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En el instante 23 de junio de 2026, 15:51:43 UTC,
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Modificado el valor del campo
spatial_coverage
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en A review of searcher efficiency and carcass persistence in infrastructure-driven mortality assessment studies.
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| 81 | "notes": "Infrastructures in natural areas are expanding rapidly | 81 | "notes": "Infrastructures in natural areas are expanding rapidly | ||
| 82 | worldwide. Consequently, roads, power-lines, and wind-farms cause | 82 | worldwide. Consequently, roads, power-lines, and wind-farms cause | ||
| 83 | millions of fatalities across several animal groups. Assessing the | 83 | millions of fatalities across several animal groups. Assessing the | ||
| 84 | population impact of these infrastructures requires sound estimates of | 84 | population impact of these infrastructures requires sound estimates of | ||
| 85 | the total number of fatalities. These estimates can be heavily biased | 85 | the total number of fatalities. These estimates can be heavily biased | ||
| 86 | due to differences in searcher efficiency and carcass persistence | 86 | due to differences in searcher efficiency and carcass persistence | ||
| 87 | rates, which may ultimately lead to the incorrect quantification of | 87 | rates, which may ultimately lead to the incorrect quantification of | ||
| 88 | actual mortality, or to the inadequate prioritization of locations for | 88 | actual mortality, or to the inadequate prioritization of locations for | ||
| 89 | mitigation. We reviewed 294 studies using carcass surveys conducted | 89 | mitigation. We reviewed 294 studies using carcass surveys conducted | ||
| 90 | worldwide and performed analyses on the effects of variables | 90 | worldwide and performed analyses on the effects of variables | ||
| 91 | potentially influencing searcher efficiency and carcass persistence | 91 | potentially influencing searcher efficiency and carcass persistence | ||
| 92 | rates. Our analytical review, including the largest number of studies | 92 | rates. Our analytical review, including the largest number of studies | ||
| 93 | to date, the use of multivariate approaches, and the study weighting | 93 | to date, the use of multivariate approaches, and the study weighting | ||
| 94 | by sample size, contradicts some previous findings.\n Palabras clave: | 94 | by sample size, contradicts some previous findings.\n Palabras clave: | ||
| 95 | Mortality", | 95 | Mortality", | ||
| 96 | "notes_translated": { | 96 | "notes_translated": { | ||
| 97 | "en": "Infrastructures in natural areas are expanding rapidly | 97 | "en": "Infrastructures in natural areas are expanding rapidly | ||
| 98 | worldwide. Consequently, roads, power-lines, and wind-farms cause | 98 | worldwide. Consequently, roads, power-lines, and wind-farms cause | ||
| 99 | millions of fatalities across several animal groups. Assessing the | 99 | millions of fatalities across several animal groups. Assessing the | ||
| 100 | population impact of these infrastructures requires sound estimates of | 100 | population impact of these infrastructures requires sound estimates of | ||
| 101 | the total number of fatalities. These estimates can be heavily biased | 101 | the total number of fatalities. These estimates can be heavily biased | ||
| 102 | due to differences in searcher efficiency and carcass persistence | 102 | due to differences in searcher efficiency and carcass persistence | ||
| 103 | rates, which may ultimately lead to the incorrect quantification of | 103 | rates, which may ultimately lead to the incorrect quantification of | ||
| 104 | actual mortality, or to the inadequate prioritization of locations for | 104 | actual mortality, or to the inadequate prioritization of locations for | ||
| 105 | mitigation. We reviewed 294 studies using carcass surveys conducted | 105 | mitigation. We reviewed 294 studies using carcass surveys conducted | ||
| 106 | worldwide and performed analyses on the effects of variables | 106 | worldwide and performed analyses on the effects of variables | ||
| 107 | potentially influencing searcher efficiency and carcass persistence | 107 | potentially influencing searcher efficiency and carcass persistence | ||
| 108 | rates. Our analytical review, including the largest number of studies | 108 | rates. Our analytical review, including the largest number of studies | ||
| 109 | to date, the use of multivariate approaches, and the study weighting | 109 | to date, the use of multivariate approaches, and the study weighting | ||
| 110 | by sample size, contradicts some previous findings.", | 110 | by sample size, contradicts some previous findings.", | ||
| 111 | "es": "Infrastructures in natural areas are expanding rapidly | 111 | "es": "Infrastructures in natural areas are expanding rapidly | ||
| 112 | worldwide. Consequently, roads, power-lines, and wind-farms cause | 112 | worldwide. Consequently, roads, power-lines, and wind-farms cause | ||
| 113 | millions of fatalities across several animal groups. Assessing the | 113 | millions of fatalities across several animal groups. Assessing the | ||
| 114 | population impact of these infrastructures requires sound estimates of | 114 | population impact of these infrastructures requires sound estimates of | ||
| 115 | the total number of fatalities. These estimates can be heavily biased | 115 | the total number of fatalities. These estimates can be heavily biased | ||
