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En el instante 25 de junio de 2026, 12:39:54 UTC,
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Modificado el valor del campo
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a2026-06-25
en Distributional patterns of endemic, native and alien species along a roadside elevation gradient in Tenerife, Canary Islands. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Distributional patterns of endemic, native and alien species along a roadside elevation gradient in Tenerife, Canary Islands.
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| 88 | "notes": "Invasion by alien plant species may be rapid and | 102 | "notes": "Invasion by alien plant species may be rapid and | ||
| 89 | aggressive, causing erosion of local biodiversity. This is | 103 | aggressive, causing erosion of local biodiversity. This is | ||
| 90 | particularly true for islands, where natural and anthropogenic | 104 | particularly true for islands, where natural and anthropogenic | ||
| 91 | corridors promote the rapid spread of invasive plants. Although | 105 | corridors promote the rapid spread of invasive plants. Although | ||
| 92 | evidence shows that corridors may facilitate plant invasions, the | 106 | evidence shows that corridors may facilitate plant invasions, the | ||
| 93 | question of how their importance in the spread of alien species varies | 107 | question of how their importance in the spread of alien species varies | ||
| 94 | along environmental gradients deserves more attention. Here, we | 108 | along environmental gradients deserves more attention. Here, we | ||
| 95 | addressed this issue by examining diversity patterns (species richness | 109 | addressed this issue by examining diversity patterns (species richness | ||
| 96 | of endemic, native and alien species) along and across roads, along an | 110 | of endemic, native and alien species) along and across roads, along an | ||
| 97 | elevation gradient from sea-level up to 2050 m a.s.l. in Tenerife | 111 | elevation gradient from sea-level up to 2050 m a.s.l. in Tenerife | ||
| 98 | (Canary Islands, Spain), at multiple spatial scales. Species richness | 112 | (Canary Islands, Spain), at multiple spatial scales. Species richness | ||
| 99 | was assessed using a multi-scale sampling design consisting of 59 | 113 | was assessed using a multi-scale sampling design consisting of 59 | ||
| 100 | T-transects of 150 m \u00d7 2 m, along three major roads each placed | 114 | T-transects of 150 m \u00d7 2 m, along three major roads each placed | ||
| 101 | over the whole elevation gradient. Each transect was composed of three | 115 | over the whole elevation gradient. Each transect was composed of three | ||
| 102 | sections of five plots each: Section 1 was located on the road edges, | 116 | sections of five plots each: Section 1 was located on the road edges, | ||
| 103 | Section 2 at intermediate distance, and Section 3 far from the road | 117 | Section 2 at intermediate distance, and Section 3 far from the road | ||
| 104 | edge, the latter representing the \u201cnative community\u201d less | 118 | edge, the latter representing the \u201cnative community\u201d less | ||
| 105 | affected by road-specific disturbance. The effect of elevation and | 119 | affected by road-specific disturbance. The effect of elevation and | ||
| 106 | distance from roadsides was evaluated for the three groups of species | 120 | distance from roadsides was evaluated for the three groups of species | ||
| 107 | (endemic, native and alien species), using parametric and | 121 | (endemic, native and alien species), using parametric and | ||
| 108 | non-parametric regression analyses as well as additive diversity | 122 | non-parametric regression analyses as well as additive diversity | ||
| 109 | partitioning. Differences among roads explained the majority of the | 123 | partitioning. Differences among roads explained the majority of the | ||
| 110 | variation in alien species richness and composition. Patterns in alien | 124 | variation in alien species richness and composition. Patterns in alien | ||
| 111 | species richness were also affected by elevation, with a decline in | 125 | species richness were also affected by elevation, with a decline in | ||
| 112 | richness with increasing elevation and no alien species recorded at | 126 | richness with increasing elevation and no alien species recorded at | ||
| 113 | high elevations. Elevation was the most important factor determining | 127 | high elevations. Elevation was the most important factor determining | ||
| 114 | patterns in endemic and native species. These findings confirm that | 128 | patterns in endemic and native species. These findings confirm that | ||
| 115 | climate filtering reflected in varying patterns along elevational | 129 | climate filtering reflected in varying patterns along elevational | ||
| 116 | gradients is an important determinant of the richness of alien species | 130 | gradients is an important determinant of the richness of alien species | ||
