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En el instante 23 de junio de 2026, 16:01:06 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 Road and topography effects on invasion: edge effects in rat foraging patterns in two oceanic island forests (Tenerife, Canary Islands).
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| 82 | "notes": "We studied the effect of road edges on foraging activity | 82 | "notes": "We studied the effect of road edges on foraging activity | ||
| 83 | by introduced ship or roof rats Rattus rattus in road-fragmented | 83 | by introduced ship or roof rats Rattus rattus in road-fragmented | ||
| 84 | laurel and pine forests on Tenerife (Canary Islands). By using | 84 | laurel and pine forests on Tenerife (Canary Islands). By using | ||
| 85 | selective baited stations enabling only foraging by rats we assessed | 85 | selective baited stations enabling only foraging by rats we assessed | ||
| 86 | bait removal rates along a road-interior gradient and different | 86 | bait removal rates along a road-interior gradient and different | ||
| 87 | topographic locations. We recorded higher removal rates in the laurel | 87 | topographic locations. We recorded higher removal rates in the laurel | ||
| 88 | than in the pine forest regardless of the distance to road. We | 88 | than in the pine forest regardless of the distance to road. We | ||
| 89 | detected an edge effect of paved roads on introduced rat foraging. | 89 | detected an edge effect of paved roads on introduced rat foraging. | ||
| 90 | Removal rates were significantly greater along road edges than in | 90 | Removal rates were significantly greater along road edges than in | ||
| 91 | forest interior in the laurel forest but not in the pine forest. Rats | 91 | forest interior in the laurel forest but not in the pine forest. Rats | ||
| 92 | were more active along road habitats in forest ridges and slopes than | 92 | were more active along road habitats in forest ridges and slopes than | ||
| 93 | in ravine beds in the laurel forest. There was no difference between | 93 | in ravine beds in the laurel forest. There was no difference between | ||
| 94 | topographic locations in rat activity at any distance from the road in | 94 | topographic locations in rat activity at any distance from the road in | ||
| 95 | the pine forest. It is suggested that variation in foraging intensity | 95 | the pine forest. It is suggested that variation in foraging intensity | ||
| 96 | by introduced rats in road-fragmented forests on these islands may | 96 | by introduced rats in road-fragmented forests on these islands may | ||
| 97 | depend, among other factors, on forest type, road edge effects and | 97 | depend, among other factors, on forest type, road edge effects and | ||
| 98 | topographic pattern of the landscape.", | 98 | topographic pattern of the landscape.", | ||
| 99 | "notes_translated": { | 99 | "notes_translated": { | ||
| 100 | "en": "We studied the effect of road edges on foraging activity by | 100 | "en": "We studied the effect of road edges on foraging activity by | ||
| 101 | introduced ship or roof rats Rattus rattus in road-fragmented laurel | 101 | introduced ship or roof rats Rattus rattus in road-fragmented laurel | ||
| 102 | and pine forests on Tenerife (Canary Islands). By using selective | 102 | and pine forests on Tenerife (Canary Islands). By using selective | ||
| 103 | baited stations enabling only foraging by rats we assessed bait | 103 | baited stations enabling only foraging by rats we assessed bait | ||
| 104 | removal rates along a road-interior gradient and different topographic | 104 | removal rates along a road-interior gradient and different topographic | ||
| 105 | locations. We recorded higher removal rates in the laurel than in the | 105 | locations. We recorded higher removal rates in the laurel than in the | ||
| 106 | pine forest regardless of the distance to road. We detected an edge | 106 | pine forest regardless of the distance to road. We detected an edge | ||
