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a2026-06-25
en Road edge effect and elevation patterns of native and alien plants on an oceanic island (Tenerife, Canary Islands). -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Road edge effect and elevation patterns of native and alien plants on an oceanic island (Tenerife, Canary Islands).
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| 82 | "notes": "We studied road edge effects on floristic composition and | 96 | "notes": "We studied road edge effects on floristic composition and | ||
| 83 | richness of alien and native plants on five zonal ecosystems, | 97 | richness of alien and native plants on five zonal ecosystems, | ||
| 84 | following a steep altitudinal gradient from arid coastal and | 98 | following a steep altitudinal gradient from arid coastal and | ||
| 85 | mid-elevation scrublands, through laurel and pine forests, to summit | 99 | mid-elevation scrublands, through laurel and pine forests, to summit | ||
| 86 | scrub, on Tenerife (Canary Islands). We analyzed vegetation within | 100 | scrub, on Tenerife (Canary Islands). We analyzed vegetation within | ||
| 87 | transects running from the road edge to the core of natural habitats. | 101 | transects running from the road edge to the core of natural habitats. | ||
| 88 | Alien richness significantly decreased with distance to road edge for | 102 | Alien richness significantly decreased with distance to road edge for | ||
| 89 | most ecosystems. Native richness also decreased with increasing road | 103 | most ecosystems. Native richness also decreased with increasing road | ||
| 90 | distance for the coastal scrub and pine forest, but increased for the | 104 | distance for the coastal scrub and pine forest, but increased for the | ||
| 91 | thermophilous scrub. We found a decrease in both native and alien | 105 | thermophilous scrub. We found a decrease in both native and alien | ||
| 92 | species richness with elevation. Our results suggest that road edge | 106 | species richness with elevation. Our results suggest that road edge | ||
| 93 | effects in alien plant invasion are stronger in native shrub | 107 | effects in alien plant invasion are stronger in native shrub | ||
| 94 | communities at low elevations than in forests (laurel and Canary | 108 | communities at low elevations than in forests (laurel and Canary | ||
| 95 | Island pine forest), where aliens were limited to a narrow road edge | 109 | Island pine forest), where aliens were limited to a narrow road edge | ||
| 96 | band. Detrended correspondence analyses showed that road edge plots | 110 | band. Detrended correspondence analyses showed that road edge plots | ||
| 97 | were floristically very different from interior plots and that each | 111 | were floristically very different from interior plots and that each | ||
| 98 | ecosystem harboured a specific alien assemblage with few species | 112 | ecosystem harboured a specific alien assemblage with few species | ||
| 99 | present in more than one ecosystem, suggesting a marked species | 113 | present in more than one ecosystem, suggesting a marked species | ||
| 100 | turnover of roadside alien species across altitudinal belts up to the | 114 | turnover of roadside alien species across altitudinal belts up to the | ||
| 101 | pine forest. However, at high elevations, very few aliens invaded | 115 | pine forest. However, at high elevations, very few aliens invaded | ||
| 102 | roadsides, probably due to harsh environmental conditions and still | 116 | roadsides, probably due to harsh environmental conditions and still | ||
| 103 | relatively low propagule pressure.", | 117 | relatively low propagule pressure.", | ||
| 104 | "notes_translated": { | 118 | "notes_translated": { | ||
| 105 | "en": "We studied road edge effects on floristic composition and | 119 | "en": "We studied road edge effects on floristic composition and | ||
| 106 | richness of alien and native plants on five zonal ecosystems, | 120 | richness of alien and native plants on five zonal ecosystems, | ||
| 107 | following a steep altitudinal gradient from arid coastal and | 121 | following a steep altitudinal gradient from arid coastal and | ||
| 108 | mid-elevation scrublands, through laurel and pine forests, to summit | 122 | mid-elevation scrublands, through laurel and pine forests, to summit | ||
| 109 | scrub, on Tenerife (Canary Islands). We analyzed vegetation within | 123 | scrub, on Tenerife (Canary Islands). We analyzed vegetation within | ||
| 110 | transects running from the road edge to the core of natural habitats. | 124 | transects running from the road edge to the core of natural habitats. | ||