| 117 | (which are not adapted to high elevations), while anthropogenic | 131 | (which are not adapted to high elevations), while anthropogenic | ||
| 118 | pressures may explain the richness of alien species at low | 132 | pressures may explain the richness of alien species at low | ||
| 119 | elevation.", | 133 | elevation.", | ||
| 120 | "notes_translated": { | 134 | "notes_translated": { | ||
| 121 | "en": "Invasion by alien plant species may be rapid and | 135 | "en": "Invasion by alien plant species may be rapid and | ||
| 122 | aggressive, causing erosion of local biodiversity. This is | 136 | aggressive, causing erosion of local biodiversity. This is | ||
| 123 | particularly true for islands, where natural and anthropogenic | 137 | particularly true for islands, where natural and anthropogenic | ||
| 124 | corridors promote the rapid spread of invasive plants. Although | 138 | corridors promote the rapid spread of invasive plants. Although | ||
| 125 | evidence shows that corridors may facilitate plant invasions, the | 139 | evidence shows that corridors may facilitate plant invasions, the | ||
| 126 | question of how their importance in the spread of alien species varies | 140 | question of how their importance in the spread of alien species varies | ||
| 127 | along environmental gradients deserves more attention. Here, we | 141 | along environmental gradients deserves more attention. Here, we | ||
| 128 | addressed this issue by examining diversity patterns (species richness | 142 | addressed this issue by examining diversity patterns (species richness | ||
| 129 | of endemic, native and alien species) along and across roads, along an | 143 | of endemic, native and alien species) along and across roads, along an | ||
| 130 | elevation gradient from sea-level up to 2050 m a.s.l. in Tenerife | 144 | elevation gradient from sea-level up to 2050 m a.s.l. in Tenerife | ||
| 131 | (Canary Islands, Spain), at multiple spatial scales. Species richness | 145 | (Canary Islands, Spain), at multiple spatial scales. Species richness | ||
| 132 | was assessed using a multi-scale sampling design consisting of 59 | 146 | was assessed using a multi-scale sampling design consisting of 59 | ||
| 133 | T-transects of 150 m \u00d7 2 m, along three major roads each placed | 147 | T-transects of 150 m \u00d7 2 m, along three major roads each placed | ||
| 134 | over the whole elevation gradient. Each transect was composed of three | 148 | over the whole elevation gradient. Each transect was composed of three | ||
| 135 | sections of five plots each: Section 1 was located on the road edges, | 149 | sections of five plots each: Section 1 was located on the road edges, | ||
| 136 | Section 2 at intermediate distance, and Section 3 far from the road | 150 | Section 2 at intermediate distance, and Section 3 far from the road | ||
| 137 | edge, the latter representing the \u201cnative community\u201d less | 151 | edge, the latter representing the \u201cnative community\u201d less | ||
| 138 | affected by road-specific disturbance. The effect of elevation and | 152 | affected by road-specific disturbance. The effect of elevation and | ||
| 139 | distance from roadsides was evaluated for the three groups of species | 153 | distance from roadsides was evaluated for the three groups of species | ||
| 140 | (endemic, native and alien species), using parametric and | 154 | (endemic, native and alien species), using parametric and | ||
| 141 | non-parametric regression analyses as well as additive diversity | 155 | non-parametric regression analyses as well as additive diversity | ||
| 142 | partitioning. Differences among roads explained the majority of the | 156 | partitioning. Differences among roads explained the majority of the | ||
| 143 | variation in alien species richness and composition. Patterns in alien | 157 | variation in alien species richness and composition. Patterns in alien | ||
| 144 | species richness were also affected by elevation, with a decline in | 158 | species richness were also affected by elevation, with a decline in | ||
| 145 | richness with increasing elevation and no alien species recorded at | 159 | richness with increasing elevation and no alien species recorded at | ||
| 146 | high elevations. Elevation was the most important factor determining | 160 | high elevations. Elevation was the most important factor determining | ||
| 147 | patterns in endemic and native species. These findings confirm that | 161 | patterns in endemic and native species. These findings confirm that | ||
| 148 | climate filtering reflected in varying patterns along elevational | 162 | climate filtering reflected in varying patterns along elevational | ||
| 149 | gradients is an important determinant of the richness of alien species | 163 | gradients is an important determinant of the richness of alien species | ||
| 150 | (which are not adapted to high elevations), while anthropogenic | 164 | (which are not adapted to high elevations), while anthropogenic | ||