| 107 | effect of paved roads on introduced rat foraging. Removal rates were | 107 | effect of paved roads on introduced rat foraging. Removal rates were | ||
| 108 | significantly greater along road edges than in forest interior in the | 108 | significantly greater along road edges than in forest interior in the | ||
| 109 | laurel forest but not in the pine forest. Rats were more active along | 109 | laurel forest but not in the pine forest. Rats were more active along | ||
| 110 | road habitats in forest ridges and slopes than in ravine beds in the | 110 | road habitats in forest ridges and slopes than in ravine beds in the | ||
| 111 | laurel forest. There was no difference between topographic locations | 111 | laurel forest. There was no difference between topographic locations | ||
| 112 | in rat activity at any distance from the road in the pine forest. It | 112 | in rat activity at any distance from the road in the pine forest. It | ||
| 113 | is suggested that variation in foraging intensity by introduced rats | 113 | is suggested that variation in foraging intensity by introduced rats | ||
| 114 | in road-fragmented forests on these islands may depend, among other | 114 | in road-fragmented forests on these islands may depend, among other | ||
| 115 | factors, on forest type, road edge effects and topographic pattern of | 115 | factors, on forest type, road edge effects and topographic pattern of | ||
| 116 | the landscape.", | 116 | the landscape.", | ||
| 117 | "es": "We studied the effect of road edges on foraging activity by | 117 | "es": "We studied the effect of road edges on foraging activity by | ||
| 118 | introduced ship or roof rats Rattus rattus in road-fragmented laurel | 118 | introduced ship or roof rats Rattus rattus in road-fragmented laurel | ||
| 119 | and pine forests on Tenerife (Canary Islands). By using selective | 119 | and pine forests on Tenerife (Canary Islands). By using selective | ||
| 120 | baited stations enabling only foraging by rats we assessed bait | 120 | baited stations enabling only foraging by rats we assessed bait | ||
| 121 | removal rates along a road-interior gradient and different topographic | 121 | removal rates along a road-interior gradient and different topographic | ||
| 122 | locations. We recorded higher removal rates in the laurel than in the | 122 | locations. We recorded higher removal rates in the laurel than in the | ||
| 123 | pine forest regardless of the distance to road. We detected an edge | 123 | pine forest regardless of the distance to road. We detected an edge | ||
| 124 | effect of paved roads on introduced rat foraging. Removal rates were | 124 | effect of paved roads on introduced rat foraging. Removal rates were | ||
| 125 | significantly greater along road edges than in forest interior in the | 125 | significantly greater along road edges than in forest interior in the | ||
| 126 | laurel forest but not in the pine forest. Rats were more active along | 126 | laurel forest but not in the pine forest. Rats were more active along | ||
| 127 | road habitats in forest ridges and slopes than in ravine beds in the | 127 | road habitats in forest ridges and slopes than in ravine beds in the | ||
| 128 | laurel forest. There was no difference between topographic locations | 128 | laurel forest. There was no difference between topographic locations | ||
| 129 | in rat activity at any distance from the road in the pine forest. It | 129 | in rat activity at any distance from the road in the pine forest. It | ||
| 130 | is suggested that variation in foraging intensity by introduced rats | 130 | is suggested that variation in foraging intensity by introduced rats | ||
| 131 | in road-fragmented forests on these islands may depend, among other | 131 | in road-fragmented forests on these islands may depend, among other | ||
| 132 | factors, on forest type, road edge effects and topographic pattern of | 132 | factors, on forest type, road edge effects and topographic pattern of | ||
| 133 | the landscape." | 133 | the landscape." | ||
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| 241 | ], | ||||
| 242 | [ | ||||
