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En el instante 25 de junio de 2026, 12:43:11 UTC,
-
Modificado el valor del campo
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a2026-06-25
en Assessing large-scale wildlife responses to human infrastructure development. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Assessing large-scale wildlife responses to human infrastructure development.
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| 77 | "name": "14f22233-2606-5a9e-b34b-4d4dfe5f5fdb", | 91 | "name": "14f22233-2606-5a9e-b34b-4d4dfe5f5fdb", | ||
| 78 | "notes": "Habitat loss and deterioration represent the main threats | 92 | "notes": "Habitat loss and deterioration represent the main threats | ||
| 79 | to wildlife species, and are closely linked to the expansion of roads | 93 | to wildlife species, and are closely linked to the expansion of roads | ||
| 80 | and human settlements. Unfortunately, large-scale effects of these | 94 | and human settlements. Unfortunately, large-scale effects of these | ||
| 81 | structures remain generally overlooked. Here, we analyzed the European | 95 | structures remain generally overlooked. Here, we analyzed the European | ||
| 82 | transportation infrastructure network and found that 50% of the | 96 | transportation infrastructure network and found that 50% of the | ||
| 83 | continent is within 1.5 km of transportation infrastructure. We | 97 | continent is within 1.5 km of transportation infrastructure. We | ||
| 84 | present a method for assessing the impacts from infrastructure on | 98 | present a method for assessing the impacts from infrastructure on | ||
| 85 | wildlife, based on functional response curves describing density | 99 | wildlife, based on functional response curves describing density | ||
| 86 | reductions in birds and mammals (e.g., road-effect zones), and apply | 100 | 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 | 101 | 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 | 102 | 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 | 103 | mammals), with moderate declines predicted for birds (22.6% of | ||
| 90 | individuals) and severe declines predicted for mammals (46.6%). | 104 | individuals) and severe declines predicted for mammals (46.6%). | ||
| 91 | Despite certain limitations, we suggest the approach proposed is | 105 | Despite certain limitations, we suggest the approach proposed is | ||
| 92 | widely applicable to the evaluation of effects of planned | 106 | widely applicable to the evaluation of effects of planned | ||
| 93 | infrastructure developments under multiple scenarios, and propose an | 107 | infrastructure developments under multiple scenarios, and propose an | ||
| 94 | internationally coordinated strategy to update and improve it in the | 108 | internationally coordinated strategy to update and improve it in the | ||
| 95 | future.", | 109 | future.", | ||
| 96 | "notes_translated": { | 110 | "notes_translated": { | ||
| 97 | "en": "Habitat loss and deterioration represent the main threats | 111 | "en": "Habitat loss and deterioration represent the main threats | ||
| 98 | to wildlife species, and are closely linked to the expansion of roads | 112 | to wildlife species, and are closely linked to the expansion of roads | ||
| 99 | and human settlements. Unfortunately, large-scale effects of these | 113 | and human settlements. Unfortunately, large-scale effects of these | ||
| 100 | structures remain generally overlooked. Here, we analyzed the European | 114 | structures remain generally overlooked. Here, we analyzed the European | ||
| 101 | transportation infrastructure network and found that 50% of the | 115 | transportation infrastructure network and found that 50% of the | ||
| 102 | continent is within 1.5 km of transportation infrastructure. We | 116 | continent is within 1.5 km of transportation infrastructure. We | ||
| 103 | present a method for assessing the impacts from infrastructure on | 117 | present a method for assessing the impacts from infrastructure on | ||
| 104 | wildlife, based on functional response curves describing density | 118 | wildlife, based on functional response curves describing density | ||
| 105 | reductions in birds and mammals (e.g., road-effect zones), and apply | 119 | 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 | 120 | 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 | 121 | 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 | 122 | mammals), with moderate declines predicted for birds (22.6% of | ||
| 109 | individuals) and severe declines predicted for mammals (46.6%). | 123 | individuals) and severe declines predicted for mammals (46.6%). | ||
| 110 | Despite certain limitations, we suggest the approach proposed is | 124 | Despite certain limitations, we suggest the approach proposed is | ||
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| 112 | infrastructure developments under multiple scenarios, and propose an | 126 | infrastructure developments under multiple scenarios, and propose an | ||
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| 115 | "es": "Habitat loss and deterioration represent the main threats | 129 | "es": "Habitat loss and deterioration represent the main threats | ||
| 116 | to wildlife species, and are closely linked to the expansion of roads | 130 | to wildlife species, and are closely linked to the expansion of roads | ||
| 117 | and human settlements. Unfortunately, large-scale effects of these | 131 | and human settlements. Unfortunately, large-scale effects of these | ||
| 118 | structures remain generally overlooked. Here, we analyzed the European | 132 | structures remain generally overlooked. Here, we analyzed the European | ||
