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129 results for “urban greening”
Supplementary material 4 from: Zulian G, Marando F, Mentaschi L, Alzetta C, Wilk B, Maes J (2022) Green balance in urban areas as an indicator for policy support: a multi-level application. One Ecosystem 7: e72685. https://doi.org/10.3897/oneeco.7.e72685
Greenness and changes in vegetation cover in not densely built areas
Supplementary material 2 from: Zulian G, Marando F, Mentaschi L, Alzetta C, Wilk B, Maes J (2022) Green balance in urban areas as an indicator for policy support: a multi-level application. One Ecosystem 7: e72685. https://doi.org/10.3897/oneeco.7.e72685
Setting the context at European Level
Supplementary material 6 from: Stanley CH, Hecht R, Cakir S, Brzoska P (2022) Approach to user group-specific assessment of urban green spaces for a more equitable supply exemplified by the elderly population. One Ecosystem 7: e83325. https://doi.org/10.3897/oneeco.7.e83325
Supplementary material 6
Supplementary material 5 from: Stanley CH, Hecht R, Cakir S, Brzoska P (2022) Approach to user group-specific assessment of urban green spaces for a more equitable supply exemplified by the elderly population. One Ecosystem 7: e83325. https://doi.org/10.3897/oneeco.7.e83325
Supplementary material 5
Supplementary material 9 from: Stanley CH, Hecht R, Cakir S, Brzoska P (2022) Approach to user group-specific assessment of urban green spaces for a more equitable supply exemplified by the elderly population. One Ecosystem 7: e83325. https://doi.org/10.3897/oneeco.7.e83325
Supplementary material 9
Supplementary material 2 from: Stanley CH, Hecht R, Cakir S, Brzoska P (2022) Approach to user group-specific assessment of urban green spaces for a more equitable supply exemplified by the elderly population. One Ecosystem 7: e83325. https://doi.org/10.3897/oneeco.7.e83325
Supplementary material 2
Supplementary material 4 from: Stanley CH, Hecht R, Cakir S, Brzoska P (2022) Approach to user group-specific assessment of urban green spaces for a more equitable supply exemplified by the elderly population. One Ecosystem 7: e83325. https://doi.org/10.3897/oneeco.7.e83325
Supplementary material 4
Supplementary material 8 from: Stanley CH, Hecht R, Cakir S, Brzoska P (2022) Approach to user group-specific assessment of urban green spaces for a more equitable supply exemplified by the elderly population. One Ecosystem 7: e83325. https://doi.org/10.3897/oneeco.7.e83325
Supplementary material 8
Supplementary material 1 from: Stanley CH, Hecht R, Cakir S, Brzoska P (2022) Approach to user group-specific assessment of urban green spaces for a more equitable supply exemplified by the elderly population. One Ecosystem 7: e83325. https://doi.org/10.3897/oneeco.7.e83325
Supplementary material 1
Supplementary material 3 from: Stanley CH, Hecht R, Cakir S, Brzoska P (2022) Approach to user group-specific assessment of urban green spaces for a more equitable supply exemplified by the elderly population. One Ecosystem 7: e83325. https://doi.org/10.3897/oneeco.7.e83325
Supplementary material 3
Supplementary material 7 from: Stanley CH, Hecht R, Cakir S, Brzoska P (2022) Approach to user group-specific assessment of urban green spaces for a more equitable supply exemplified by the elderly population. One Ecosystem 7: e83325. https://doi.org/10.3897/oneeco.7.e83325
Supplementary material 7
Supplementary material 1 from: Sprondel N, Donner J, Mahlkow N, Köppel J (2016) Urban climate and heat stress: how likely is the implementation of adaptation measures in mid-latitude cities? The case of façade greening analyzed with Bayesian networks. One Ecosystem 1: e9280. https://doi.org/10.3897/oneeco.1.e9280
Questionnaire for Bayesian network analysis
The boreal soil microbiome of different urban green spaces
<p>This study describes the soil microbiome in relation to the aboveground plant diversity of three types of urban green spaces: built green spaces with sown lawns, planted trees and ornamental flowerbeds, open green spaces such as meadows and pastures, and urban forests. </p> <p>Data includes information on study sites, soil physio-chemical properties, vegetation, and soil microbiome: Plot information, Soil properties, Vegetation, Meta includes column information in sheets plot and soil. In vegetation sheet column names are species. Explanations for species name abbreviations can be found in sheet meta2. Micoboal commnity composition and taxonomy in Bacteria_nmds and Fungi_nmds. </p>