| 151 | pressures may explain the richness of alien species at low | 165 | pressures may explain the richness of alien species at low | ||
| 152 | elevation.", | 166 | elevation.", | ||
| 153 | "es": "Invasion by alien plant species may be rapid and | 167 | "es": "Invasion by alien plant species may be rapid and | ||
| 154 | aggressive, causing erosion of local biodiversity. This is | 168 | aggressive, causing erosion of local biodiversity. This is | ||
| 155 | particularly true for islands, where natural and anthropogenic | 169 | particularly true for islands, where natural and anthropogenic | ||
| 156 | corridors promote the rapid spread of invasive plants. Although | 170 | corridors promote the rapid spread of invasive plants. Although | ||
| 157 | evidence shows that corridors may facilitate plant invasions, the | 171 | evidence shows that corridors may facilitate plant invasions, the | ||
| 158 | question of how their importance in the spread of alien species varies | 172 | question of how their importance in the spread of alien species varies | ||
| 159 | along environmental gradients deserves more attention. Here, we | 173 | along environmental gradients deserves more attention. Here, we | ||
| 160 | addressed this issue by examining diversity patterns (species richness | 174 | addressed this issue by examining diversity patterns (species richness | ||
| 161 | of endemic, native and alien species) along and across roads, along an | 175 | of endemic, native and alien species) along and across roads, along an | ||
| 162 | elevation gradient from sea-level up to 2050 m a.s.l. in Tenerife | 176 | elevation gradient from sea-level up to 2050 m a.s.l. in Tenerife | ||
| 163 | (Canary Islands, Spain), at multiple spatial scales. Species richness | 177 | (Canary Islands, Spain), at multiple spatial scales. Species richness | ||
| 164 | was assessed using a multi-scale sampling design consisting of 59 | 178 | was assessed using a multi-scale sampling design consisting of 59 | ||
| 165 | T-transects of 150 m \u00d7 2 m, along three major roads each placed | 179 | T-transects of 150 m \u00d7 2 m, along three major roads each placed | ||
| 166 | over the whole elevation gradient. Each transect was composed of three | 180 | over the whole elevation gradient. Each transect was composed of three | ||
| 167 | sections of five plots each: Section 1 was located on the road edges, | 181 | sections of five plots each: Section 1 was located on the road edges, | ||
| 168 | Section 2 at intermediate distance, and Section 3 far from the road | 182 | Section 2 at intermediate distance, and Section 3 far from the road | ||
| 169 | edge, the latter representing the \u201cnative community\u201d less | 183 | edge, the latter representing the \u201cnative community\u201d less | ||
| 170 | affected by road-specific disturbance. The effect of elevation and | 184 | affected by road-specific disturbance. The effect of elevation and | ||
| 171 | distance from roadsides was evaluated for the three groups of species | 185 | distance from roadsides was evaluated for the three groups of species | ||
| 172 | (endemic, native and alien species), using parametric and | 186 | (endemic, native and alien species), using parametric and | ||
| 173 | non-parametric regression analyses as well as additive diversity | 187 | non-parametric regression analyses as well as additive diversity | ||
| 174 | partitioning. Differences among roads explained the majority of the | 188 | partitioning. Differences among roads explained the majority of the | ||
| 175 | variation in alien species richness and composition. Patterns in alien | 189 | variation in alien species richness and composition. Patterns in alien | ||
| 176 | species richness were also affected by elevation, with a decline in | 190 | species richness were also affected by elevation, with a decline in | ||
| 177 | richness with increasing elevation and no alien species recorded at | 191 | richness with increasing elevation and no alien species recorded at | ||
| 178 | high elevations. Elevation was the most important factor determining | 192 | high elevations. Elevation was the most important factor determining | ||
| 179 | patterns in endemic and native species. These findings confirm that | 193 | patterns in endemic and native species. These findings confirm that | ||
| 180 | climate filtering reflected in varying patterns along elevational | 194 | climate filtering reflected in varying patterns along elevational | ||
| 181 | gradients is an important determinant of the richness of alien species | 195 | gradients is an important determinant of the richness of alien species | ||
| 182 | (which are not adapted to high elevations), while anthropogenic | 196 | (which are not adapted to high elevations), while anthropogenic | ||
| 183 | pressures may explain the richness of alien species at low elevation." | 197 | pressures may explain the richness of alien species at low elevation." | ||
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