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En el instante 23 de junio de 2026, 16:14:13 UTC,
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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 How do alien plants distribute along roads on oceanic islands? A case study in Tenerife, Canary Islands.
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| 82 | "notes": "Islands are paradigms of the pervasive spread of alien | 82 | "notes": "Islands are paradigms of the pervasive spread of alien | ||
| 83 | plants, but little work has been done assessing pattern and cause of | 83 | plants, but little work has been done assessing pattern and cause of | ||
| 84 | the distribution of such plants in relation to roads on oceanic | 84 | the distribution of such plants in relation to roads on oceanic | ||
| 85 | islands. We studied richness, composition, and distribution of alien | 85 | islands. We studied richness, composition, and distribution of alien | ||
| 86 | plants and compared them with native species along roads on Tenerife | 86 | plants and compared them with native species along roads on Tenerife | ||
| 87 | (Canary Islands). We studied a single road transect that sampled two | 87 | (Canary Islands). We studied a single road transect that sampled two | ||
| 88 | contrasting wind-facing aspects (leeward versus windward) and ran from | 88 | contrasting wind-facing aspects (leeward versus windward) and ran from | ||
| 89 | coastal Euphorbia scrubland through thermophilous scrubland to | 89 | coastal Euphorbia scrubland through thermophilous scrubland to | ||
| 90 | Makaronesian laurel forest at the top of a mountainous massif. We | 90 | Makaronesian laurel forest at the top of a mountainous massif. We | ||
| 91 | evaluated the effects of elevation, aspect, distance to urban nuclei, | 91 | evaluated the effects of elevation, aspect, distance to urban nuclei, | ||
| 92 | and several road-edge features (including road-edge width and | 92 | and several road-edge features (including road-edge width and | ||
| 93 | management\u2014implying disturbance intensity), using regression | 93 | management\u2014implying disturbance intensity), using regression | ||
| 94 | models, analysis of variance, and multivariate ordination methods. | 94 | models, analysis of variance, and multivariate ordination methods. | ||
| 95 | Richness of both endemics and native nonendemics was explained by | 95 | Richness of both endemics and native nonendemics was explained by | ||
| 96 | elevation (related to well-defined vegetation belts), steepness of the | 96 | elevation (related to well-defined vegetation belts), steepness of the | ||
| 97 | edge slope, and cover of rocky ground. Despite a short elevational | 97 | edge slope, and cover of rocky ground. Despite a short elevational | ||
| 98 | gradient (0\u2013650m), we found clear altitudinal zonation by | 98 | gradient (0\u2013650m), we found clear altitudinal zonation by | ||
| 99 | biogeographic origin of both nonendemic natives and aliens, and | 99 | biogeographic origin of both nonendemic natives and aliens, and | ||
| 100 | altitudinal distribution of aliens followed the same zonation as that | 100 | altitudinal distribution of aliens followed the same zonation as that | ||
| 101 | of natives. Alien species\u2019 richness was related to management | 101 | of natives. Alien species\u2019 richness was related to management | ||
| 102 | intensity determining edge disturbance, road-edge width, and distance | 102 | intensity determining edge disturbance, road-edge width, and distance | ||
| 103 | to the nearest urban nuclei (propagule sources). Different variables | 103 | to the nearest urban nuclei (propagule sources). Different variables | ||
| 104 | explained distribution patterns of natives, endemics, and aliens along | 104 | explained distribution patterns of natives, endemics, and aliens along | ||
| 105 | roadsides on leeward and windward aspects. Altitude and aspect also | 105 | roadsides on leeward and windward aspects. Altitude and aspect also | ||
| 106 | had a strong influence on the frequency of life strategies (woody | 106 | had a strong influence on the frequency of life strategies (woody | ||
| 107 | species, annuals and biennial/perennial herbs) of roadside plant | 107 | species, annuals and biennial/perennial herbs) of roadside plant | ||
| 108 | communities. Due to harsher environmental filters operating on the | 108 | communities. Due to harsher environmental filters operating on the | ||
| 109 | leeward aspect, alien species were distributed along the altitudinal | 109 | leeward aspect, alien species were distributed along the altitudinal | ||