Table 3 in Remarks on Hymenoptera on urban green roofs in Belgium
<p>Table 3. Hymenoptera families occurring on green roofs; absolute numbers and species</p><table><thead><tr><th>Cat.</th><th>Species</th><th>Family</th><th>Roofs (n=20)</th><th>Occurences (n = 273)</th></tr></thead><tbody><tr><th>C.</th><td><i>Lasius niger</i></td><td>Formicidae</td><td>18</td><td>131</td></tr><tr><th></th><td><i>Bombus terrestris-compl.</i></td><td>Apidae</td><td>16</td><td>53</td></tr><tr><th></th><td><i>Lasioglossum morio</i></td><td>Halictidae</td><td>16</td><td>36</td></tr><tr><th></th><td><i>Hylaeus hyalinatus</i></td><td>Colettidae</td><td>15</td><td>31</td></tr><tr><th></th><td><i>Lasioglossum laticeps</i></td><td>Halictidae</td><td>13</td><td>40</td></tr><tr><th></th><td><i>Bombus pascuorum</i></td><td>Apidae</td><td>11</td><td>23</td></tr><tr><th></th><td><i>Megachile rotundata</i></td><td>Megachilidae</td><td>11</td><td>17</td></tr><tr><th></th><td><i>Lasioglossum nitidulum</i></td><td>Halictidae</td><td>10</td><td>26</td></tr><tr><th></th><td><i>Tetramorium caespitum</i></td><td>Formicidae</td><td>9</td><td>22</td></tr><tr><th></th><td><i>Vespula germanica</i></td><td>Vespidae</td><td>9</td><td>20</td></tr><tr><th></th><td><i>Vespula vulgaris</i></td><td>Vespidae</td><td>9</td><td>12</td></tr><tr><th></th><td><i>Leiophron deficiens</i></td><td>Braconidae</td><td>9</td><td>11</td></tr><tr><th></th><td><i>Apis mellifera</i></td><td>Apidae</td><td>8</td><td>14</td></tr><tr><th></th><td><i>Bombus lapidarius</i></td><td>Apidae</td><td>7</td><td>17</td></tr><tr><th></th><td><i>Gonatopus clavipes</i></td><td>Dryinidae</td><td>7</td><td>13</td></tr><tr><th></th><td><i>Lasius flavus</i></td><td>Formicidae</td><td>7</td><td>9</td></tr><tr><th></th><td><i>Polistes dominula</i></td><td>Vespidae</td><td>7</td><td>8</td></tr><tr><th></th><td><i>Lasius brunneus</i></td><td>Formicidae</td><td>6</td><td>6</td></tr><tr><th></th><td><i>Lasius umbratus</i></td><td>Formicidae</td><td>6</td><td>6</td></tr><tr><th></th><td><i>Myrmica scabrinodis</i></td><td>Formicidae</td><td>5</td><td>10</td></tr><tr><th></th><td><i>Myrmecina graminicola</i></td><td>Formicidae</td><td>5</td><td>5</td></tr><tr><th></th><td><i>Dasypoda hirtipes</i></td><td>Melittidae</td><td>5</td><td>5</td></tr><tr><th></th><td><i>Myrmica rugulosa</i></td><td>Formicidae</td><td>4</td><td>7</td></tr><tr><th></th><td><i>Hylaeus pictipes</i></td><td>Colettidae</td><td>4</td><td>5</td></tr><tr><th></th><td><i>Idiasta dichrocera</i></td><td>Braconidae</td><td>4</td><td>4</td></tr><tr><th></th><td><i>Meloboris collector</i></td><td>Ichneumonidae</td><td>4</td><td>4</td></tr><tr><th>B.</th><td><i>Spilomena mocsaryi</i></td><td>Crabronidae</td><td>3</td><td>3</td></tr><tr><th></th><td><i>Trypoxylon minus</i></td><td>Crabronidae</td><td>3</td><td>3</td></tr><tr><th></th><td><i>Gonatopus lunatus</i></td><td>Dryinidae</td><td>3</td><td>3</td></tr><tr><th></th><td><i>Hypoponera punctatissima</i></td><td>Formicidae</td><td>3</td><td>4</td></tr><tr><th></th><td><i>Gelis declivis</i></td><td>Ichneumonidae</td><td>3</td><td>5</td></tr><tr><th></th><td><i>Gelis festinans</i></td><td>Ichneumonidae</td><td>3</td><td>5</td></tr><tr><th></th><td><i>Anthidium manicatum</i></td><td>Megachilidae</td><td>3</td><td>3</td></tr><tr><th></th><td><i>Andrena nitida</i></td><td>Andrenidae</td><td>3</td><td>3</td></tr><tr><th></th><td><i>Hylaeus communis</i></td><td>Colettidae</td><td>3</td><td>3</td></tr></tbody></table>
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>
Data for "Urbanization and a green corridor do not impact genetic divergence in common milkweed"
<p>This data for "Urbanization and a green corridor do not impact genetic divergence in common milkweed", a publication in preparation for submission (2/7/2023)</p>
Dataset on 'Green in grey: ecosystem services and disservices perceptions from small-scale green infrastructure along a rural-urban gradient in Bengaluru, India'
