along a latitudinal cline. It is unknown how ALAN affects this photosensitive trait or if local adaptation has occurred along an urbanization gradient. Using a common garden experiment, we experimentally demonstrated that simulated ALAN reduces diapause incidence in this species by as much as 40%. There was no difference, however, between urban and rural demes. We also calculated diapause incidence from wild demes in urban areas to determine if wild populations exhibited lower than predicted incidence compared to estimates from total nocturnal darkness. In early fall, lower than predicted diapause incidence was recorded but all demes reached nearly 100% diapause before terminating egg laying. It is possible that nocturnal resting behavior in vegetation limits the amount of ALAN exposure this species experiences potentially limiting local adaptation.</p>
Figure 8 in Reproductive ecology of the glass frog Espadarana prosoblepon (Anura: Centrolenidae) in an urban forest of the Central Andes of Colombia
Figure 8. Egg clutches of Espadarana prosoblepon at different stages of development.
Figure 1 in Relationship between environmental conditions and hostseeking activity of Ochlerotatus albifasciatus (Diptera: Culicidae) in an agroecosystem and in an urban area in Chubut, Central Patagonia, Argentina
Figure 1. Absolute frequencies of Ochlerotatus albifasciatus for the catches in Sarmiento Valley.
FIGURES 12–14 in Nest and Immatures of the South American Anthidiine Bee Notanthidium (Allanthidium) chilense (Urban) (Apoidea: Megachilidae)
FIGURES 12–14. Photomicrogrphs of larval right mandible of Notanthidium chilense (arrows pointing to single large seta arising from small tubercle on outer base). 12. Dorsal, 13. inner, and 14. ventral views.
Fig. 2 in Histopathology of gills, kidney and liver of a Neotropical fish caged in an urban stream
Fig. 2. Photomicrographs of the gill of P. lineatus caged in Cambé stream. a) normal aspect of the gill, showing the filament (gray arrow), the lamellae (L), the water channel (*), a pillar cell (black arrow) and an epithelial cell (arrowhead); b) lamellae with the marginal channel dilated (black arrow), hyperplasia of the epithelial cells (white arrow) and epithelial lifting (arrowheads); c) fusion of 3 lamellae (white arrow) and blood congestion (arrowhead); d) lamellar disorganization (arrowheads), partial fusion of some lamellae (white arrow) and hypertrophy of the lamellar epithelium (black arrow); e) lamellar aneurysm (white arrow) and epithelium rupture with hemorrhage (*). Scale bar 20mm, H.E.
Data from: Socioeconomic status effects on health vary between rural and urban Turkana
<p>Background and objectives: Understanding the social determinants of health is a major goal in evolutionary biology and human health research. Low socioeconomic status (often operationalized as absolute material wealth) is consistently associated with chronic stress, poor health, and premature death in high income countries. However, the degree to which wealth gradients in health are universal<span>—</span>or are instead made even steeper under contemporary, post-industrial conditions<span>—</span>remains poorly understood.</p> <p>Methodology: We quantified absolute material wealth and several health outcomes among a population of traditional pastoralists, the Turkana of northwest Kenya, who are currently transitioning toward a more urban, market-integrated lifestyle. We assessed whether wealth associations with health differed in subsistence-level versus urban contexts. We also explored the causes and consequences of wealth-health associations by measuring serum cortisol, potential sociobehavioral mediators in early life and adulthood, and adult reproductive success (number of surviving offspring).</p> <p>Results: Higher socioeconomic status and greater material wealth predicts better self-reported health and more offspring in traditional pastoralist Turkana, but worse cardiometabolic health and fewer offspring in urban Turkana. We do not find robust evidence for either direct biological mediators (i.e., cortisol) or indirect sociobehavioral mediators (e.g., adult diet or health behaviors, early life experiences) of wealth-health relationships in either context.</p> <p>Conclusions and implications: While social gradients in health are well-established across a variety of primate species, and in humans, across a variety of socioecological contexts, we show that the relationship between wealth and health can vary within a single population. Our findings emphasize that changes in economic and societal circumstances may directly alter how, why, and under what conditions socioeconomic status is predictive of health.</p>
Boston Trustees urban garden crop and tree data
