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En el instante 25 de junio de 2026, 12:30:06 UTC,
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Modificado el valor del campo
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a2026-06-25
en Mountain roads and non-native species modify elevational patterns of plant diversity. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Mountain roads and non-native species modify elevational patterns of plant diversity.
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| 88 | "notes": "We investigated patterns of species richness and community | 102 | "notes": "We investigated patterns of species richness and community | ||
| 89 | dissimilarity along elevation gradients using globally replicated, | 103 | dissimilarity along elevation gradients using globally replicated, | ||
| 90 | standardized surveys of vascular plants. We asked how these patterns | 104 | standardized surveys of vascular plants. We asked how these patterns | ||
| 91 | of diversity are influenced by anthropogenic pressures (road | 105 | of diversity are influenced by anthropogenic pressures (road | ||
| 92 | construction and non-native species). Global. 2008\u20132015. Vascular | 106 | construction and non-native species). Global. 2008\u20132015. Vascular | ||
| 93 | plants. Native and non-native vascular plant species were recorded in | 107 | plants. Native and non-native vascular plant species were recorded in | ||
| 94 | 943 plots along 25 elevation gradients, in nine mountain regions, on | 108 | 943 plots along 25 elevation gradients, in nine mountain regions, on | ||
| 95 | four continents. Sampling took place in plots along and away from | 109 | four continents. Sampling took place in plots along and away from | ||
| 96 | roads. We analysed the effects of elevation and distance from road on | 110 | roads. We analysed the effects of elevation and distance from road on | ||
| 97 | species richness patterns and community dissimilarity | 111 | species richness patterns and community dissimilarity | ||
| 98 | (beta-diversity), and assessed how non-native species modified such | 112 | (beta-diversity), and assessed how non-native species modified such | ||
| 99 | elevational diversity patterns. Globally, native and total species | 113 | elevational diversity patterns. Globally, native and total species | ||
| 100 | richness showed a unimodal relationship with elevation that peaked at | 114 | richness showed a unimodal relationship with elevation that peaked at | ||
| 101 | lower-mid elevations, but these patterns were altered along roads and | 115 | lower-mid elevations, but these patterns were altered along roads and | ||
| 102 | due to non-native species. Differences in elevational species richness | 116 | due to non-native species. Differences in elevational species richness | ||
| 103 | patterns between regions disappeared along roadsides, and non-native | 117 | patterns between regions disappeared along roadsides, and non-native | ||
| 104 | species changed the patterns\u2019 character in all study regions. | 118 | species changed the patterns\u2019 character in all study regions. | ||
| 105 | Community dissimilarity was reduced along roadsides and through | 119 | Community dissimilarity was reduced along roadsides and through | ||
| 106 | non-native species. We also found a significant elevational decay of | 120 | non-native species. We also found a significant elevational decay of | ||
| 107 | beta-diversity, which however was not affected by roads or non-native | 121 | beta-diversity, which however was not affected by roads or non-native | ||
| 108 | species. Idiosyncratic native species richness patterns in plots away | 122 | species. Idiosyncratic native species richness patterns in plots away | ||
| 109 | from roads implicate region-specific mechanisms underlying these | 123 | from roads implicate region-specific mechanisms underlying these | ||
| 110 | patterns. However, along roadsides a clearer elevational signal | 124 | patterns. However, along roadsides a clearer elevational signal | ||
| 111 | emerged and species richness mostly peaked at mid-elevations. We | 125 | emerged and species richness mostly peaked at mid-elevations. We | ||
| 112 | conclude that both roads and non-native species lead to a | 126 | conclude that both roads and non-native species lead to a | ||
| 113 | homogenization of species richness patterns and plant communities in | 127 | homogenization of species richness patterns and plant communities in | ||
| 114 | mountains.", | 128 | mountains.", | ||
| 115 | "notes_translated": { | 129 | "notes_translated": { | ||
| 116 | "en": "We investigated patterns of species richness and community | 130 | "en": "We investigated patterns of species richness and community | ||
| 117 | dissimilarity along elevation gradients using globally replicated, | 131 | dissimilarity along elevation gradients using globally replicated, | ||
| 118 | standardized surveys of vascular plants. We asked how these patterns | 132 | standardized surveys of vascular plants. We asked how these patterns | ||
| 119 | of diversity are influenced by anthropogenic pressures (road | 133 | of diversity are influenced by anthropogenic pressures (road | ||
| 120 | construction and non-native species). Global. 2008\u20132015. Vascular | 134 | construction and non-native species). Global. 2008\u20132015. Vascular | ||
| 121 | plants. Native and non-native vascular plant species were recorded in | 135 | plants. Native and non-native vascular plant species were recorded in | ||
| 122 | 943 plots along 25 elevation gradients, in nine mountain regions, on | 136 | 943 plots along 25 elevation gradients, in nine mountain regions, on | ||
| 123 | four continents. Sampling took place in plots along and away from | 137 | four continents. Sampling took place in plots along and away from | ||
| 124 | roads. We analysed the effects of elevation and distance from road on | 138 | roads. We analysed the effects of elevation and distance from road on | ||
| 125 | species richness patterns and community dissimilarity | 139 | species richness patterns and community dissimilarity | ||
| 126 | (beta-diversity), and assessed how non-native species modified such | 140 | (beta-diversity), and assessed how non-native species modified such | ||