| 110 | gradient in apparent consistency with general biogeographical | 110 | gradient in apparent consistency with general biogeographical | ||
| 111 | affinities. Tropical/subtropical taxa showed exponential decrease with | 111 | affinities. Tropical/subtropical taxa showed exponential decrease with | ||
| 112 | increasing elevation, Mediterranean taxa showed a unimodal response | 112 | increasing elevation, Mediterranean taxa showed a unimodal response | ||
| 113 | (i.e., maximum richness at mid elevation, minimum at the extremes of | 113 | (i.e., maximum richness at mid elevation, minimum at the extremes of | ||
| 114 | the gradient), and temperate taxa showed linear increase with | 114 | the gradient), and temperate taxa showed linear increase with | ||
| 115 | elevation. Native but nonendemic species followed analogous trends to | 115 | elevation. Native but nonendemic species followed analogous trends to | ||
| 116 | those of aliens. This suggests climatic matching as a prerequisite for | 116 | those of aliens. This suggests climatic matching as a prerequisite for | ||
| 117 | successful invasion of this topographically complex island. Other road | 117 | successful invasion of this topographically complex island. Other road | ||
| 118 | traits, such as edge width, slope steepness, soil cover, and road-edge | 118 | traits, such as edge width, slope steepness, soil cover, and road-edge | ||
| 119 | disturbance intensity may play a complementary role, at a more local | 119 | disturbance intensity may play a complementary role, at a more local | ||
| 120 | scale, to shape the distribution of alien plants on these island | 120 | scale, to shape the distribution of alien plants on these island | ||
| 121 | roads.", | 121 | roads.", | ||
| 122 | "notes_translated": { | 122 | "notes_translated": { | ||
| 123 | "en": "Islands are paradigms of the pervasive spread of alien | 123 | "en": "Islands are paradigms of the pervasive spread of alien | ||
| 124 | plants, but little work has been done assessing pattern and cause of | 124 | plants, but little work has been done assessing pattern and cause of | ||
| 125 | the distribution of such plants in relation to roads on oceanic | 125 | the distribution of such plants in relation to roads on oceanic | ||
| 126 | islands. We studied richness, composition, and distribution of alien | 126 | islands. We studied richness, composition, and distribution of alien | ||
| 127 | plants and compared them with native species along roads on Tenerife | 127 | plants and compared them with native species along roads on Tenerife | ||
| 128 | (Canary Islands). We studied a single road transect that sampled two | 128 | (Canary Islands). We studied a single road transect that sampled two | ||
| 129 | contrasting wind-facing aspects (leeward versus windward) and ran from | 129 | contrasting wind-facing aspects (leeward versus windward) and ran from | ||
| 130 | coastal Euphorbia scrubland through thermophilous scrubland to | 130 | coastal Euphorbia scrubland through thermophilous scrubland to | ||
| 131 | Makaronesian laurel forest at the top of a mountainous massif. We | 131 | Makaronesian laurel forest at the top of a mountainous massif. We | ||
| 132 | evaluated the effects of elevation, aspect, distance to urban nuclei, | 132 | evaluated the effects of elevation, aspect, distance to urban nuclei, | ||
| 133 | and several road-edge features (including road-edge width and | 133 | and several road-edge features (including road-edge width and | ||
| 134 | management\u2014implying disturbance intensity), using regression | 134 | management\u2014implying disturbance intensity), using regression | ||
| 135 | models, analysis of variance, and multivariate ordination methods. | 135 | models, analysis of variance, and multivariate ordination methods. | ||
| 136 | Richness of both endemics and native nonendemics was explained by | 136 | Richness of both endemics and native nonendemics was explained by | ||
| 137 | elevation (related to well-defined vegetation belts), steepness of the | 137 | elevation (related to well-defined vegetation belts), steepness of the | ||
| 138 | edge slope, and cover of rocky ground. Despite a short elevational | 138 | edge slope, and cover of rocky ground. Despite a short elevational | ||
| 139 | gradient (0\u2013650m), we found clear altitudinal zonation by | 139 | gradient (0\u2013650m), we found clear altitudinal zonation by | ||
| 140 | biogeographic origin of both nonendemic natives and aliens, and | 140 | biogeographic origin of both nonendemic natives and aliens, and | ||
| 141 | altitudinal distribution of aliens followed the same zonation as that | 141 | altitudinal distribution of aliens followed the same zonation as that | ||
