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En el instante 23 de junio de 2026, 16:12:27 UTC,
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Modificado el valor del campo
spatial_coverage
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en Effects of traffic noise on paserine populations in Mediterranean wooded pastures.
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| 79 | "notes": "The effect of traffic noise on the breeding density of 20 | 79 | "notes": "The effect of traffic noise on the breeding density of 20 | ||
| 80 | passerine species was examined over a 2-year period in three different | 80 | passerine species was examined over a 2-year period in three different | ||
| 81 | road types passing through pasture-woodlands in western-central Spain. | 81 | road types passing through pasture-woodlands in western-central Spain. | ||
| 82 | No statistically significant differences were observed during the 2 | 82 | No statistically significant differences were observed during the 2 | ||
| 83 | years studied. An average of 19.6 birds/10 ha was recorded for the | 83 | years studied. An average of 19.6 birds/10 ha was recorded for the | ||
| 84 | low-traffic road (LT), 21.7 birds/10 ha for the medium-traffic road | 84 | low-traffic road (LT), 21.7 birds/10 ha for the medium-traffic road | ||
| 85 | (MT) and 19.1 birds/10 ha for the high-traffic road (HT). A total of | 85 | (MT) and 19.1 birds/10 ha for the high-traffic road (HT). A total of | ||
| 86 | 11 species (55%) did not show any statistically significant | 86 | 11 species (55%) did not show any statistically significant | ||
| 87 | differences in breeding density among the different types of roads. By | 87 | differences in breeding density among the different types of roads. By | ||
| 88 | contrast, other species, such as the Blackbird, the Iberian Shrike and | 88 | contrast, other species, such as the Blackbird, the Iberian Shrike and | ||
| 89 | the Linnet, did point to differences between the MT and HT roads. | 89 | the Linnet, did point to differences between the MT and HT roads. | ||
| 90 | House and Rock Sparrows, as well as the Corn Bunting, showed higher | 90 | House and Rock Sparrows, as well as the Corn Bunting, showed higher | ||
| 91 | breeding densities near the HT road. The opposite effect was observed | 91 | breeding densities near the HT road. The opposite effect was observed | ||
| 92 | for the Wheatear, the Iberian chiffchaff and the Woodlark, for which | 92 | for the Wheatear, the Iberian chiffchaff and the Woodlark, for which | ||
| 93 | high breeding densities were recorded in the vicinity of the LT road. | 93 | high breeding densities were recorded in the vicinity of the LT road. | ||
| 94 | Our results suggest that traffic noise constitutes a serious problem | 94 | Our results suggest that traffic noise constitutes a serious problem | ||
| 95 | for at least 15% of the breeding bird community.\n Palabras clave: | 95 | for at least 15% of the breeding bird community.\n Palabras clave: | ||
| 96 | Noise, Population", | 96 | Noise, Population", | ||
| 97 | "notes_translated": { | 97 | "notes_translated": { | ||
| 98 | "en": "The effect of traffic noise on the breeding density of 20 | 98 | "en": "The effect of traffic noise on the breeding density of 20 | ||
| 99 | passerine species was examined over a 2-year period in three different | 99 | passerine species was examined over a 2-year period in three different | ||
| 100 | road types passing through pasture-woodlands in western-central Spain. | 100 | road types passing through pasture-woodlands in western-central Spain. | ||
| 101 | No statistically significant differences were observed during the 2 | 101 | No statistically significant differences were observed during the 2 | ||
| 102 | years studied. An average of 19.6 birds/10 ha was recorded for the | 102 | years studied. An average of 19.6 birds/10 ha was recorded for the | ||
| 103 | low-traffic road (LT), 21.7 birds/10 ha for the medium-traffic road | 103 | low-traffic road (LT), 21.7 birds/10 ha for the medium-traffic road | ||
| 104 | (MT) and 19.1 birds/10 ha for the high-traffic road (HT). A total of | 104 | (MT) and 19.1 birds/10 ha for the high-traffic road (HT). A total of | ||