| 127 | elevational diversity patterns. Globally, native and total species | 141 | elevational diversity patterns. Globally, native and total species | ||
| 128 | richness showed a unimodal relationship with elevation that peaked at | 142 | richness showed a unimodal relationship with elevation that peaked at | ||
| 129 | lower-mid elevations, but these patterns were altered along roads and | 143 | lower-mid elevations, but these patterns were altered along roads and | ||
| 130 | due to non-native species. Differences in elevational species richness | 144 | due to non-native species. Differences in elevational species richness | ||
| 131 | patterns between regions disappeared along roadsides, and non-native | 145 | patterns between regions disappeared along roadsides, and non-native | ||
| 132 | species changed the patterns\u2019 character in all study regions. | 146 | species changed the patterns\u2019 character in all study regions. | ||
| 133 | Community dissimilarity was reduced along roadsides and through | 147 | Community dissimilarity was reduced along roadsides and through | ||
| 134 | non-native species. We also found a significant elevational decay of | 148 | non-native species. We also found a significant elevational decay of | ||
| 135 | beta-diversity, which however was not affected by roads or non-native | 149 | beta-diversity, which however was not affected by roads or non-native | ||
| 136 | species. Idiosyncratic native species richness patterns in plots away | 150 | species. Idiosyncratic native species richness patterns in plots away | ||
| 137 | from roads implicate region-specific mechanisms underlying these | 151 | from roads implicate region-specific mechanisms underlying these | ||
| 138 | patterns. However, along roadsides a clearer elevational signal | 152 | patterns. However, along roadsides a clearer elevational signal | ||
| 139 | emerged and species richness mostly peaked at mid-elevations. We | 153 | emerged and species richness mostly peaked at mid-elevations. We | ||
| 140 | conclude that both roads and non-native species lead to a | 154 | conclude that both roads and non-native species lead to a | ||
| 141 | homogenization of species richness patterns and plant communities in | 155 | homogenization of species richness patterns and plant communities in | ||
| 142 | mountains.", | 156 | mountains.", | ||
| 143 | "es": "We investigated patterns of species richness and community | 157 | "es": "We investigated patterns of species richness and community | ||
| 144 | dissimilarity along elevation gradients using globally replicated, | 158 | dissimilarity along elevation gradients using globally replicated, | ||
| 145 | standardized surveys of vascular plants. We asked how these patterns | 159 | standardized surveys of vascular plants. We asked how these patterns | ||
| 146 | of diversity are influenced by anthropogenic pressures (road | 160 | of diversity are influenced by anthropogenic pressures (road | ||
| 147 | construction and non-native species). Global. 2008\u20132015. Vascular | 161 | construction and non-native species). Global. 2008\u20132015. Vascular | ||
| 148 | plants. Native and non-native vascular plant species were recorded in | 162 | plants. Native and non-native vascular plant species were recorded in | ||
| 149 | 943 plots along 25 elevation gradients, in nine mountain regions, on | 163 | 943 plots along 25 elevation gradients, in nine mountain regions, on | ||
| 150 | four continents. Sampling took place in plots along and away from | 164 | four continents. Sampling took place in plots along and away from | ||
| 151 | roads. We analysed the effects of elevation and distance from road on | 165 | roads. We analysed the effects of elevation and distance from road on | ||
| 152 | species richness patterns and community dissimilarity | 166 | species richness patterns and community dissimilarity | ||
| 153 | (beta-diversity), and assessed how non-native species modified such | 167 | (beta-diversity), and assessed how non-native species modified such | ||
| 154 | elevational diversity patterns. Globally, native and total species | 168 | elevational diversity patterns. Globally, native and total species | ||
| 155 | richness showed a unimodal relationship with elevation that peaked at | 169 | richness showed a unimodal relationship with elevation that peaked at | ||
| 156 | lower-mid elevations, but these patterns were altered along roads and | 170 | lower-mid elevations, but these patterns were altered along roads and | ||
| 157 | due to non-native species. Differences in elevational species richness | 171 | due to non-native species. Differences in elevational species richness | ||
| 158 | patterns between regions disappeared along roadsides, and non-native | 172 | patterns between regions disappeared along roadsides, and non-native | ||
| 159 | species changed the patterns\u2019 character in all study regions. | 173 | species changed the patterns\u2019 character in all study regions. | ||
| 160 | Community dissimilarity was reduced along roadsides and through | 174 | Community dissimilarity was reduced along roadsides and through | ||
| 161 | non-native species. We also found a significant elevational decay of | 175 | non-native species. We also found a significant elevational decay of | ||
| 162 | beta-diversity, which however was not affected by roads or non-native | 176 | beta-diversity, which however was not affected by roads or non-native | ||
| 163 | species. Idiosyncratic native species richness patterns in plots away | 177 | species. Idiosyncratic native species richness patterns in plots away | ||
| 164 | from roads implicate region-specific mechanisms underlying these | 178 | from roads implicate region-specific mechanisms underlying these | ||
| 165 | patterns. However, along roadsides a clearer elevational signal | 179 | patterns. However, along roadsides a clearer elevational signal | ||
| 166 | emerged and species richness mostly peaked at mid-elevations. We | 180 | emerged and species richness mostly peaked at mid-elevations. We | ||
| 167 | conclude that both roads and non-native species lead to a | 181 | conclude that both roads and non-native species lead to a | ||
| 168 | homogenization of species richness patterns and plant communities in | 182 | homogenization of species richness patterns and plant communities in | ||
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