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| f | 1 | { | f | 1 | { |
| 2 | "access_rights": | 2 | "access_rights": | ||
| 3 | .europa.eu/metadata-codelist/LimitationsOnPublicAccess/noLimitations", | 3 | .europa.eu/metadata-codelist/LimitationsOnPublicAccess/noLimitations", | ||
| 4 | "alternate_identifier": "DOI: 10.1016/j.biocon.2016.06.004", | 4 | "alternate_identifier": "DOI: 10.1016/j.biocon.2016.06.004", | ||
| 5 | "author": "Santos, S.M., Mira, A., Salgueiro, P.A., Costa, P., | 5 | "author": "Santos, S.M., Mira, A., Salgueiro, P.A., Costa, P., | ||
| 6 | Medinas, D. y Beja, P.", | 6 | Medinas, D. y Beja, P.", | ||
| 7 | "author_name": "Santos, S.M., Mira, A., Salgueiro, P.A., Costa, P., | 7 | "author_name": "Santos, S.M., Mira, A., Salgueiro, P.A., Costa, P., | ||
| 8 | Medinas, D. y Beja, P.", | 8 | Medinas, D. y Beja, P.", | ||
| 9 | "classification_variables": { | 9 | "classification_variables": { | ||
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| 12 | "conforms_to": [ | 12 | "conforms_to": [ | ||
| 13 | "https://www.boe.es/eli/es/res/2013/02/19/(4)" | 13 | "https://www.boe.es/eli/es/res/2013/02/19/(4)" | ||
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| 18 | "name": "Organismo publicador del Cat\u00e1logo", | 18 | "name": "Organismo publicador del Cat\u00e1logo", | ||
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| 27 | "contact_name": "Organismo publicador del Cat\u00e1logo", | 27 | "contact_name": "Organismo publicador del Cat\u00e1logo", | ||
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| 31 | "http://datos.gob.es/recurso/sector-publico/org/Organismo/EA0000000", | 31 | "http://datos.gob.es/recurso/sector-publico/org/Organismo/EA0000000", | ||
| 32 | "contact_url": "https://organismo.example.org/", | 32 | "contact_url": "https://organismo.example.org/", | ||
| 33 | "created": "2025-05-23", | 33 | "created": "2025-05-23", | ||
| 34 | "creator": [ | 34 | "creator": [ | ||
| 35 | { | 35 | { | ||
| 36 | "name": "Santos, S.M., Mira, A., Salgueiro, P.A., Costa, P., | 36 | "name": "Santos, S.M., Mira, A., Salgueiro, P.A., Costa, P., | ||
| 37 | Medinas, D. y Beja, P." | 37 | Medinas, D. y Beja, P." | ||
| 38 | } | 38 | } | ||
| 39 | ], | 39 | ], | ||
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| 41 | "dataset_scope": "non_spatial_dataset", | 41 | "dataset_scope": "non_spatial_dataset", | ||
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| 43 | "encoding": "UTF-8", | 43 | "encoding": "UTF-8", | ||
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| 47 | "groups": [ | 47 | "groups": [ | ||
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| 49 | "description": "La fragmentaci\u00f3n del h\u00e1bitat se define | 49 | "description": "La fragmentaci\u00f3n del h\u00e1bitat se define | ||
| 50 | como el proceso durante el cual una gran extensi\u00f3n de | 50 | como el proceso durante el cual una gran extensi\u00f3n de | ||
| 51 | h\u00e1bitat se transforma en una serie de parches m\u00e1s | 51 | h\u00e1bitat se transforma en una serie de parches m\u00e1s | ||
| 52 | peque\u00f1os de menor superficie total aislados entre s\u00ed por una | 52 | peque\u00f1os de menor superficie total aislados entre s\u00ed por una | ||
| 53 | matriz de h\u00e1bitats distinta de la original", | 53 | matriz de h\u00e1bitats distinta de la original", | ||
| 54 | "display_name": "Fragmentaci\u00f3n del h\u00e1bitat", | 54 | "display_name": "Fragmentaci\u00f3n del h\u00e1bitat", | ||
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| 58 | "name": "fragmentacion-habitat", | 58 | "name": "fragmentacion-habitat", | ||
| 59 | "title": "Fragmentaci\u00f3n del h\u00e1bitat" | 59 | "title": "Fragmentaci\u00f3n del h\u00e1bitat" | ||
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| 69 | "license_id": "cc-by", | 69 | "license_id": "cc-by", | ||
| 70 | "license_title": "Creative Commons Attribution", | 70 | "license_title": "Creative Commons Attribution", | ||
