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En el instante 23 de junio de 2026, 16:13:09 UTC,
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Modificado el valor del campo
spatial_coverage
a[{'bbox': '{"type": "Polygon", "coordinates": [[[-18.16, 27.64], [4.32, 27.64], [4.32, 43.79], [-18.16, 43.79], [-18.16, 27.64]]]}', 'centroid': '{"type": "Point", "coordinates": [-6.92, 35.715]}', 'text': 'España', 'uri': 'http://datos.gob.es/recurso/sector-publico/territorio/Pais/España'}]
en Assessing large-scale wildlife responses to human infrastructure development.
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| 78 | "notes": "Habitat loss and deterioration represent the main threats | 78 | "notes": "Habitat loss and deterioration represent the main threats | ||
| 79 | to wildlife species, and are closely linked to the expansion of roads | 79 | to wildlife species, and are closely linked to the expansion of roads | ||
| 80 | and human settlements. Unfortunately, large-scale effects of these | 80 | and human settlements. Unfortunately, large-scale effects of these | ||
| 81 | structures remain generally overlooked. Here, we analyzed the European | 81 | structures remain generally overlooked. Here, we analyzed the European | ||
| 82 | transportation infrastructure network and found that 50% of the | 82 | transportation infrastructure network and found that 50% of the | ||
| 83 | continent is within 1.5 km of transportation infrastructure. We | 83 | continent is within 1.5 km of transportation infrastructure. We | ||
| 84 | present a method for assessing the impacts from infrastructure on | 84 | present a method for assessing the impacts from infrastructure on | ||
| 85 | wildlife, based on functional response curves describing density | 85 | wildlife, based on functional response curves describing density | ||
| 86 | reductions in birds and mammals (e.g., road-effect zones), and apply | 86 | reductions in birds and mammals (e.g., road-effect zones), and apply | ||
| 87 | it to Spain as a case study. The imprint of infrastructure extends | 87 | it to Spain as a case study. The imprint of infrastructure extends | ||
| 88 | over most of the country (55.5% in the case of birds and 97.9% for | 88 | over most of the country (55.5% in the case of birds and 97.9% for | ||
| 89 | mammals), with moderate declines predicted for birds (22.6% of | 89 | mammals), with moderate declines predicted for birds (22.6% of | ||
| 90 | individuals) and severe declines predicted for mammals (46.6%). | 90 | individuals) and severe declines predicted for mammals (46.6%). | ||
| 91 | Despite certain limitations, we suggest the approach proposed is | 91 | Despite certain limitations, we suggest the approach proposed is | ||
| 92 | widely applicable to the evaluation of effects of planned | 92 | widely applicable to the evaluation of effects of planned | ||
| 93 | infrastructure developments under multiple scenarios, and propose an | 93 | infrastructure developments under multiple scenarios, and propose an | ||
| 94 | internationally coordinated strategy to update and improve it in the | 94 | internationally coordinated strategy to update and improve it in the | ||
| 95 | future.", | 95 | future.", | ||
| 96 | "notes_translated": { | 96 | "notes_translated": { | ||
| 97 | "en": "Habitat loss and deterioration represent the main threats | 97 | "en": "Habitat loss and deterioration represent the main threats | ||
| 98 | to wildlife species, and are closely linked to the expansion of roads | 98 | to wildlife species, and are closely linked to the expansion of roads | ||
| 99 | and human settlements. Unfortunately, large-scale effects of these | 99 | and human settlements. Unfortunately, large-scale effects of these | ||
| 100 | structures remain generally overlooked. Here, we analyzed the European | 100 | structures remain generally overlooked. Here, we analyzed the European | ||
| 101 | transportation infrastructure network and found that 50% of the | 101 | transportation infrastructure network and found that 50% of the | ||
| 102 | continent is within 1.5 km of transportation infrastructure. We | 102 | continent is within 1.5 km of transportation infrastructure. We | ||
