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En el instante 23 de junio de 2026, 16:04:38 UTC,
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Modificado el valor del campo
spatial_coverage
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en Modeling the impact of road mortality on barn owl (Tyto alba) populations using age-structured models.
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| 78 | "notes": "Road mortality affects natural populations worldwide. | 78 | "notes": "Road mortality affects natural populations worldwide. | ||
| 79 | Although the effects of road mortality are often documented, studies | 79 | Although the effects of road mortality are often documented, studies | ||
| 80 | assessing the impact of road mortality on the viability of the | 80 | assessing the impact of road mortality on the viability of the | ||
| 81 | affected populations are not so common. In fact, road mortality data | 81 | affected populations are not so common. In fact, road mortality data | ||
| 82 | are often limited to a small number of years from which it is | 82 | are often limited to a small number of years from which it is | ||
| 83 | difficult to build statistical models to assess the impact of road | 83 | difficult to build statistical models to assess the impact of road | ||
| 84 | mortality on population trends, including the probability of | 84 | mortality on population trends, including the probability of | ||
| 85 | extinction. In the last decades several studies have reported a | 85 | extinction. In the last decades several studies have reported a | ||
| 86 | considerable decline in barn owl (Tyto alba) populations attributed | 86 | considerable decline in barn owl (Tyto alba) populations attributed | ||
| 87 | mainly to land use change and to the expansion of the road network to | 87 | mainly to land use change and to the expansion of the road network to | ||
| 88 | accommodate traffic growth. For instance, road monitoring programs | 88 | accommodate traffic growth. For instance, road monitoring programs | ||
| 89 | show high road mortality rates ranging from 0.07 owls/km/year to 2.61 | 89 | show high road mortality rates ranging from 0.07 owls/km/year to 2.61 | ||
| 90 | owls/km/year. We developed a stochastic, age-structured model to | 90 | owls/km/year. We developed a stochastic, age-structured model to | ||
| 91 | evaluate the impact of road-kills on barn owl populations and their | 91 | evaluate the impact of road-kills on barn owl populations and their | ||
| 92 | risk of extinction \u2026\n Palabras clave: Mortality, Population", | 92 | risk of extinction \u2026\n Palabras clave: Mortality, Population", | ||
| 93 | "notes_translated": { | 93 | "notes_translated": { | ||
| 94 | "en": "Road mortality affects natural populations worldwide. | 94 | "en": "Road mortality affects natural populations worldwide. | ||
| 95 | Although the effects of road mortality are often documented, studies | 95 | Although the effects of road mortality are often documented, studies | ||
| 96 | assessing the impact of road mortality on the viability of the | 96 | assessing the impact of road mortality on the viability of the | ||
| 97 | affected populations are not so common. In fact, road mortality data | 97 | affected populations are not so common. In fact, road mortality data | ||
| 98 | are often limited to a small number of years from which it is | 98 | are often limited to a small number of years from which it is | ||
| 99 | difficult to build statistical models to assess the impact of road | 99 | difficult to build statistical models to assess the impact of road | ||
| 100 | mortality on population trends, including the probability of | 100 | mortality on population trends, including the probability of | ||
| 101 | extinction. In the last decades several studies have reported a | 101 | extinction. In the last decades several studies have reported a | ||
| 102 | considerable decline in barn owl (Tyto alba) populations attributed | 102 | considerable decline in barn owl (Tyto alba) populations attributed | ||
| 103 | mainly to land use change and to the expansion of the road network to | 103 | mainly to land use change and to the expansion of the road network to | ||
| 104 | accommodate traffic growth. For instance, road monitoring programs | 104 | accommodate traffic growth. For instance, road monitoring programs | ||
| 105 | show high road mortality rates ranging from 0.07 owls/km/year to 2.61 | 105 | show high road mortality rates ranging from 0.07 owls/km/year to 2.61 | ||
| 106 | owls/km/year. We developed a stochastic, age-structured model to | 106 | owls/km/year. We developed a stochastic, age-structured model to | ||
| 107 | evaluate the impact of road-kills on barn owl populations and their | 107 | evaluate the impact of road-kills on barn owl populations and their | ||
| 108 | risk of extinction \u2026", | 108 | risk of extinction \u2026", | ||
| 109 | "es": "Road mortality affects natural populations worldwide. | 109 | "es": "Road mortality affects natural populations worldwide. | ||
| 110 | Although the effects of road mortality are often documented, studies | 110 | Although the effects of road mortality are often documented, studies | ||
| 111 | assessing the impact of road mortality on the viability of the | 111 | assessing the impact of road mortality on the viability of the | ||
| 112 | affected populations are not so common. In fact, road mortality data | 112 | affected populations are not so common. In fact, road mortality data | ||
| 113 | are often limited to a small number of years from which it is | 113 | are often limited to a small number of years from which it is | ||
| 114 | difficult to build statistical models to assess the impact of road | 114 | difficult to build statistical models to assess the impact of road | ||