| 71 | "license_url": "http://www.opendefinition.org/licenses/cc-by", | 71 | "license_url": "http://www.opendefinition.org/licenses/cc-by", | ||
| 72 | "lineage_process_steps": [], | 72 | "lineage_process_steps": [], | ||
| 73 | "lineage_source": [ | 73 | "lineage_source": [ | ||
| 74 | "Biological Conservation. Vol. 200", | 74 | "Biological Conservation. Vol. 200", | ||
| 75 | "pags. 122-130" | 75 | "pags. 122-130" | ||
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| 79 | "metadata_created": "2026-06-23T14:47:58.125873", | 79 | "metadata_created": "2026-06-23T14:47:58.125873", | ||
| n | 80 | "metadata_modified": "2026-06-25T12:22:09.108320", | n | 80 | "metadata_modified": "2026-06-25T12:26:17.951927", |
| 81 | "metadata_profile": [ | 81 | "metadata_profile": [ | ||
| 82 | "https://www.w3.org/TR/vocab-dcat-3/" | 82 | "https://www.w3.org/TR/vocab-dcat-3/" | ||
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| 84 | "miteco_data_population": { | 84 | "miteco_data_population": { | ||
| 85 | "es": "" | 85 | "es": "" | ||
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| 87 | "miteco_data_territory": { | 87 | "miteco_data_territory": { | ||
| 88 | "es": "" | 88 | "es": "" | ||
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| 90 | "miteco_dataset_type": | 90 | "miteco_dataset_type": | ||
| 91 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | 91 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | ||
| 92 | "miteco_geo_level": "1", | 92 | "miteco_geo_level": "1", | ||
| 93 | "modified": "2026-06-25", | 93 | "modified": "2026-06-25", | ||
| 94 | "name": "ed3d031f-9bf0-5e3d-87e2-bb9d75ea0c84", | 94 | "name": "ed3d031f-9bf0-5e3d-87e2-bb9d75ea0c84", | ||
| 95 | "notes": "Collision with vehicles is an important source of bird | 95 | "notes": "Collision with vehicles is an important source of bird | ||
| 96 | mortality, but it is uncertain why some species are killed more often | 96 | mortality, but it is uncertain why some species are killed more often | ||
| 97 | than others. Focusing on passerines, we tested whether mortality is | 97 | than others. Focusing on passerines, we tested whether mortality is | ||
| 98 | associated with bird abundances, and with traits reflecting flight | 98 | associated with bird abundances, and with traits reflecting flight | ||
| 99 | manoeuvrability, habitat, diet, and foraging and social behaviours. We | 99 | manoeuvrability, habitat, diet, and foraging and social behaviours. We | ||
| 100 | also tested whether the species most vulnerable to road-killing were | 100 | also tested whether the species most vulnerable to road-killing were | ||
| 101 | scarcer near (< 500 m) or far (> 500\u20135000 m) from roads. During | 101 | scarcer near (< 500 m) or far (> 500\u20135000 m) from roads. During | ||
| 102 | the breeding seasons of 2009\u20132011, we surveyed roadkills daily | 102 | the breeding seasons of 2009\u20132011, we surveyed roadkills daily | ||
| 103 | along 50 km of roads, and estimated bird abundances from 74 point | 103 | along 50 km of roads, and estimated bird abundances from 74 point | ||
| 104 | counts. After correcting for phylogenetic relatedness, there was | 104 | counts. After correcting for phylogenetic relatedness, there was | ||
| 105 | strong correlation between roadkill numbers and the abundances of 28 | 105 | strong correlation between roadkill numbers and the abundances of 28 | ||
| 106 | species counted near roads. However, selectivity indices indicated | 106 | species counted near roads. However, selectivity indices indicated | ||
| 107 | that Blue tit (Parus caeruleus), Blackcap (Sylvia atricapilla) and | 107 | that Blue tit (Parus caeruleus), Blackcap (Sylvia atricapilla) and | ||
| 108 | European goldfinch (Carduelis carduelis) were significantly more | 108 | European goldfinch (Carduelis carduelis) were significantly more | ||
| 109 | road-killed than expected from their abundances, while the inverse was | 109 | road-killed than expected from their abundances, while the inverse was | ||