| 103 | present a method for assessing the impacts from infrastructure on | 103 | present a method for assessing the impacts from infrastructure on | ||
| 104 | wildlife, based on functional response curves describing density | 104 | wildlife, based on functional response curves describing density | ||
| 105 | reductions in birds and mammals (e.g., road-effect zones), and apply | 105 | reductions in birds and mammals (e.g., road-effect zones), and apply | ||
| 106 | it to Spain as a case study. The imprint of infrastructure extends | 106 | it to Spain as a case study. The imprint of infrastructure extends | ||
| 107 | over most of the country (55.5% in the case of birds and 97.9% for | 107 | over most of the country (55.5% in the case of birds and 97.9% for | ||
| 108 | mammals), with moderate declines predicted for birds (22.6% of | 108 | mammals), with moderate declines predicted for birds (22.6% of | ||
| 109 | individuals) and severe declines predicted for mammals (46.6%). | 109 | individuals) and severe declines predicted for mammals (46.6%). | ||
| 110 | Despite certain limitations, we suggest the approach proposed is | 110 | Despite certain limitations, we suggest the approach proposed is | ||
| 111 | widely applicable to the evaluation of effects of planned | 111 | widely applicable to the evaluation of effects of planned | ||
| 112 | infrastructure developments under multiple scenarios, and propose an | 112 | infrastructure developments under multiple scenarios, and propose an | ||
| 113 | internationally coordinated strategy to update and improve it in the | 113 | internationally coordinated strategy to update and improve it in the | ||
| 114 | future.", | 114 | future.", | ||
| 115 | "es": "Habitat loss and deterioration represent the main threats | 115 | "es": "Habitat loss and deterioration represent the main threats | ||
| 116 | to wildlife species, and are closely linked to the expansion of roads | 116 | to wildlife species, and are closely linked to the expansion of roads | ||
| 117 | and human settlements. Unfortunately, large-scale effects of these | 117 | and human settlements. Unfortunately, large-scale effects of these | ||
| 118 | structures remain generally overlooked. Here, we analyzed the European | 118 | structures remain generally overlooked. Here, we analyzed the European | ||
| 119 | transportation infrastructure network and found that 50% of the | 119 | transportation infrastructure network and found that 50% of the | ||
| 120 | continent is within 1.5 km of transportation infrastructure. We | 120 | continent is within 1.5 km of transportation infrastructure. We | ||
| 121 | present a method for assessing the impacts from infrastructure on | 121 | present a method for assessing the impacts from infrastructure on | ||
| 122 | wildlife, based on functional response curves describing density | 122 | wildlife, based on functional response curves describing density | ||
| 123 | reductions in birds and mammals (e.g., road-effect zones), and apply | 123 | reductions in birds and mammals (e.g., road-effect zones), and apply | ||
| 124 | it to Spain as a case study. The imprint of infrastructure extends | 124 | it to Spain as a case study. The imprint of infrastructure extends | ||
| 125 | over most of the country (55.5% in the case of birds and 97.9% for | 125 | over most of the country (55.5% in the case of birds and 97.9% for | ||
| 126 | mammals), with moderate declines predicted for birds (22.6% of | 126 | mammals), with moderate declines predicted for birds (22.6% of | ||
| 127 | individuals) and severe declines predicted for mammals (46.6%). | 127 | individuals) and severe declines predicted for mammals (46.6%). | ||
| 128 | Despite certain limitations, we suggest the approach proposed is | 128 | Despite certain limitations, we suggest the approach proposed is | ||
| 129 | widely applicable to the evaluation of effects of planned | 129 | widely applicable to the evaluation of effects of planned | ||
| 130 | infrastructure developments under multiple scenarios, and propose an | 130 | infrastructure developments under multiple scenarios, and propose an | ||