| 243 | 4.32, | ||||
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| 246 | [ | ||||
| 247 | 4.32, | ||||
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| 249 | ], | ||||
| 250 | [ | ||||
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| 269 | "text": "Espa\u00f1a", | 240 | "text": "Espa\u00f1a", | ||
| 270 | "uri": | 241 | "uri": | ||
| 271 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | 242 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | ||
| 272 | } | 243 | } | ||
| 273 | ], | 244 | ], | ||
| 274 | "spatial_resolution_in_meters": "", | 245 | "spatial_resolution_in_meters": "", | ||
| 275 | "spatial_uri": | 246 | "spatial_uri": | ||
| 276 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | 247 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | ||
| 277 | "state": "active", | 248 | "state": "active", | ||
| 278 | "study_variables": { | 249 | "study_variables": { | ||
| 279 | "es": "" | 250 | "es": "" | ||
| 280 | }, | 251 | }, | ||
| 281 | "tag_uri": [ | 252 | "tag_uri": [ | ||
| 282 | 253 | ||||
| 283 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 254 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 284 | ], | 255 | ], | ||
| 285 | "tags": [ | 256 | "tags": [ | ||
| 286 | { | 257 | { | ||
| 287 | "display_name": "efectos-de-borde-y-margen-asociados-a-la", | 258 | "display_name": "efectos-de-borde-y-margen-asociados-a-la", | ||
| 288 | "id": "430b41a3-9e45-421d-92e3-00d12878405d", | 259 | "id": "430b41a3-9e45-421d-92e3-00d12878405d", | ||
| 289 | "name": "efectos-de-borde-y-margen-asociados-a-la", | 260 | "name": "efectos-de-borde-y-margen-asociados-a-la", | ||
| 290 | "state": "active", | 261 | "state": "active", | ||
| 291 | "vocabulary_id": null | 262 | "vocabulary_id": null | ||
| 292 | }, | 263 | }, | ||
| 293 | { | 264 | { | ||
| 294 | "display_name": "fragmentacion", | 265 | "display_name": "fragmentacion", | ||
| 295 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | 266 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | ||
| 296 | "name": "fragmentacion", | 267 | "name": "fragmentacion", | ||
| 297 | "state": "active", | 268 | "state": "active", | ||
| 298 | "vocabulary_id": null | 269 | "vocabulary_id": null | ||
| 299 | } | 270 | } | ||
| 300 | ], | 271 | ], | ||
| 301 | "thematic_area": [ | 272 | "thematic_area": [ | ||
| 302 | "especies_silvestres" | 273 | "especies_silvestres" | ||
| 303 | ], | 274 | ], | ||
| 304 | "theme_es": [ | 275 | "theme_es": [ | ||
| 305 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 276 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 306 | ], | 277 | ], | ||
| 307 | "title": "Road and topography effects on invasion: edge effects in | 278 | "title": "Road and topography effects on invasion: edge effects in | ||
| 308 | rat foraging patterns in two oceanic island forests (Tenerife, Canary | 279 | rat foraging patterns in two oceanic island forests (Tenerife, Canary | ||
| 309 | Islands).", | 280 | Islands).", | ||
| 310 | "title_translated": { | 281 | "title_translated": { | ||
| 311 | "en": "", | 282 | "en": "", | ||
| 312 | "es": "Road and topography effects on invasion: edge effects in | 283 | "es": "Road and topography effects on invasion: edge effects in | ||
| 313 | rat foraging patterns in two oceanic island forests (Tenerife, Canary | 284 | rat foraging patterns in two oceanic island forests (Tenerife, Canary | ||
| 314 | Islands)." | 285 | Islands)." | ||
| 315 | }, | 286 | }, | ||
| 316 | "topic": | 287 | "topic": | ||
| 317 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 288 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 318 | "type": "dataset", | 289 | "type": "dataset", | ||
| 319 | "url": | 290 | "url": | ||
| 320 | //iepnb.es:443/catalogo/dataset/b4df30dc-d79e-51e3-b329-e1f154c58b44", | 291 | //iepnb.es:443/catalogo/dataset/b4df30dc-d79e-51e3-b329-e1f154c58b44", | ||
| 321 | "version": "", | 292 | "version": "", | ||
| 322 | "version_notes": { | 293 | "version_notes": { | ||
| 323 | "en": "", | 294 | "en": "", | ||
| 324 | "es": "" | 295 | "es": "" | ||
| 325 | } | 296 | } | ||
| 326 | } | 297 | } |