<p>This dataset includes the raw data of a survey of 649 residents of 61 villages along a rural-urban gradient in Bengaluru, India. It presents socio-demographic characteristics (village, village rural-urban state, age, gender, level of education, caste, and sources of household income) and Likert-scale answers (ranging from 1, i.e., not important to 5, i.e., very important) to rank the perceived importance of ecosystem services and disservice from five types of small-scale green infrastructure: Domestic trees (DT), Farm trees (FT), Street trees (ST), Platform trees (PT), Temple trees (TT).</p> <p>The complete method is described in Thapa, P., Torralba, M., Bhaskar, D., Nagendra, H., Plieninger, T. (2023): Green in grey: ecosystem services and disservices perceptions from small-scale green infrastructure along a rural-urban gradient in Bengaluru, India. Ecosystems and People, in press.</p>
Questionnaire data for assessing what determines urban residents' engagement in activities for the protection of urban green spaces (UGS)
<p>This dataset contains the core data used to investigate what determines Munich’s residents’ engagement in activities for the protection of urban green spaces (UGS). We conducted an exploratory factor analysis and a structural equation modelling based on the data from an online and in-person questionnaire.</p> <p><strong>List of data and content</strong></p> <ol> <li>Questionnaire_English: The content of the questionnaire in English (*.pdf)</li> <li>Questionnaire_RawData_ Munchen_German: Core data from the questionnaire in German (*.xlsx)</li> <li>InputEFA1: Core data for the first exploratory factor analysis with the input for analysis in Mplus (*.xlsx)</li> <li>InputEFA2: Core data for the second exploratory factor analysis with the input for analysis in Mplus (*.xlsx)</li> <li>InputSEM: Core data for the structural equation modelling with the input for analysis in Mplus (*.xlsx)</li> <li>ResultsSEM: Results of the structural equation modelling (*.xlsx)</li> <li>InputCFA1: Core data for the first confirmatory factor analysis with the input for analysis in Mplus (*.xlsx)</li> <li>ResultsCFA1: Results of the confirmatory factor analysis (*.xlsx)</li> <li>InputCFA2: Core data for the second confirmatory factor analysis with the input for analysis in Mplus (*.xlsx)</li> <li>ResultsCFA2: Results of the confirmatory factor analysis (*.xlsx)</li> <li>Acronyms_Shortings: Acronyms and shortings used in the uploaded files (*.pdf)</li> </ol> <p><strong>Data processing</strong></p> <p>The software for performing the exploratory factor analysis and structural equation modelling was Mplus 8.8 (Muthén and Muthén, 1998). The details on the methodological steps are available in the published publication. To quickly understand the <a href="https://www.statmodel.com/HTML_UG/chapter4V8.htm">EFA</a>,<a href="https://www.statmodel.com/download/usersguide/Chapter5.pdf"> CFA and SEM model and settings</a> the details are provided in the hyperlinks.</p> <p><strong>Acknowledgments</strong></p> <p>The authors thank to all participants for their participation in the online and in-person questionnaires. Data processing and analysis would not have been possible without the help of Tomomi Saito.</p> <p>This work was supported by a grant from the Alexander von Humboldt Foundation and by the Leibniz Best Minds Competition, Leibniz-Junior Research Group, Grant J76/2019.</p>
Codes, raw predation data on dummy caterpillars, and environmental data about urban green spaces across 26 Brazilian state capitals
<p>Data collected by the Urban Predation Risk Network about predation pressure on dummy caterpillars exposed for eight days in 26 small green spaces and 24 forest patches across 26 Brazilian state capitals. The raw predation data describes the type of predator and the day in which each caterpillar was found with marks, as well as the sites' coordinates. The environmental data provides information for each site about precipitation, annual mean temperature, temperature seasonality, elevation, and coordinates. This database also provides summarized information about predation at each site, such as the total number of attacked caterpillars and the number of attacked caterpillars by each predator group. The data files contain a metadata sheet with a description of each column.</p> <p>The code provided was used to assess the local and large-scale drivers of predation pressure on dummy caterpillars in small green spaces and forest patches across 26 Brazilian cities.</p>
ScienceDex guides
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These curated guides explain access requirements, typical timelines, costs, and reuse considerations for widely used research datasets.
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.