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En el instante 23 de junio de 2026, 16:13:16 UTC,
-
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 Reduced bird occurrence in pine forest fragments associated with road proximity in a Mediterranean agricultural area.
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| 79 | "notes": "This study investigated the effect of road and highway | 79 | "notes": "This study investigated the effect of road and highway | ||
| 80 | proximity on the occurrence of bird species in isolated secondary pine | 80 | proximity on the occurrence of bird species in isolated secondary pine | ||
| 81 | forest fragments in an agricultural matrix. We assessed the effects of | 81 | forest fragments in an agricultural matrix. We assessed the effects of | ||
| 82 | road proximity separately for three different groups of bird species | 82 | road proximity separately for three different groups of bird species | ||
| 83 | in order to detect ecological responses related to species biology. | 83 | in order to detect ecological responses related to species biology. | ||
| 84 | Bird occurrence was mainly related to fragment size but also to | 84 | Bird occurrence was mainly related to fragment size but also to | ||
| 85 | vegetation structure and fragment connectivity. When corrected for | 85 | vegetation structure and fragment connectivity. When corrected for | ||
| 86 | patch characteristics, we found that fragments up to 2 km away from a | 86 | patch characteristics, we found that fragments up to 2 km away from a | ||
| 87 | main highway contained less forest species, both generalists and | 87 | main highway contained less forest species, both generalists and | ||
| 88 | specialists than fragments more distantly located. This pattern was | 88 | specialists than fragments more distantly located. This pattern was | ||
| 89 | independent of the side of the highway analysed. Considering each bird | 89 | independent of the side of the highway analysed. Considering each bird | ||
| 90 | species separately, we found consistent lower occurrence probabilities | 90 | species separately, we found consistent lower occurrence probabilities | ||
| 91 | near the highway in 50% of forest species. This difference was not | 91 | near the highway in 50% of forest species. This difference was not | ||
| 92 | found for ubiquitous species that were to some extent positively | 92 | found for ubiquitous species that were to some extent positively | ||
| 93 | influenced by proximity of other major roads. Our results suggest that | 93 | influenced by proximity of other major roads. Our results suggest that | ||
| 94 | highway proximity, but not that of other major roads, decrease | 94 | highway proximity, but not that of other major roads, decrease | ||
| 95 | occupancy probability of forest birds in isolated forest fragments, | 95 | occupancy probability of forest birds in isolated forest fragments, | ||
| 96 | thus reducing probability of metapopulation persistence. Although low | 96 | thus reducing probability of metapopulation persistence. Although low | ||
| 97 | habitat quality as a result of noise disturbance is likely to account | 97 | habitat quality as a result of noise disturbance is likely to account | ||
| 98 | for some of the results, the long distance effect detected strongly | 98 | for some of the results, the long distance effect detected strongly | ||
| 99 | suggests that other factors rather than direct traffic disturbance | 99 | suggests that other factors rather than direct traffic disturbance | ||
| 100 | alone are involved in lower bird occurrences near the highway. | 100 | alone are involved in lower bird occurrences near the highway. | ||
| 101 | Decreased connectivity among forest fragments associated to avoidance | 101 | Decreased connectivity among forest fragments associated to avoidance | ||
| 102 | of areas near the highway is an alternative explanation to the results | 102 | of areas near the highway is an alternative explanation to the results | ||
| 103 | obtained. We suggest that these findings should be included in | 103 | obtained. We suggest that these findings should be included in | ||
| 104 | strategic environmental impact assessment studies conducted to | 104 | strategic environmental impact assessment studies conducted to | ||
| 105 | determine the ecological impact of large transport infrastructures | 105 | determine the ecological impact of large transport infrastructures | ||
| 106 | across highly fragmented landscapes.", | 106 | across highly fragmented landscapes.", | ||
| 107 | "notes_translated": { | 107 | "notes_translated": { | ||
| 108 | "en": "This study investigated the effect of road and highway | 108 | "en": "This study investigated the effect of road and highway | ||
| 109 | proximity on the occurrence of bird species in isolated secondary pine | 109 | proximity on the occurrence of bird species in isolated secondary pine | ||
| 110 | forest fragments in an agricultural matrix. We assessed the effects of | 110 | forest fragments in an agricultural matrix. We assessed the effects of | ||
| 111 | road proximity separately for three different groups of bird species | 111 | road proximity separately for three different groups of bird species | ||
| 112 | in order to detect ecological responses related to species biology. | 112 | in order to detect ecological responses related to species biology. | ||