| 111 | Alien richness significantly decreased with distance to road edge for | 125 | Alien richness significantly decreased with distance to road edge for | ||
| 112 | most ecosystems. Native richness also decreased with increasing road | 126 | most ecosystems. Native richness also decreased with increasing road | ||
| 113 | distance for the coastal scrub and pine forest, but increased for the | 127 | distance for the coastal scrub and pine forest, but increased for the | ||
| 114 | thermophilous scrub. We found a decrease in both native and alien | 128 | thermophilous scrub. We found a decrease in both native and alien | ||
| 115 | species richness with elevation. Our results suggest that road edge | 129 | species richness with elevation. Our results suggest that road edge | ||
| 116 | effects in alien plant invasion are stronger in native shrub | 130 | effects in alien plant invasion are stronger in native shrub | ||
| 117 | communities at low elevations than in forests (laurel and Canary | 131 | communities at low elevations than in forests (laurel and Canary | ||
| 118 | Island pine forest), where aliens were limited to a narrow road edge | 132 | Island pine forest), where aliens were limited to a narrow road edge | ||
| 119 | band. Detrended correspondence analyses showed that road edge plots | 133 | band. Detrended correspondence analyses showed that road edge plots | ||
| 120 | were floristically very different from interior plots and that each | 134 | were floristically very different from interior plots and that each | ||
| 121 | ecosystem harboured a specific alien assemblage with few species | 135 | ecosystem harboured a specific alien assemblage with few species | ||
| 122 | present in more than one ecosystem, suggesting a marked species | 136 | present in more than one ecosystem, suggesting a marked species | ||
| 123 | turnover of roadside alien species across altitudinal belts up to the | 137 | turnover of roadside alien species across altitudinal belts up to the | ||
| 124 | pine forest. However, at high elevations, very few aliens invaded | 138 | pine forest. However, at high elevations, very few aliens invaded | ||
| 125 | roadsides, probably due to harsh environmental conditions and still | 139 | roadsides, probably due to harsh environmental conditions and still | ||
| 126 | relatively low propagule pressure.", | 140 | relatively low propagule pressure.", | ||
| 127 | "es": "We studied road edge effects on floristic composition and | 141 | "es": "We studied road edge effects on floristic composition and | ||
| 128 | richness of alien and native plants on five zonal ecosystems, | 142 | richness of alien and native plants on five zonal ecosystems, | ||
| 129 | following a steep altitudinal gradient from arid coastal and | 143 | following a steep altitudinal gradient from arid coastal and | ||
| 130 | mid-elevation scrublands, through laurel and pine forests, to summit | 144 | mid-elevation scrublands, through laurel and pine forests, to summit | ||
| 131 | scrub, on Tenerife (Canary Islands). We analyzed vegetation within | 145 | scrub, on Tenerife (Canary Islands). We analyzed vegetation within | ||
| 132 | transects running from the road edge to the core of natural habitats. | 146 | transects running from the road edge to the core of natural habitats. | ||
| 133 | Alien richness significantly decreased with distance to road edge for | 147 | Alien richness significantly decreased with distance to road edge for | ||
| 134 | most ecosystems. Native richness also decreased with increasing road | 148 | most ecosystems. Native richness also decreased with increasing road | ||
| 135 | distance for the coastal scrub and pine forest, but increased for the | 149 | distance for the coastal scrub and pine forest, but increased for the | ||
| 136 | thermophilous scrub. We found a decrease in both native and alien | 150 | thermophilous scrub. We found a decrease in both native and alien | ||
| 137 | species richness with elevation. Our results suggest that road edge | 151 | species richness with elevation. Our results suggest that road edge | ||
| 138 | effects in alien plant invasion are stronger in native shrub | 152 | effects in alien plant invasion are stronger in native shrub | ||
| 139 | communities at low elevations than in forests (laurel and Canary | 153 | communities at low elevations than in forests (laurel and Canary | ||
| 140 | Island pine forest), where aliens were limited to a narrow road edge | 154 | Island pine forest), where aliens were limited to a narrow road edge | ||
| 141 | band. Detrended correspondence analyses showed that road edge plots | 155 | band. Detrended correspondence analyses showed that road edge plots | ||