| 142 | of natives. Alien species\u2019 richness was related to management | 142 | of natives. Alien species\u2019 richness was related to management | ||
| 143 | intensity determining edge disturbance, road-edge width, and distance | 143 | intensity determining edge disturbance, road-edge width, and distance | ||
| 144 | to the nearest urban nuclei (propagule sources). Different variables | 144 | to the nearest urban nuclei (propagule sources). Different variables | ||
| 145 | explained distribution patterns of natives, endemics, and aliens along | 145 | explained distribution patterns of natives, endemics, and aliens along | ||
| 146 | roadsides on leeward and windward aspects. Altitude and aspect also | 146 | roadsides on leeward and windward aspects. Altitude and aspect also | ||
| 147 | had a strong influence on the frequency of life strategies (woody | 147 | had a strong influence on the frequency of life strategies (woody | ||
| 148 | species, annuals and biennial/perennial herbs) of roadside plant | 148 | species, annuals and biennial/perennial herbs) of roadside plant | ||
| 149 | communities. Due to harsher environmental filters operating on the | 149 | communities. Due to harsher environmental filters operating on the | ||
| 150 | leeward aspect, alien species were distributed along the altitudinal | 150 | leeward aspect, alien species were distributed along the altitudinal | ||
| 151 | gradient in apparent consistency with general biogeographical | 151 | gradient in apparent consistency with general biogeographical | ||
| 152 | affinities. Tropical/subtropical taxa showed exponential decrease with | 152 | affinities. Tropical/subtropical taxa showed exponential decrease with | ||
| 153 | increasing elevation, Mediterranean taxa showed a unimodal response | 153 | increasing elevation, Mediterranean taxa showed a unimodal response | ||
| 154 | (i.e., maximum richness at mid elevation, minimum at the extremes of | 154 | (i.e., maximum richness at mid elevation, minimum at the extremes of | ||
| 155 | the gradient), and temperate taxa showed linear increase with | 155 | the gradient), and temperate taxa showed linear increase with | ||
| 156 | elevation. Native but nonendemic species followed analogous trends to | 156 | elevation. Native but nonendemic species followed analogous trends to | ||
| 157 | those of aliens. This suggests climatic matching as a prerequisite for | 157 | those of aliens. This suggests climatic matching as a prerequisite for | ||
| 158 | successful invasion of this topographically complex island. Other road | 158 | successful invasion of this topographically complex island. Other road | ||
| 159 | traits, such as edge width, slope steepness, soil cover, and road-edge | 159 | traits, such as edge width, slope steepness, soil cover, and road-edge | ||
| 160 | disturbance intensity may play a complementary role, at a more local | 160 | disturbance intensity may play a complementary role, at a more local | ||
| 161 | scale, to shape the distribution of alien plants on these island | 161 | scale, to shape the distribution of alien plants on these island | ||
| 162 | roads.", | 162 | roads.", | ||
| 163 | "es": "Islands are paradigms of the pervasive spread of alien | 163 | "es": "Islands are paradigms of the pervasive spread of alien | ||
| 164 | plants, but little work has been done assessing pattern and cause of | 164 | plants, but little work has been done assessing pattern and cause of | ||
| 165 | the distribution of such plants in relation to roads on oceanic | 165 | the distribution of such plants in relation to roads on oceanic | ||
| 166 | islands. We studied richness, composition, and distribution of alien | 166 | islands. We studied richness, composition, and distribution of alien | ||
| 167 | plants and compared them with native species along roads on Tenerife | 167 | plants and compared them with native species along roads on Tenerife | ||
| 168 | (Canary Islands). We studied a single road transect that sampled two | 168 | (Canary Islands). We studied a single road transect that sampled two | ||
| 169 | contrasting wind-facing aspects (leeward versus windward) and ran from | 169 | contrasting wind-facing aspects (leeward versus windward) and ran from | ||
| 170 | coastal Euphorbia scrubland through thermophilous scrubland to | 170 | coastal Euphorbia scrubland through thermophilous scrubland to | ||
| 171 | Makaronesian laurel forest at the top of a mountainous massif. We | 171 | Makaronesian laurel forest at the top of a mountainous massif. We | ||
| 172 | evaluated the effects of elevation, aspect, distance to urban nuclei, | 172 | evaluated the effects of elevation, aspect, distance to urban nuclei, | ||