| 113 | Bird occurrence was mainly related to fragment size but also to | 113 | Bird occurrence was mainly related to fragment size but also to | ||
| 114 | vegetation structure and fragment connectivity. When corrected for | 114 | vegetation structure and fragment connectivity. When corrected for | ||
| 115 | patch characteristics, we found that fragments up to 2 km away from a | 115 | patch characteristics, we found that fragments up to 2 km away from a | ||
| 116 | main highway contained less forest species, both generalists and | 116 | main highway contained less forest species, both generalists and | ||
| 117 | specialists than fragments more distantly located. This pattern was | 117 | specialists than fragments more distantly located. This pattern was | ||
| 118 | independent of the side of the highway analysed. Considering each bird | 118 | independent of the side of the highway analysed. Considering each bird | ||
| 119 | species separately, we found consistent lower occurrence probabilities | 119 | species separately, we found consistent lower occurrence probabilities | ||
| 120 | near the highway in 50% of forest species. This difference was not | 120 | near the highway in 50% of forest species. This difference was not | ||
| 121 | found for ubiquitous species that were to some extent positively | 121 | found for ubiquitous species that were to some extent positively | ||
| 122 | influenced by proximity of other major roads. Our results suggest that | 122 | influenced by proximity of other major roads. Our results suggest that | ||
| 123 | highway proximity, but not that of other major roads, decrease | 123 | highway proximity, but not that of other major roads, decrease | ||
| 124 | occupancy probability of forest birds in isolated forest fragments, | 124 | occupancy probability of forest birds in isolated forest fragments, | ||
| 125 | thus reducing probability of metapopulation persistence. Although low | 125 | thus reducing probability of metapopulation persistence. Although low | ||
| 126 | habitat quality as a result of noise disturbance is likely to account | 126 | habitat quality as a result of noise disturbance is likely to account | ||
| 127 | for some of the results, the long distance effect detected strongly | 127 | for some of the results, the long distance effect detected strongly | ||
| 128 | suggests that other factors rather than direct traffic disturbance | 128 | suggests that other factors rather than direct traffic disturbance | ||
| 129 | alone are involved in lower bird occurrences near the highway. | 129 | alone are involved in lower bird occurrences near the highway. | ||
| 130 | Decreased connectivity among forest fragments associated to avoidance | 130 | Decreased connectivity among forest fragments associated to avoidance | ||
| 131 | of areas near the highway is an alternative explanation to the results | 131 | of areas near the highway is an alternative explanation to the results | ||
| 132 | obtained. We suggest that these findings should be included in | 132 | obtained. We suggest that these findings should be included in | ||
| 133 | strategic environmental impact assessment studies conducted to | 133 | strategic environmental impact assessment studies conducted to | ||
| 134 | determine the ecological impact of large transport infrastructures | 134 | determine the ecological impact of large transport infrastructures | ||
| 135 | across highly fragmented landscapes.", | 135 | across highly fragmented landscapes.", | ||
| 136 | "es": "This study investigated the effect of road and highway | 136 | "es": "This study investigated the effect of road and highway | ||
| 137 | proximity on the occurrence of bird species in isolated secondary pine | 137 | proximity on the occurrence of bird species in isolated secondary pine | ||
| 138 | forest fragments in an agricultural matrix. We assessed the effects of | 138 | forest fragments in an agricultural matrix. We assessed the effects of | ||
| 139 | road proximity separately for three different groups of bird species | 139 | road proximity separately for three different groups of bird species | ||
| 140 | in order to detect ecological responses related to species biology. | 140 | in order to detect ecological responses related to species biology. | ||
| 141 | Bird occurrence was mainly related to fragment size but also to | 141 | Bird occurrence was mainly related to fragment size but also to | ||
| 142 | vegetation structure and fragment connectivity. When corrected for | 142 | vegetation structure and fragment connectivity. When corrected for | ||
| 143 | patch characteristics, we found that fragments up to 2 km away from a | 143 | patch characteristics, we found that fragments up to 2 km away from a | ||
| 144 | main highway contained less forest species, both generalists and | 144 | main highway contained less forest species, both generalists and | ||
| 145 | specialists than fragments more distantly located. This pattern was | 145 | specialists than fragments more distantly located. This pattern was | ||
| 146 | independent of the side of the highway analysed. Considering each bird | 146 | independent of the side of the highway analysed. Considering each bird | ||
| 147 | species separately, we found consistent lower occurrence probabilities | 147 | species separately, we found consistent lower occurrence probabilities | ||