<div> <p>This dataset includes field data collected from gardens plots<strong> </strong>in 38 urban gardens across the city of Boston in 8 neighborhoods: Dorchester, East Boston, Fenway, Jamaica Plain, Mattapan, Mission Hill, Roxbury, and South End across 3 seasons: spring, summer, and fall (June 3-7, 2021; August 25-26, 2021; October 23-24, 2021). Neighborhood borders were defined by census tract block group designations available from the city <a href="https://www.zotero.org/google-docs/?iT7ffU">(Department of Innovation and Technology 2021)</a>. Census data was taken from American Community Survey -1 year estimates for 2021 available from the <a href="https://www.census.gov/data/developers/data-sets/acs-1year.html">U.S. Census Bureau</a>. For each garden, all plots were hand mapped on site by researchers, enumerated, and then randomly selected using a number generator for further census. In each plot, every individual crop plant was counted and identified to species and cultivar if known or marked by gardeners. In addition, the number and species of each tree in the garden was surveyed. </p> <p>We identified each crop species (no ornamental, non-edible plants were surveyed other than communal garden trees) and classified each plant species as annual or perennial according to whether they could survive across multiple growing seasons in the temperate region and are practiced as perennial crops, ie. gardeners do not typically remove the entire plant at the end of growing season. Biennial and woody plants were all classified as perennial. We classified all crops according to USDA classifications as vegetable, fruit, grain, culinary, medicinal, and combinations of these classifications. </p> <p>We also include an R notebook with code used to generate figures and run analyses supporting the work entitled, "Rooting in place: Trees and perennials reflect permanence in urban gardens and communities" by the authors listed. A knitted html for R Markdown file is also included.</p> <p> </p> </div>
Urban planning effectiveness and citizen satisfaction. A systematic literature review.
<p><strong>Background:</strong> The population is increasingly demanding a better quality of life in their territories, which requires better urban planning. This study aims to find out the effectiveness of urban planning implemented by local governments on citizen satisfaction.</p> <p><strong>Method:</strong> A systematic literature review was conducted exploring the evolution of the state of the art databases in Scopus, WOS and Dimensions, involving a relevant selection of empirical studies on the effectiveness of urban planning on citizen satisfaction, using quality criteria and the application of the Prism diagram.</p> <p>Results: The findings in the various empirical contributions find converging in three main blocks the contributions related to: (i) Urban planning as a catalyst for the impact of citizen satisfaction, given that using the planning tool will lead to the development of local policies based on the Neoliberalism approach for smart urban development; (ii) Theoretical contributions for urban planning that contextualises a modernist planning based on a multidimensional aspect to address quality of life for modern well-being and (iii) Smart planning for citizen satisfaction for the design and implementation of public governance reforms aimed at optimising urban planning management at the local level for smart urban city development. </p> <p><strong>Conclusion:</strong> There is strong theoretical and empirical support that is closely linked to sustainable development, happiness, public space, urban growth, urban areas, satisfied customers and urban residents. Future research should examine the relative weight of urban planning dimensions and effectiveness in the sustainable development of territories and citizen satisfaction.</p> <p><strong><em>Keywords:</em></strong> PRISMA, bibliometrics, bibliometrix, urban planning, citizen satisfaction, systematic review, state of the art.</p>
Figures 8-14 from: Engel M, Oliveira F, Urban D (2011) The identity of the Neotropical stingless bee Frieseomelitta meadewaldoi (Cockerell, 1915) (Hymenoptera, Apidae). ZooKeys 111: 19-31. https://doi.org/10.3897/zookeys.111.1345
Figures 8-14 - Trigona meadewaldoi Cockerell, 1915 (lectotype, NHML; non-type, DZUP), and Trigona doederleini Friese, 1900 (lectotype, AMNH) (all are workers). 8 Facial view of Trigona freiremaiai holotype. 9 Facial view of Frieseomelitta meadewaldoi from the State of Bahia, Brazil (non-type material). 10 Lateral habitus of Trigona freiremaiai holotype. 11 Lateral habitus of Frieseomelitta meadewaldoi (non-type material). 12 Dorsal oblique view of mesoscutum and mesoscutellum of Trigona freiremaiai holotype. 13 Metatibia of Trigona doederleini lectotype. 14 Metatibia of Trigona meadewaldoi lectotype.
Figures1-7 from: Engel M, Oliveira F, Urban D (2011) The identity of the Neotropical stingless bee Frieseomelitta meadewaldoi (Cockerell, 1915) (Hymenoptera, Apidae). ZooKeys 111: 19-31. https://doi.org/10.3897/zookeys.111.1345
Figures1-7 - Trigona meadewaldoi Cockerell, 1915 (lectotype, NHML), Tetragona francoi Moure, 1946 (holotype, DZUP), and Trigona doederleini Friese, 1900 (lectotype, AMNH) (all are workers). 1 Lateral habitus of Trigona meadewaldoi lectotype as preserved 2 Dorsal view of metasoma of Trigona meadewaldoi lectotype 3 External surface of metatibia of Trigona meadewaldoi lectotype 4 Facial view of Tetragona francoi holotype 5 Lateral habitus of Tetragona francoi holotype 6 Facial view of Trigona doederleini lectotype 7 Dorsal oblique view of mesoscutum and mesoscutellum of Tetragona francoi holotype.