| 116 | due to differences in searcher efficiency and carcass persistence | 116 | due to differences in searcher efficiency and carcass persistence | ||
| 117 | rates, which may ultimately lead to the incorrect quantification of | 117 | rates, which may ultimately lead to the incorrect quantification of | ||
| 118 | actual mortality, or to the inadequate prioritization of locations for | 118 | actual mortality, or to the inadequate prioritization of locations for | ||
| 119 | mitigation. We reviewed 294 studies using carcass surveys conducted | 119 | mitigation. We reviewed 294 studies using carcass surveys conducted | ||
| 120 | worldwide and performed analyses on the effects of variables | 120 | worldwide and performed analyses on the effects of variables | ||
| 121 | potentially influencing searcher efficiency and carcass persistence | 121 | potentially influencing searcher efficiency and carcass persistence | ||
| 122 | rates. Our analytical review, including the largest number of studies | 122 | rates. Our analytical review, including the largest number of studies | ||
| 123 | to date, the use of multivariate approaches, and the study weighting | 123 | to date, the use of multivariate approaches, and the study weighting | ||
| 124 | by sample size, contradicts some previous findings.\n Palabras clave: | 124 | by sample size, contradicts some previous findings.\n Palabras clave: | ||
| 125 | Mortality" | 125 | Mortality" | ||
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| 241 | ], | ||||
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| 255 | "coordinates": [ | ||||
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| 259 | "type": "Point" | ||||
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| 262 | "uri": | 233 | "uri": | ||
| 263 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | 234 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | ||
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| 267 | "spatial_uri": | 238 | "spatial_uri": | ||
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| 269 | "state": "active", | 240 | "state": "active", | ||
| 270 | "study_variables": { | 241 | "study_variables": { | ||
| 271 | "es": "" | 242 | "es": "" | ||
| 272 | }, | 243 | }, | ||
| 273 | "tag_uri": [ | 244 | "tag_uri": [ | ||
| 274 | 245 | ||||
| 275 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 246 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 276 | ], | 247 | ], | ||
| 277 | "tags": [ | 248 | "tags": [ | ||
| 278 | { | 249 | { | ||
| 279 | "display_name": "accidentes-y-atropellos-de-fauna", | 250 | "display_name": "accidentes-y-atropellos-de-fauna", | ||
| 280 | "id": "629c6d17-b04f-404c-900a-8c31fae0ecc4", | 251 | "id": "629c6d17-b04f-404c-900a-8c31fae0ecc4", | ||
| 281 | "name": "accidentes-y-atropellos-de-fauna", | 252 | "name": "accidentes-y-atropellos-de-fauna", | ||
| 282 | "state": "active", | 253 | "state": "active", | ||
| 283 | "vocabulary_id": null | 254 | "vocabulary_id": null | ||
| 284 | }, | 255 | }, | ||
| 285 | { | 256 | { | ||
| 286 | "display_name": "fragmentacion", | 257 | "display_name": "fragmentacion", | ||
| 287 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | 258 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | ||
| 288 | "name": "fragmentacion", | 259 | "name": "fragmentacion", | ||
| 289 | "state": "active", | 260 | "state": "active", | ||
| 290 | "vocabulary_id": null | 261 | "vocabulary_id": null | ||
| 291 | }, | 262 | }, | ||
| 292 | { | 263 | { | ||
| 293 | "display_name": "mortalidad", | 264 | "display_name": "mortalidad", | ||
| 294 | "id": "94e60fa3-2b44-479b-bea2-82bdb52cdf10", | 265 | "id": "94e60fa3-2b44-479b-bea2-82bdb52cdf10", | ||
| 295 | "name": "mortalidad", | 266 | "name": "mortalidad", | ||
| 296 | "state": "active", | 267 | "state": "active", | ||
| 297 | "vocabulary_id": null | 268 | "vocabulary_id": null | ||
| 298 | } | 269 | } | ||
| 299 | ], | 270 | ], | ||
| 300 | "thematic_area": [ | 271 | "thematic_area": [ | ||
| 301 | "especies_silvestres" | 272 | "especies_silvestres" | ||
| 302 | ], | 273 | ], | ||
| 303 | "theme_es": [ | 274 | "theme_es": [ | ||
| 304 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 275 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 305 | ], | 276 | ], | ||
| 306 | "title": "A review of searcher efficiency and carcass persistence in | 277 | "title": "A review of searcher efficiency and carcass persistence in | ||
| 307 | infrastructure-driven mortality assessment studies.", | 278 | infrastructure-driven mortality assessment studies.", | ||
| 308 | "title_translated": { | 279 | "title_translated": { | ||
| 309 | "en": "", | 280 | "en": "", | ||
| 310 | "es": "A review of searcher efficiency and carcass persistence in | 281 | "es": "A review of searcher efficiency and carcass persistence in | ||
| 311 | infrastructure-driven mortality assessment studies." | 282 | infrastructure-driven mortality assessment studies." | ||
| 312 | }, | 283 | }, | ||
| 313 | "topic": | 284 | "topic": | ||
| 314 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 285 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 315 | "type": "dataset", | 286 | "type": "dataset", | ||
| 316 | "url": | 287 | "url": | ||
| 317 | //iepnb.es:443/catalogo/dataset/de0c2f3c-4012-5f2c-a271-d522a09b3aa5", | 288 | //iepnb.es:443/catalogo/dataset/de0c2f3c-4012-5f2c-a271-d522a09b3aa5", | ||
| 318 | "version": "", | 289 | "version": "", | ||
| 319 | "version_notes": { | 290 | "version_notes": { | ||
| 320 | "en": "", | 291 | "en": "", | ||
| 321 | "es": "" | 292 | "es": "" | ||
| 322 | } | 293 | } | ||
| 323 | } | 294 | } |