| 148 | near the highway in 50% of forest species. This difference was not | 148 | near the highway in 50% of forest species. This difference was not | ||
| 149 | found for ubiquitous species that were to some extent positively | 149 | found for ubiquitous species that were to some extent positively | ||
| 150 | influenced by proximity of other major roads. Our results suggest that | 150 | influenced by proximity of other major roads. Our results suggest that | ||
| 151 | highway proximity, but not that of other major roads, decrease | 151 | highway proximity, but not that of other major roads, decrease | ||
| 152 | occupancy probability of forest birds in isolated forest fragments, | 152 | occupancy probability of forest birds in isolated forest fragments, | ||
| 153 | thus reducing probability of metapopulation persistence. Although low | 153 | thus reducing probability of metapopulation persistence. Although low | ||
| 154 | habitat quality as a result of noise disturbance is likely to account | 154 | habitat quality as a result of noise disturbance is likely to account | ||
| 155 | for some of the results, the long distance effect detected strongly | 155 | for some of the results, the long distance effect detected strongly | ||
| 156 | suggests that other factors rather than direct traffic disturbance | 156 | suggests that other factors rather than direct traffic disturbance | ||
| 157 | alone are involved in lower bird occurrences near the highway. | 157 | alone are involved in lower bird occurrences near the highway. | ||
| 158 | Decreased connectivity among forest fragments associated to avoidance | 158 | Decreased connectivity among forest fragments associated to avoidance | ||
| 159 | of areas near the highway is an alternative explanation to the results | 159 | of areas near the highway is an alternative explanation to the results | ||
| 160 | obtained. We suggest that these findings should be included in | 160 | obtained. We suggest that these findings should be included in | ||
| 161 | strategic environmental impact assessment studies conducted to | 161 | strategic environmental impact assessment studies conducted to | ||
| 162 | determine the ecological impact of large transport infrastructures | 162 | determine the ecological impact of large transport infrastructures | ||
| 163 | across highly fragmented landscapes." | 163 | across highly fragmented landscapes." | ||
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| 254 | ps://www.sciencedirect.com/science/article/abs/pii/S0169204601001918", | 254 | ps://www.sciencedirect.com/science/article/abs/pii/S0169204601001918", | ||
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| 299 | "text": "Espa\u00f1a", | 270 | "text": "Espa\u00f1a", | ||
| 300 | "uri": | 271 | "uri": | ||
| 301 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | 272 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | ||
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| 312 | 283 | ||||
| 313 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 284 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 314 | ], | 285 | ], | ||
| 315 | "tags": [ | 286 | "tags": [ | ||
| 316 | { | 287 | { | ||
| 317 | "display_name": "fragmentacion", | 288 | "display_name": "fragmentacion", | ||
| 318 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | 289 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | ||
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| 324 | "display_name": "otros-recursos-que-incluyen-informacion-", | 295 | "display_name": "otros-recursos-que-incluyen-informacion-", | ||
| 325 | "id": "2b3610b7-85fe-495c-990a-40e99a432df1", | 296 | "id": "2b3610b7-85fe-495c-990a-40e99a432df1", | ||
| 326 | "name": "otros-recursos-que-incluyen-informacion-", | 297 | "name": "otros-recursos-que-incluyen-informacion-", | ||
| 327 | "state": "active", | 298 | "state": "active", | ||
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| 329 | } | 300 | } | ||
| 330 | ], | 301 | ], | ||
| 331 | "thematic_area": [ | 302 | "thematic_area": [ | ||
| 332 | "especies_silvestres" | 303 | "especies_silvestres" | ||
| 333 | ], | 304 | ], | ||
| 334 | "theme_es": [ | 305 | "theme_es": [ | ||
| 335 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 306 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 336 | ], | 307 | ], | ||
| 337 | "title": "Reduced bird occurrence in pine forest fragments | 308 | "title": "Reduced bird occurrence in pine forest fragments | ||
| 338 | associated with road proximity in a Mediterranean agricultural area.", | 309 | associated with road proximity in a Mediterranean agricultural area.", | ||
| 339 | "title_translated": { | 310 | "title_translated": { | ||
| 340 | "en": "", | 311 | "en": "", | ||
| 341 | "es": "Reduced bird occurrence in pine forest fragments associated | 312 | "es": "Reduced bird occurrence in pine forest fragments associated | ||
| 342 | with road proximity in a Mediterranean agricultural area." | 313 | with road proximity in a Mediterranean agricultural area." | ||
| 343 | }, | 314 | }, | ||
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| 346 | "type": "dataset", | 317 | "type": "dataset", | ||
| 347 | "url": | 318 | "url": | ||
| 348 | //iepnb.es:443/catalogo/dataset/13b2b78d-1999-5997-a7d5-884a97165e48", | 319 | //iepnb.es:443/catalogo/dataset/13b2b78d-1999-5997-a7d5-884a97165e48", | ||
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| 354 | } | 325 | } |