| 110 | found for seven species. Using phylogenetic generalised estimating | 110 | found for seven species. Using phylogenetic generalised estimating | ||
| 111 | equations, we found that selectivity indexes were strongly related to | 111 | equations, we found that selectivity indexes were strongly related to | ||
| 112 | foraging behaviour and habitat type, and weakly so to body size, wing | 112 | foraging behaviour and habitat type, and weakly so to body size, wing | ||
| 113 | load, diet and social behaviour. The most vulnerable passerines were | 113 | load, diet and social behaviour. The most vulnerable passerines were | ||
| 114 | foliage/bark and swoop foragers, inhabiting woodlands, with small body | 114 | foliage/bark and swoop foragers, inhabiting woodlands, with small body | ||
| 115 | size and low wing load. The species most vulnerable to road collisions | 115 | size and low wing load. The species most vulnerable to road collisions | ||
| 116 | were not scarcer close to roads. Overall, our study suggests that | 116 | were not scarcer close to roads. Overall, our study suggests that | ||
| 117 | traits provide a basis to identify the passerine species most | 117 | traits provide a basis to identify the passerine species most | ||
| 118 | vulnerable to road collisions, which may be priority targets for | 118 | vulnerable to road collisions, which may be priority targets for | ||
| 119 | future research on the population-level effects of roadkills.", | 119 | future research on the population-level effects of roadkills.", | ||
| 120 | "notes_translated": { | 120 | "notes_translated": { | ||
| 121 | "en": "Collision with vehicles is an important source of bird | 121 | "en": "Collision with vehicles is an important source of bird | ||
| 122 | mortality, but it is uncertain why some species are killed more often | 122 | mortality, but it is uncertain why some species are killed more often | ||
| 123 | than others. Focusing on passerines, we tested whether mortality is | 123 | than others. Focusing on passerines, we tested whether mortality is | ||
| 124 | associated with bird abundances, and with traits reflecting | 124 | associated with bird abundances, and with traits reflecting | ||
| 125 | flight\u00a0manoeuvrability, habitat, diet, and foraging and social | 125 | flight\u00a0manoeuvrability, habitat, diet, and foraging and social | ||
| 126 | behaviours. We also tested whether the species most vulnerable to | 126 | behaviours. We also tested whether the species most vulnerable to | ||
| 127 | road-killing were scarcer near (<\u00a0500\u00a0m) or far | 127 | road-killing were scarcer near (<\u00a0500\u00a0m) or far | ||
| 128 | (>\u00a0500\u20135000\u00a0m) from roads. During the breeding seasons | 128 | (>\u00a0500\u20135000\u00a0m) from roads. During the breeding seasons | ||
| 129 | of 2009\u20132011, we surveyed\u00a0roadkills\u00a0daily along | 129 | of 2009\u20132011, we surveyed\u00a0roadkills\u00a0daily along | ||
| 130 | 50\u00a0km of roads, and estimated bird abundances from 74 point | 130 | 50\u00a0km of roads, and estimated bird abundances from 74 point | ||
| 131 | counts. After correcting for phylogenetic relatedness, there was | 131 | counts. After correcting for phylogenetic relatedness, there was | ||
| 132 | strong correlation between roadkill numbers and the abundances of 28 | 132 | strong correlation between roadkill numbers and the abundances of 28 | ||
| 133 | species counted near roads. However,\u00a0selectivity\u00a0indices | 133 | species counted near roads. However,\u00a0selectivity\u00a0indices | ||
| 134 | indicated that Blue tit (Parus\u00a0caeruleus), Blackcap (Sylvia | 134 | indicated that Blue tit (Parus\u00a0caeruleus), Blackcap (Sylvia | ||
| 135 | atricapilla) and European goldfinch (Carduelis\u00a0carduelis) were | 135 | atricapilla) and European goldfinch (Carduelis\u00a0carduelis) were | ||