| 119 | transportation infrastructure network and found that 50% of the | 133 | transportation infrastructure network and found that 50% of the | ||
| 120 | continent is within 1.5 km of transportation infrastructure. We | 134 | continent is within 1.5 km of transportation infrastructure. We | ||
| 121 | present a method for assessing the impacts from infrastructure on | 135 | present a method for assessing the impacts from infrastructure on | ||
| 122 | wildlife, based on functional response curves describing density | 136 | wildlife, based on functional response curves describing density | ||
| 123 | reductions in birds and mammals (e.g., road-effect zones), and apply | 137 | 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 | 138 | 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 | 139 | 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 | 140 | mammals), with moderate declines predicted for birds (22.6% of | ||
| 127 | individuals) and severe declines predicted for mammals (46.6%). | 141 | individuals) and severe declines predicted for mammals (46.6%). | ||
| 128 | Despite certain limitations, we suggest the approach proposed is | 142 | Despite certain limitations, we suggest the approach proposed is | ||
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| 130 | infrastructure developments under multiple scenarios, and propose an | 144 | infrastructure developments under multiple scenarios, and propose an | ||
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| 230 | 27.64]]]}", | 244 | 27.64]]]}", | ||
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| 232 | { | 246 | { | ||
| 233 | "bbox": "{\"type\": \"Polygon\", \"coordinates\": [[[-18.16, | 247 | "bbox": "{\"type\": \"Polygon\", \"coordinates\": [[[-18.16, | ||
| 234 | 27.64], [4.32, 27.64], [4.32, 43.79], [-18.16, 43.79], [-18.16, | 248 | 27.64], [4.32, 27.64], [4.32, 43.79], [-18.16, 43.79], [-18.16, | ||
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| 237 | 35.715]}", | 251 | 35.715]}", | ||
| 238 | "text": "Espa\u00f1a", | 252 | "text": "Espa\u00f1a", | ||
| 239 | "uri": | 253 | "uri": | ||
| 240 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | 254 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | ||
| 241 | } | 255 | } | ||
| 242 | ], | 256 | ], | ||
| 243 | "spatial_resolution_in_meters": "", | 257 | "spatial_resolution_in_meters": "", | ||
| 244 | "spatial_uri": | 258 | "spatial_uri": | ||
| 245 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | 259 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | ||
| 246 | "state": "active", | 260 | "state": "active", | ||
| 247 | "study_variables": { | 261 | "study_variables": { | ||
| 248 | "es": "" | 262 | "es": "" | ||
| 249 | }, | 263 | }, | ||
| 250 | "tag_uri": [ | 264 | "tag_uri": [ | ||
| 251 | 265 | ||||
| 252 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 266 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 253 | ], | 267 | ], | ||
| 254 | "tags": [ | 268 | "tags": [ | ||
| 255 | { | 269 | { | ||
| 256 | "display_name": "aspectos-globales-sobre-fragmentacion-de", | 270 | "display_name": "aspectos-globales-sobre-fragmentacion-de", | ||
| 257 | "id": "2379c860-0540-450a-9a23-72454ee80469", | 271 | "id": "2379c860-0540-450a-9a23-72454ee80469", | ||
| 258 | "name": "aspectos-globales-sobre-fragmentacion-de", | 272 | "name": "aspectos-globales-sobre-fragmentacion-de", | ||
| 259 | "state": "active", | 273 | "state": "active", | ||
| 260 | "vocabulary_id": null | 274 | "vocabulary_id": null | ||
| 261 | }, | 275 | }, | ||
| 262 | { | 276 | { | ||
| 263 | "display_name": "fragmentacion", | 277 | "display_name": "fragmentacion", | ||
| 264 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | 278 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | ||
| 265 | "name": "fragmentacion", | 279 | "name": "fragmentacion", | ||
| 266 | "state": "active", | 280 | "state": "active", | ||
| 267 | "vocabulary_id": null | 281 | "vocabulary_id": null | ||
| 268 | } | 282 | } | ||
| 269 | ], | 283 | ], | ||
| 270 | "thematic_area": [ | 284 | "thematic_area": [ | ||
| 271 | "especies_silvestres" | 285 | "especies_silvestres" | ||
| 272 | ], | 286 | ], | ||
| 273 | "theme_es": [ | 287 | "theme_es": [ | ||
| 274 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 288 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 275 | ], | 289 | ], | ||
| 276 | "title": "Assessing large-scale wildlife responses to human | 290 | "title": "Assessing large-scale wildlife responses to human | ||
| 277 | infrastructure development.", | 291 | infrastructure development.", | ||
| 278 | "title_translated": { | 292 | "title_translated": { | ||
| 279 | "en": "", | 293 | "en": "", | ||
| 280 | "es": "Assessing large-scale wildlife responses to human | 294 | "es": "Assessing large-scale wildlife responses to human | ||
| 281 | infrastructure development." | 295 | infrastructure development." | ||
| 282 | }, | 296 | }, | ||
| 283 | "topic": | 297 | "topic": | ||
| 284 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 298 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 285 | "type": "dataset", | 299 | "type": "dataset", | ||
| 286 | "url": | 300 | "url": | ||
| 287 | //iepnb.es:443/catalogo/dataset/14f22233-2606-5a9e-b34b-4d4dfe5f5fdb", | 301 | //iepnb.es:443/catalogo/dataset/14f22233-2606-5a9e-b34b-4d4dfe5f5fdb", | ||
| 288 | "version": "", | 302 | "version": "", | ||
| 289 | "version_notes": { | 303 | "version_notes": { | ||
| 290 | "en": "", | 304 | "en": "", | ||
| 291 | "es": "" | 305 | "es": "" | ||
| 292 | } | 306 | } | ||
| 293 | } | 307 | } |