| 142 | were floristically very different from interior plots and that each | 156 | were floristically very different from interior plots and that each | ||
| 143 | ecosystem harboured a specific alien assemblage with few species | 157 | ecosystem harboured a specific alien assemblage with few species | ||
| 144 | present in more than one ecosystem, suggesting a marked species | 158 | present in more than one ecosystem, suggesting a marked species | ||
| 145 | turnover of roadside alien species across altitudinal belts up to the | 159 | turnover of roadside alien species across altitudinal belts up to the | ||
| 146 | pine forest. However, at high elevations, very few aliens invaded | 160 | pine forest. However, at high elevations, very few aliens invaded | ||
| 147 | roadsides, probably due to harsh environmental conditions and still | 161 | roadsides, probably due to harsh environmental conditions and still | ||
| 148 | relatively low propagule pressure." | 162 | relatively low propagule pressure." | ||
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| 247 | 27.64]]]}", | 261 | 27.64]]]}", | ||
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| 256 | "uri": | 270 | "uri": | ||
| 257 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | 271 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | ||
| 258 | } | 272 | } | ||
| 259 | ], | 273 | ], | ||
| 260 | "spatial_resolution_in_meters": "", | 274 | "spatial_resolution_in_meters": "", | ||
| 261 | "spatial_uri": | 275 | "spatial_uri": | ||
| 262 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | 276 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | ||
| 263 | "state": "active", | 277 | "state": "active", | ||
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| 265 | "es": "" | 279 | "es": "" | ||
| 266 | }, | 280 | }, | ||
| 267 | "tag_uri": [ | 281 | "tag_uri": [ | ||
| 268 | 282 | ||||
| 269 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 283 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 270 | ], | 284 | ], | ||
| 271 | "tags": [ | 285 | "tags": [ | ||
| 272 | { | 286 | { | ||
| 273 | "display_name": "efectos-de-borde-y-margen-asociados-a-la", | 287 | "display_name": "efectos-de-borde-y-margen-asociados-a-la", | ||
| 274 | "id": "430b41a3-9e45-421d-92e3-00d12878405d", | 288 | "id": "430b41a3-9e45-421d-92e3-00d12878405d", | ||
| 275 | "name": "efectos-de-borde-y-margen-asociados-a-la", | 289 | "name": "efectos-de-borde-y-margen-asociados-a-la", | ||
| 276 | "state": "active", | 290 | "state": "active", | ||
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| 279 | { | 293 | { | ||
| 280 | "display_name": "fragmentacion", | 294 | "display_name": "fragmentacion", | ||
| 281 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | 295 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | ||
| 282 | "name": "fragmentacion", | 296 | "name": "fragmentacion", | ||
| 283 | "state": "active", | 297 | "state": "active", | ||
| 284 | "vocabulary_id": null | 298 | "vocabulary_id": null | ||
| 285 | } | 299 | } | ||
| 286 | ], | 300 | ], | ||
| 287 | "thematic_area": [ | 301 | "thematic_area": [ | ||
| 288 | "especies_silvestres" | 302 | "especies_silvestres" | ||
| 289 | ], | 303 | ], | ||
| 290 | "theme_es": [ | 304 | "theme_es": [ | ||
| 291 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 305 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 292 | ], | 306 | ], | ||
| 293 | "title": "Road edge effect and elevation patterns of native and | 307 | "title": "Road edge effect and elevation patterns of native and | ||
| 294 | alien plants on an oceanic island (Tenerife, Canary Islands).", | 308 | alien plants on an oceanic island (Tenerife, Canary Islands).", | ||
| 295 | "title_translated": { | 309 | "title_translated": { | ||
| 296 | "en": "", | 310 | "en": "", | ||
| 297 | "es": "Road edge effect and elevation patterns of native and alien | 311 | "es": "Road edge effect and elevation patterns of native and alien | ||
| 298 | plants on an oceanic island (Tenerife, Canary Islands)." | 312 | plants on an oceanic island (Tenerife, Canary Islands)." | ||
| 299 | }, | 313 | }, | ||
| 300 | "topic": | 314 | "topic": | ||
| 301 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 315 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 302 | "type": "dataset", | 316 | "type": "dataset", | ||
| 303 | "url": | 317 | "url": | ||
| 304 | //iepnb.es:443/catalogo/dataset/44c50bae-5b76-5a02-bef4-965d5a31815f", | 318 | //iepnb.es:443/catalogo/dataset/44c50bae-5b76-5a02-bef4-965d5a31815f", | ||
| 305 | "version": "", | 319 | "version": "", | ||
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| 307 | "en": "", | 321 | "en": "", | ||
| 308 | "es": "" | 322 | "es": "" | ||
| 309 | } | 323 | } | ||
| 310 | } | 324 | } |