| 136 | significantly more road-killed than expected from their abundances, | 136 | significantly more road-killed than expected from their abundances, | ||
| 137 | while the inverse was found for seven species. Using phylogenetic | 137 | while the inverse was found for seven species. Using phylogenetic | ||
| 138 | generalised estimating equations, we found | 138 | generalised estimating equations, we found | ||
| 139 | that\u00a0selectivity\u00a0indexes were strongly related to foraging | 139 | that\u00a0selectivity\u00a0indexes were strongly related to foraging | ||
| 140 | behaviour and habitat type, and weakly so to body size, wing load, | 140 | behaviour and habitat type, and weakly so to body size, wing load, | ||
| 141 | diet and social behaviour. The most vulnerable passerines were | 141 | diet and social behaviour. The most vulnerable passerines were | ||
| 142 | foliage/bark and swoop foragers, inhabiting woodlands, with small body | 142 | foliage/bark and swoop foragers, inhabiting woodlands, with small body | ||
| 143 | size and low wing load. The species most vulnerable to road collisions | 143 | size and low wing load. The species most vulnerable to road collisions | ||
| 144 | were not scarcer close to roads. Overall, our study suggests that | 144 | were not scarcer close to roads. Overall, our study suggests that | ||
| 145 | traits provide a basis to identify the passerine species most | 145 | traits provide a basis to identify the passerine species most | ||
| 146 | vulnerable to road collisions, which may be priority targets for | 146 | vulnerable to road collisions, which may be priority targets for | ||
| 147 | future research on the population-level effects of\u00a0roadkills.", | 147 | future research on the population-level effects of\u00a0roadkills.", | ||
| 148 | "es": "Collision with vehicles is an important source of bird | 148 | "es": "Collision with vehicles is an important source of bird | ||
| 149 | mortality, but it is uncertain why some species are killed more often | 149 | mortality, but it is uncertain why some species are killed more often | ||
| 150 | than others. Focusing on passerines, we tested whether mortality is | 150 | than others. Focusing on passerines, we tested whether mortality is | ||
| 151 | associated with bird abundances, and with traits reflecting flight | 151 | associated with bird abundances, and with traits reflecting flight | ||
| 152 | manoeuvrability, habitat, diet, and foraging and social behaviours. We | 152 | manoeuvrability, habitat, diet, and foraging and social behaviours. We | ||
| 153 | also tested whether the species most vulnerable to road-killing were | 153 | also tested whether the species most vulnerable to road-killing were | ||
| 154 | scarcer near (< 500 m) or far (> 500\u20135000 m) from roads. During | 154 | scarcer near (< 500 m) or far (> 500\u20135000 m) from roads. During | ||
| 155 | the breeding seasons of 2009\u20132011, we surveyed roadkills daily | 155 | the breeding seasons of 2009\u20132011, we surveyed roadkills daily | ||
| 156 | along 50 km of roads, and estimated bird abundances from 74 point | 156 | along 50 km of roads, and estimated bird abundances from 74 point | ||
| 157 | counts. After correcting for phylogenetic relatedness, there was | 157 | counts. After correcting for phylogenetic relatedness, there was | ||
| 158 | strong correlation between roadkill numbers and the abundances of 28 | 158 | strong correlation between roadkill numbers and the abundances of 28 | ||
| 159 | species counted near roads. However, selectivity indices indicated | 159 | species counted near roads. However, selectivity indices indicated | ||
| 160 | that Blue tit (Parus caeruleus), Blackcap (Sylvia atricapilla) and | 160 | that Blue tit (Parus caeruleus), Blackcap (Sylvia atricapilla) and | ||
| 161 | European goldfinch (Carduelis carduelis) were significantly more | 161 | European goldfinch (Carduelis carduelis) were significantly more | ||