| 131 | internationally coordinated strategy to update and improve it in the | 131 | internationally coordinated strategy to update and improve it in the | ||
| 132 | future." | 132 | future." | ||
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| 247 | ], | ||||
| 248 | [ | ||||
| 249 | -18.16, | ||||
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| 251 | ], | ||||
| 252 | [ | ||||
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| 256 | ] | ||||
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| 261 | "coordinates": [ | ||||
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| 263 | 35.715 | ||||
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| 268 | "uri": | 239 | "uri": | ||
| 269 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | 240 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | ||
| 270 | } | 241 | } | ||
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| 272 | "spatial_resolution_in_meters": "", | 243 | "spatial_resolution_in_meters": "", | ||
| 273 | "spatial_uri": | 244 | "spatial_uri": | ||
| 274 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | 245 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | ||
| 275 | "state": "active", | 246 | "state": "active", | ||
| 276 | "study_variables": { | 247 | "study_variables": { | ||
| 277 | "es": "" | 248 | "es": "" | ||
| 278 | }, | 249 | }, | ||
| 279 | "tag_uri": [ | 250 | "tag_uri": [ | ||
| 280 | 251 | ||||
| 281 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 252 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 282 | ], | 253 | ], | ||
| 283 | "tags": [ | 254 | "tags": [ | ||
| 284 | { | 255 | { | ||
| 285 | "display_name": "aspectos-globales-sobre-fragmentacion-de", | 256 | "display_name": "aspectos-globales-sobre-fragmentacion-de", | ||
| 286 | "id": "2379c860-0540-450a-9a23-72454ee80469", | 257 | "id": "2379c860-0540-450a-9a23-72454ee80469", | ||
| 287 | "name": "aspectos-globales-sobre-fragmentacion-de", | 258 | "name": "aspectos-globales-sobre-fragmentacion-de", | ||
| 288 | "state": "active", | 259 | "state": "active", | ||
| 289 | "vocabulary_id": null | 260 | "vocabulary_id": null | ||
| 290 | }, | 261 | }, | ||
| 291 | { | 262 | { | ||
| 292 | "display_name": "fragmentacion", | 263 | "display_name": "fragmentacion", | ||
| 293 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | 264 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | ||
| 294 | "name": "fragmentacion", | 265 | "name": "fragmentacion", | ||
| 295 | "state": "active", | 266 | "state": "active", | ||
| 296 | "vocabulary_id": null | 267 | "vocabulary_id": null | ||
| 297 | } | 268 | } | ||
| 298 | ], | 269 | ], | ||
| 299 | "thematic_area": [ | 270 | "thematic_area": [ | ||
| 300 | "especies_silvestres" | 271 | "especies_silvestres" | ||
| 301 | ], | 272 | ], | ||
| 302 | "theme_es": [ | 273 | "theme_es": [ | ||
| 303 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 274 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 304 | ], | 275 | ], | ||
| 305 | "title": "Assessing large-scale wildlife responses to human | 276 | "title": "Assessing large-scale wildlife responses to human | ||
| 306 | infrastructure development.", | 277 | infrastructure development.", | ||
| 307 | "title_translated": { | 278 | "title_translated": { | ||
| 308 | "en": "", | 279 | "en": "", | ||
| 309 | "es": "Assessing large-scale wildlife responses to human | 280 | "es": "Assessing large-scale wildlife responses to human | ||
| 310 | infrastructure development." | 281 | infrastructure development." | ||
| 311 | }, | 282 | }, | ||
| 312 | "topic": | 283 | "topic": | ||
| 313 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 284 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 314 | "type": "dataset", | 285 | "type": "dataset", | ||
| 315 | "url": | 286 | "url": | ||
| 316 | //iepnb.es:443/catalogo/dataset/14f22233-2606-5a9e-b34b-4d4dfe5f5fdb", | 287 | //iepnb.es:443/catalogo/dataset/14f22233-2606-5a9e-b34b-4d4dfe5f5fdb", | ||
| 317 | "version": "", | 288 | "version": "", | ||
| 318 | "version_notes": { | 289 | "version_notes": { | ||
| 319 | "en": "", | 290 | "en": "", | ||
| 320 | "es": "" | 291 | "es": "" | ||
| 321 | } | 292 | } | ||
| 322 | } | 293 | } |