| 115 | mortality on population trends, including the probability of | 115 | mortality on population trends, including the probability of | ||
| 116 | extinction. In the last decades several studies have reported a | 116 | extinction. In the last decades several studies have reported a | ||
| 117 | considerable decline in barn owl (Tyto alba) populations attributed | 117 | considerable decline in barn owl (Tyto alba) populations attributed | ||
| 118 | mainly to land use change and to the expansion of the road network to | 118 | mainly to land use change and to the expansion of the road network to | ||
| 119 | accommodate traffic growth. For instance, road monitoring programs | 119 | accommodate traffic growth. For instance, road monitoring programs | ||
| 120 | show high road mortality rates ranging from 0.07 owls/km/year to 2.61 | 120 | show high road mortality rates ranging from 0.07 owls/km/year to 2.61 | ||
| 121 | owls/km/year. We developed a stochastic, age-structured model to | 121 | owls/km/year. We developed a stochastic, age-structured model to | ||
| 122 | evaluate the impact of road-kills on barn owl populations and their | 122 | evaluate the impact of road-kills on barn owl populations and their | ||
| 123 | risk of extinction \u2026\n Palabras clave: Mortality, Population" | 123 | risk of extinction \u2026\n Palabras clave: Mortality, Population" | ||
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| 253 | "coordinates": [ | ||||
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| 256 | ], | ||||
| 257 | "type": "Point" | ||||
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| 260 | "uri": | 231 | "uri": | ||
| 261 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | 232 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | ||
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| 265 | "spatial_uri": | 236 | "spatial_uri": | ||
| 266 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | 237 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | ||
| 267 | "state": "active", | 238 | "state": "active", | ||
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| 272 | 243 | ||||
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| 274 | ], | 245 | ], | ||
| 275 | "tags": [ | 246 | "tags": [ | ||
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| 277 | "display_name": "accidentes-y-atropellos-de-fauna", | 248 | "display_name": "accidentes-y-atropellos-de-fauna", | ||
| 278 | "id": "629c6d17-b04f-404c-900a-8c31fae0ecc4", | 249 | "id": "629c6d17-b04f-404c-900a-8c31fae0ecc4", | ||
| 279 | "name": "accidentes-y-atropellos-de-fauna", | 250 | "name": "accidentes-y-atropellos-de-fauna", | ||
| 280 | "state": "active", | 251 | "state": "active", | ||
| 281 | "vocabulary_id": null | 252 | "vocabulary_id": null | ||
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| 284 | "display_name": "fragmentacion", | 255 | "display_name": "fragmentacion", | ||
| 285 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | 256 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | ||
| 286 | "name": "fragmentacion", | 257 | "name": "fragmentacion", | ||
| 287 | "state": "active", | 258 | "state": "active", | ||
| 288 | "vocabulary_id": null | 259 | "vocabulary_id": null | ||
| 289 | }, | 260 | }, | ||
| 290 | { | 261 | { | ||
| 291 | "display_name": "mortalidad", | 262 | "display_name": "mortalidad", | ||
| 292 | "id": "94e60fa3-2b44-479b-bea2-82bdb52cdf10", | 263 | "id": "94e60fa3-2b44-479b-bea2-82bdb52cdf10", | ||
| 293 | "name": "mortalidad", | 264 | "name": "mortalidad", | ||
| 294 | "state": "active", | 265 | "state": "active", | ||
| 295 | "vocabulary_id": null | 266 | "vocabulary_id": null | ||
| 296 | }, | 267 | }, | ||
| 297 | { | 268 | { | ||
| 298 | "display_name": "poblacion", | 269 | "display_name": "poblacion", | ||
| 299 | "id": "e104a1ee-9489-4d5e-bb7b-7ecfe1899b23", | 270 | "id": "e104a1ee-9489-4d5e-bb7b-7ecfe1899b23", | ||
| 300 | "name": "poblacion", | 271 | "name": "poblacion", | ||
| 301 | "state": "active", | 272 | "state": "active", | ||
| 302 | "vocabulary_id": null | 273 | "vocabulary_id": null | ||
| 303 | } | 274 | } | ||
| 304 | ], | 275 | ], | ||
| 305 | "thematic_area": [ | 276 | "thematic_area": [ | ||
| 306 | "especies_silvestres" | 277 | "especies_silvestres" | ||
| 307 | ], | 278 | ], | ||
| 308 | "theme_es": [ | 279 | "theme_es": [ | ||
| 309 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 280 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 310 | ], | 281 | ], | ||
| 311 | "title": "Modeling the impact of road mortality on barn owl (Tyto | 282 | "title": "Modeling the impact of road mortality on barn owl (Tyto | ||
| 312 | alba) populations using age-structured models.", | 283 | alba) populations using age-structured models.", | ||
| 313 | "title_translated": { | 284 | "title_translated": { | ||
| 314 | "en": "", | 285 | "en": "", | ||
| 315 | "es": "Modeling the impact of road mortality on barn owl (Tyto | 286 | "es": "Modeling the impact of road mortality on barn owl (Tyto | ||
| 316 | alba) populations using age-structured models." | 287 | alba) populations using age-structured models." | ||
| 317 | }, | 288 | }, | ||
| 318 | "topic": | 289 | "topic": | ||
| 319 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 290 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 320 | "type": "dataset", | 291 | "type": "dataset", | ||
| 321 | "url": | 292 | "url": | ||
| 322 | //iepnb.es:443/catalogo/dataset/85ed3801-a7eb-55da-b404-56520cc51bbb", | 293 | //iepnb.es:443/catalogo/dataset/85ed3801-a7eb-55da-b404-56520cc51bbb", | ||
| 323 | "version": "", | 294 | "version": "", | ||
| 324 | "version_notes": { | 295 | "version_notes": { | ||
| 325 | "en": "", | 296 | "en": "", | ||
| 326 | "es": "" | 297 | "es": "" | ||
| 327 | } | 298 | } | ||
| 328 | } | 299 | } |