| 162 | road-killed than expected from their abundances, while the inverse was | 162 | road-killed than expected from their abundances, while the inverse was | ||
| 163 | found for seven species. Using phylogenetic generalised estimating | 163 | found for seven species. Using phylogenetic generalised estimating | ||
| 164 | equations, we found that selectivity indexes were strongly related to | 164 | equations, we found that selectivity indexes were strongly related to | ||
| 165 | foraging behaviour and habitat type, and weakly so to body size, wing | 165 | foraging behaviour and habitat type, and weakly so to body size, wing | ||
| 166 | load, diet and social behaviour. The most vulnerable passerines were | 166 | load, diet and social behaviour. The most vulnerable passerines were | ||
| 167 | foliage/bark and swoop foragers, inhabiting woodlands, with small body | 167 | foliage/bark and swoop foragers, inhabiting woodlands, with small body | ||
| 168 | size and low wing load. The species most vulnerable to road collisions | 168 | size and low wing load. The species most vulnerable to road collisions | ||
| 169 | were not scarcer close to roads. Overall, our study suggests that | 169 | were not scarcer close to roads. Overall, our study suggests that | ||
| 170 | traits provide a basis to identify the passerine species most | 170 | traits provide a basis to identify the passerine species most | ||
| 171 | vulnerable to road collisions, which may be priority targets for | 171 | vulnerable to road collisions, which may be priority targets for | ||
| 172 | future research on the population-level effects of roadkills." | 172 | future research on the population-level effects of roadkills." | ||
| 173 | }, | 173 | }, | ||
| 174 | "num_resources": 1, | 174 | "num_resources": 1, | ||
| 175 | "num_tags": 2, | 175 | "num_tags": 2, | ||
| 176 | "organization": { | 176 | "organization": { | ||
| 177 | "approval_status": "approved", | 177 | "approval_status": "approved", | ||
| 178 | "created": "2026-06-23T14:36:08.942021", | 178 | "created": "2026-06-23T14:36:08.942021", | ||
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| 197 | "name": "\u00c1rea de Banco de Datos de la Naturaleza. | 197 | "name": "\u00c1rea de Banco de Datos de la Naturaleza. | ||
| 198 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | 198 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | ||
| 199 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | 199 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | ||
| 200 | Demogr\u00e1fico", | 200 | Demogr\u00e1fico", | ||
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| 203 | "url": "https://www.miteco.gob.es/" | 203 | "url": "https://www.miteco.gob.es/" | ||
| 204 | } | 204 | } | ||
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| 206 | "publisher_email": "buzon-bdatos@miteco.es", | 206 | "publisher_email": "buzon-bdatos@miteco.es", | ||
| 207 | "publisher_name": "\u00c1rea de Banco de Datos de la Naturaleza. | 207 | "publisher_name": "\u00c1rea de Banco de Datos de la Naturaleza. | ||
| 208 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | 208 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | ||
| 209 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | 209 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | ||
| 210 | Demogr\u00e1fico", | 210 | Demogr\u00e1fico", | ||
| 211 | "publisher_type": | 211 | "publisher_type": | ||
| 212 | "http://purl.org/adms/publishertype/NationalAuthority", | 212 | "http://purl.org/adms/publishertype/NationalAuthority", | ||
| 213 | "publisher_uri": "https://iepnb.es/catalogo/organization/iepnb", | 213 | "publisher_uri": "https://iepnb.es/catalogo/organization/iepnb", | ||
| 214 | "publisher_url": "https://www.miteco.gob.es/", | 214 | "publisher_url": "https://www.miteco.gob.es/", | ||
| 215 | "purpose": { | 215 | "purpose": { | ||
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| 220 | "relationships_as_object": [], | 220 | "relationships_as_object": [], | ||
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