| 105 | 11 species (55%) did not show any statistically significant | 105 | 11 species (55%) did not show any statistically significant | ||
| 106 | differences in breeding density among the different types of roads. By | 106 | differences in breeding density among the different types of roads. By | ||
| 107 | contrast, other species, such as the Blackbird, the Iberian Shrike and | 107 | contrast, other species, such as the Blackbird, the Iberian Shrike and | ||
| 108 | the Linnet, did point to differences between the MT and HT roads. | 108 | the Linnet, did point to differences between the MT and HT roads. | ||
| 109 | House and Rock Sparrows, as well as the Corn Bunting, showed higher | 109 | House and Rock Sparrows, as well as the Corn Bunting, showed higher | ||
| 110 | breeding densities near the HT road. The opposite effect was observed | 110 | breeding densities near the HT road. The opposite effect was observed | ||
| 111 | for the Wheatear, the Iberian chiffchaff and the \u2026", | 111 | for the Wheatear, the Iberian chiffchaff and the \u2026", | ||
| 112 | "es": "The effect of traffic noise on the breeding density of 20 | 112 | "es": "The effect of traffic noise on the breeding density of 20 | ||
| 113 | passerine species was examined over a 2-year period in three different | 113 | passerine species was examined over a 2-year period in three different | ||
| 114 | road types passing through pasture-woodlands in western-central Spain. | 114 | road types passing through pasture-woodlands in western-central Spain. | ||
| 115 | No statistically significant differences were observed during the 2 | 115 | No statistically significant differences were observed during the 2 | ||
| 116 | years studied. An average of 19.6 birds/10 ha was recorded for the | 116 | years studied. An average of 19.6 birds/10 ha was recorded for the | ||
| 117 | low-traffic road (LT), 21.7 birds/10 ha for the medium-traffic road | 117 | low-traffic road (LT), 21.7 birds/10 ha for the medium-traffic road | ||
| 118 | (MT) and 19.1 birds/10 ha for the high-traffic road (HT). A total of | 118 | (MT) and 19.1 birds/10 ha for the high-traffic road (HT). A total of | ||
| 119 | 11 species (55%) did not show any statistically significant | 119 | 11 species (55%) did not show any statistically significant | ||
| 120 | differences in breeding density among the different types of roads. By | 120 | differences in breeding density among the different types of roads. By | ||
| 121 | contrast, other species, such as the Blackbird, the Iberian Shrike and | 121 | contrast, other species, such as the Blackbird, the Iberian Shrike and | ||
| 122 | the Linnet, did point to differences between the MT and HT roads. | 122 | the Linnet, did point to differences between the MT and HT roads. | ||
| 123 | House and Rock Sparrows, as well as the Corn Bunting, showed higher | 123 | House and Rock Sparrows, as well as the Corn Bunting, showed higher | ||
| 124 | breeding densities near the HT road. The opposite effect was observed | 124 | breeding densities near the HT road. The opposite effect was observed | ||
| 125 | for the Wheatear, the Iberian chiffchaff and the Woodlark, for which | 125 | for the Wheatear, the Iberian chiffchaff and the Woodlark, for which | ||
| 126 | high breeding densities were recorded in the vicinity of the LT road. | 126 | high breeding densities were recorded in the vicinity of the LT road. | ||
| 127 | Our results suggest that traffic noise constitutes a serious problem | 127 | Our results suggest that traffic noise constitutes a serious problem | ||
| 128 | for at least 15% of the breeding bird community.\n Palabras clave: | 128 | for at least 15% of the breeding bird community.\n Palabras clave: | ||
| 129 | Noise, Population" | 129 | Noise, Population" | ||
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| 229 | "spatial_coverage": [ | 229 | "spatial_coverage": [ | ||
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| 237 | ], | ||||
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| 245 | ], | ||||
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| 265 | "text": "Espa\u00f1a", | 236 | "text": "Espa\u00f1a", | ||
| 266 | "uri": | 237 | "uri": | ||
| 267 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | 238 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | ||