| 173 | and several road-edge features (including road-edge width and | 173 | and several road-edge features (including road-edge width and | ||
| 174 | management\u2014implying disturbance intensity), using regression | 174 | management\u2014implying disturbance intensity), using regression | ||
| 175 | models, analysis of variance, and multivariate ordination methods. | 175 | models, analysis of variance, and multivariate ordination methods. | ||
| 176 | Richness of both endemics and native nonendemics was explained by | 176 | Richness of both endemics and native nonendemics was explained by | ||
| 177 | elevation (related to well-defined vegetation belts), steepness of the | 177 | elevation (related to well-defined vegetation belts), steepness of the | ||
| 178 | edge slope, and cover of rocky ground. Despite a short elevational | 178 | edge slope, and cover of rocky ground. Despite a short elevational | ||
| 179 | gradient (0\u2013650m), we found clear altitudinal zonation by | 179 | gradient (0\u2013650m), we found clear altitudinal zonation by | ||
| 180 | biogeographic origin of both nonendemic natives and aliens, and | 180 | biogeographic origin of both nonendemic natives and aliens, and | ||
| 181 | altitudinal distribution of aliens followed the same zonation as that | 181 | altitudinal distribution of aliens followed the same zonation as that | ||
| 182 | of natives. Alien species\u2019 richness was related to management | 182 | of natives. Alien species\u2019 richness was related to management | ||
| 183 | intensity determining edge disturbance, road-edge width, and distance | 183 | intensity determining edge disturbance, road-edge width, and distance | ||
| 184 | to the nearest urban nuclei (propagule sources). Different variables | 184 | to the nearest urban nuclei (propagule sources). Different variables | ||
| 185 | explained distribution patterns of natives, endemics, and aliens along | 185 | explained distribution patterns of natives, endemics, and aliens along | ||
| 186 | roadsides on leeward and windward aspects. Altitude and aspect also | 186 | roadsides on leeward and windward aspects. Altitude and aspect also | ||
| 187 | had a strong influence on the frequency of life strategies (woody | 187 | had a strong influence on the frequency of life strategies (woody | ||
| 188 | species, annuals and biennial/perennial herbs) of roadside plant | 188 | species, annuals and biennial/perennial herbs) of roadside plant | ||
| 189 | communities. Due to harsher environmental filters operating on the | 189 | communities. Due to harsher environmental filters operating on the | ||
| 190 | leeward aspect, alien species were distributed along the altitudinal | 190 | leeward aspect, alien species were distributed along the altitudinal | ||
| 191 | gradient in apparent consistency with general biogeographical | 191 | gradient in apparent consistency with general biogeographical | ||
| 192 | affinities. Tropical/subtropical taxa showed exponential decrease with | 192 | affinities. Tropical/subtropical taxa showed exponential decrease with | ||
| 193 | increasing elevation, Mediterranean taxa showed a unimodal response | 193 | increasing elevation, Mediterranean taxa showed a unimodal response | ||
| 194 | (i.e., maximum richness at mid elevation, minimum at the extremes of | 194 | (i.e., maximum richness at mid elevation, minimum at the extremes of | ||
| 195 | the gradient), and temperate taxa showed linear increase with | 195 | the gradient), and temperate taxa showed linear increase with | ||
| 196 | elevation. Native but nonendemic species followed analogous trends to | 196 | elevation. Native but nonendemic species followed analogous trends to | ||
| 197 | those of aliens. This suggests climatic matching as a prerequisite for | 197 | those of aliens. This suggests climatic matching as a prerequisite for | ||
| 198 | successful invasion of this topographically complex island. Other road | 198 | successful invasion of this topographically complex island. Other road | ||
| 199 | traits, such as edge width, slope steepness, soil cover, and road-edge | 199 | traits, such as edge width, slope steepness, soil cover, and road-edge | ||
| 200 | disturbance intensity may play a complementary role, at a more local | 200 | disturbance intensity may play a complementary role, at a more local | ||
| 201 | scale, to shape the distribution of alien plants on these island | 201 | scale, to shape the distribution of alien plants on these island | ||
| 202 | roads." | 202 | roads." | ||
| 203 | }, | 203 | }, | ||
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