Figure 1 from: Vilisics F, Bogyó D, Sattler T, Moretti M (2012) Occurrence and assemblage composition of millipedes (Myriapoda, Diplopoda) and terrestrial isopods (Crustacea, Isopoda, Oniscidea) in urban areas of Switzerland. ZooKeys 176: 199-214. https://doi.org/10.3897/zookeys.176.2153
Figure 1 - Abundances of isopods and millipedes in Zurich, Lucerne and Lugano in logarithmic scale. Dashed line separates isopods (on the left) from millipedes. Black bars represent abundances, white circles show the species' incidences per all sites per city.
Figure 4 from: Gandhi K, Epstein M, Koehle J, Purrington F (2011) A quarter of a century succession of epigaeic beetle assemblages in remnant habitats in an urbanized matrix (Coleoptera, Carabidae). ZooKeys 147: 667-689. https://doi.org/10.3897/zookeys.147.1954
Figure 4 - Dendrogram for the similarity/dissimilarity in standardized per trap catches of epigaeic beetle assemblages in sampling years 1980 and 2005 (A) and 1981 and 2005 (B) in cottonwood and oak stands, and old fields.
Figure 2 from: Gandhi K, Epstein M, Koehle J, Purrington F (2011) A quarter of a century succession of epigaeic beetle assemblages in remnant habitats in an urbanized matrix (Coleoptera, Carabidae). ZooKeys 147: 667-689. https://doi.org/10.3897/zookeys.147.1954
Figure 2 - Mean (+SE) standardized total catches of epigaeic beetles (A), and Cyclotrachelus sodalis sodalis LeConte (B) caught in 1980 and 2005 in cottonwood (N = 3) and oak (N =4) stands, and old fields (N = 2).
Figure 3 from: Gandhi K, Epstein M, Koehle J, Purrington F (2011) A quarter of a century succession of epigaeic beetle assemblages in remnant habitats in an urbanized matrix (Coleoptera, Carabidae). ZooKeys 147: 667-689. https://doi.org/10.3897/zookeys.147.1954
Figure 3 - Estimated mean species richness of epigaeic beetles using rarefaction analyses in sampling years 1980 and 2005 (A) and 1981 and 2005 (B) in cottonwood and oak stands, and old fields.
Figures 8-17 from: Parizotto D, Urban D (2011) Michanthidium almeidai, a new species from northeastern Brazil (Hymenoptera, Megachilinae). ZooKeys 132: 65-73. https://doi.org/10.3897/zookeys.132.1840
Figures 8-17 - 8–10 dorsal view of female 8 Michanthidium almeidai sp. n. 9 Michanthidium ferrugineum 10 Michanthidium albitarse 11–12 dorsal view of scutellum and axilla 11 Michanthidium almeidai sp. n. 12 Michanthidium albitarse 13–15 dorsal view of metasoma of female 13 Michanthidium almeidai sp. n. 14 Michanthidium ferrugineum 15 Michanthidium albitarse 16–17 apex of metasoma of female 16 Michanthidium ferrugineum 17 Michanthidium almeidai sp. n.
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Allen Brain Atlas
Allen Brain Atlas is an Allen Institute collection of brain map atlases, datasets, APIs, and analysis tools covering mouse, human, and non-human primate brain resources.
Annotated Behaviour and Observability Dataset (ABODe)
ABODe is a University of Edinburgh DataShare dataset for behavior classification in group-housed mice using home-cage video, identities, bounding boxes, ground-plate positions, and annotator labels.
DANDI Archive for NWB datasets
DANDI is a BRAIN Initiative archive for publishing and sharing neurophysiology data, including electrophysiology, optophysiology, and behavioral data packaged as NWB and related standards.
International Brain Laboratory public data
The International Brain Laboratory public data releases expose standardized mouse decision-making experiments, including Neuropixels recordings, widefield calcium imaging, behavior, and session metadata accessed through the ONE API.
OpenNeuro
OpenNeuro is a free, open platform for sharing neuroimaging datasets, with public search, dataset pages, and download paths for web, S3, DataLad, and the OpenNeuro CLI.