| 268 | } | 239 | } | ||
| 269 | ], | 240 | ], | ||
| 270 | "spatial_resolution_in_meters": "", | 241 | "spatial_resolution_in_meters": "", | ||
| 271 | "spatial_uri": | 242 | "spatial_uri": | ||
| 272 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | 243 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | ||
| 273 | "state": "active", | 244 | "state": "active", | ||
| 274 | "study_variables": { | 245 | "study_variables": { | ||
| 275 | "es": "" | 246 | "es": "" | ||
| 276 | }, | 247 | }, | ||
| 277 | "tag_uri": [ | 248 | "tag_uri": [ | ||
| 278 | 249 | ||||
| 279 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 250 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 280 | ], | 251 | ], | ||
| 281 | "tags": [ | 252 | "tags": [ | ||
| 282 | { | 253 | { | ||
| 283 | "display_name": "efectos-de-borde-y-margen-asociados-a-la", | 254 | "display_name": "efectos-de-borde-y-margen-asociados-a-la", | ||
| 284 | "id": "430b41a3-9e45-421d-92e3-00d12878405d", | 255 | "id": "430b41a3-9e45-421d-92e3-00d12878405d", | ||
| 285 | "name": "efectos-de-borde-y-margen-asociados-a-la", | 256 | "name": "efectos-de-borde-y-margen-asociados-a-la", | ||
| 286 | "state": "active", | 257 | "state": "active", | ||
| 287 | "vocabulary_id": null | 258 | "vocabulary_id": null | ||
| 288 | }, | 259 | }, | ||
| 289 | { | 260 | { | ||
| 290 | "display_name": "fragmentacion", | 261 | "display_name": "fragmentacion", | ||
| 291 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | 262 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | ||
| 292 | "name": "fragmentacion", | 263 | "name": "fragmentacion", | ||
| 293 | "state": "active", | 264 | "state": "active", | ||
| 294 | "vocabulary_id": null | 265 | "vocabulary_id": null | ||
| 295 | }, | 266 | }, | ||
| 296 | { | 267 | { | ||
| 297 | "display_name": "poblacion", | 268 | "display_name": "poblacion", | ||
| 298 | "id": "e104a1ee-9489-4d5e-bb7b-7ecfe1899b23", | 269 | "id": "e104a1ee-9489-4d5e-bb7b-7ecfe1899b23", | ||
| 299 | "name": "poblacion", | 270 | "name": "poblacion", | ||
| 300 | "state": "active", | 271 | "state": "active", | ||
| 301 | "vocabulary_id": null | 272 | "vocabulary_id": null | ||
| 302 | }, | 273 | }, | ||
| 303 | { | 274 | { | ||
| 304 | "display_name": "ruido", | 275 | "display_name": "ruido", | ||
| 305 | "id": "90d12c64-cb61-42f6-a5ad-d04402740345", | 276 | "id": "90d12c64-cb61-42f6-a5ad-d04402740345", | ||
| 306 | "name": "ruido", | 277 | "name": "ruido", | ||
| 307 | "state": "active", | 278 | "state": "active", | ||
| 308 | "vocabulary_id": null | 279 | "vocabulary_id": null | ||
| 309 | } | 280 | } | ||
| 310 | ], | 281 | ], | ||
| 311 | "thematic_area": [ | 282 | "thematic_area": [ | ||
| 312 | "especies_silvestres" | 283 | "especies_silvestres" | ||
| 313 | ], | 284 | ], | ||
| 314 | "theme_es": [ | 285 | "theme_es": [ | ||
| 315 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 286 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 316 | ], | 287 | ], | ||
| 317 | "title": "Effects of traffic noise on paserine populations in | 288 | "title": "Effects of traffic noise on paserine populations in | ||
| 318 | Mediterranean wooded pastures.", | 289 | Mediterranean wooded pastures.", | ||
| 319 | "title_translated": { | 290 | "title_translated": { | ||
| 320 | "en": "", | 291 | "en": "", | ||
| 321 | "es": "Effects of traffic noise on paserine populations in | 292 | "es": "Effects of traffic noise on paserine populations in | ||
| 322 | Mediterranean wooded pastures." | 293 | Mediterranean wooded pastures." | ||
| 323 | }, | 294 | }, | ||
| 324 | "topic": | 295 | "topic": | ||
| 325 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 296 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 326 | "type": "dataset", | 297 | "type": "dataset", | ||
| 327 | "url": | 298 | "url": | ||
| 328 | //iepnb.es:443/catalogo/dataset/1e619a9d-b2df-59dd-8a11-9ae13d613763", | 299 | //iepnb.es:443/catalogo/dataset/1e619a9d-b2df-59dd-8a11-9ae13d613763", | ||
| 329 | "version": "", | 300 | "version": "", | ||
| 330 | "version_notes": { | 301 | "version_notes": { | ||
| 331 | "en": "", | 302 | "en": "", | ||
| 332 | "es": "" | 303 | "es": "" | ||
| 333 | } | 304 | } | ||
| 334 | } | 305 | } |