Cambios
En el instante 23 de junio de 2026, 16:00:22 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 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 | 88 | "notes": "We investigated patterns of species richness and community | ||
| 89 | dissimilarity along elevation gradients using globally replicated, | 89 | dissimilarity along elevation gradients using globally replicated, | ||
| 90 | standardized surveys of vascular plants. We asked how these patterns | 90 | standardized surveys of vascular plants. We asked how these patterns | ||
| 91 | of diversity are influenced by anthropogenic pressures (road | 91 | of diversity are influenced by anthropogenic pressures (road | ||
| 92 | construction and non-native species). Global. 2008\u20132015. Vascular | 92 | construction and non-native species). Global. 2008\u20132015. Vascular | ||
| 93 | plants. Native and non-native vascular plant species were recorded in | 93 | plants. Native and non-native vascular plant species were recorded in | ||
| 94 | 943 plots along 25 elevation gradients, in nine mountain regions, on | 94 | 943 plots along 25 elevation gradients, in nine mountain regions, on | ||
| 95 | four continents. Sampling took place in plots along and away from | 95 | four continents. Sampling took place in plots along and away from | ||
| 96 | roads. We analysed the effects of elevation and distance from road on | 96 | roads. We analysed the effects of elevation and distance from road on | ||
| 97 | species richness patterns and community dissimilarity | 97 | species richness patterns and community dissimilarity | ||
| 98 | (beta-diversity), and assessed how non-native species modified such | 98 | (beta-diversity), and assessed how non-native species modified such | ||
| 99 | elevational diversity patterns. Globally, native and total species | 99 | elevational diversity patterns. Globally, native and total species | ||
| 100 | richness showed a unimodal relationship with elevation that peaked at | 100 | richness showed a unimodal relationship with elevation that peaked at | ||
| 101 | lower-mid elevations, but these patterns were altered along roads and | 101 | lower-mid elevations, but these patterns were altered along roads and | ||
| 102 | due to non-native species. Differences in elevational species richness | 102 | due to non-native species. Differences in elevational species richness | ||
| 103 | patterns between regions disappeared along roadsides, and non-native | 103 | patterns between regions disappeared along roadsides, and non-native | ||
| 104 | species changed the patterns\u2019 character in all study regions. | 104 | species changed the patterns\u2019 character in all study regions. | ||
| 105 | Community dissimilarity was reduced along roadsides and through | 105 | Community dissimilarity was reduced along roadsides and through | ||
| 106 | non-native species. We also found a significant elevational decay of | 106 | non-native species. We also found a significant elevational decay of | ||
| 107 | beta-diversity, which however was not affected by roads or non-native | 107 | beta-diversity, which however was not affected by roads or non-native | ||
| 108 | species. Idiosyncratic native species richness patterns in plots away | 108 | species. Idiosyncratic native species richness patterns in plots away | ||
| 109 | from roads implicate region-specific mechanisms underlying these | 109 | from roads implicate region-specific mechanisms underlying these | ||
| 110 | patterns. However, along roadsides a clearer elevational signal | 110 | patterns. However, along roadsides a clearer elevational signal | ||
| 111 | emerged and species richness mostly peaked at mid-elevations. We | 111 | emerged and species richness mostly peaked at mid-elevations. We | ||
| 112 | conclude that both roads and non-native species lead to a | 112 | conclude that both roads and non-native species lead to a | ||
| 113 | homogenization of species richness patterns and plant communities in | 113 | homogenization of species richness patterns and plant communities in | ||
| 114 | mountains.", | 114 | mountains.", | ||
| 115 | "notes_translated": { | 115 | "notes_translated": { | ||
| 116 | "en": "We investigated patterns of species richness and community | 116 | "en": "We investigated patterns of species richness and community | ||
| 117 | dissimilarity along elevation gradients using globally replicated, | 117 | dissimilarity along elevation gradients using globally replicated, | ||
| 118 | standardized surveys of vascular plants. We asked how these patterns | 118 | standardized surveys of vascular plants. We asked how these patterns | ||
| 119 | of diversity are influenced by anthropogenic pressures (road | 119 | of diversity are influenced by anthropogenic pressures (road | ||
| 120 | construction and non-native species). Global. 2008\u20132015. Vascular | 120 | construction and non-native species). Global. 2008\u20132015. Vascular | ||
| 121 | plants. Native and non-native vascular plant species were recorded in | 121 | plants. Native and non-native vascular plant species were recorded in | ||
| 122 | 943 plots along 25 elevation gradients, in nine mountain regions, on | 122 | 943 plots along 25 elevation gradients, in nine mountain regions, on | ||
| 123 | four continents. Sampling took place in plots along and away from | 123 | four continents. Sampling took place in plots along and away from | ||
| 124 | roads. We analysed the effects of elevation and distance from road on | 124 | roads. We analysed the effects of elevation and distance from road on | ||
| 125 | species richness patterns and community dissimilarity | 125 | species richness patterns and community dissimilarity | ||
| 126 | (beta-diversity), and assessed how non-native species modified such | 126 | (beta-diversity), and assessed how non-native species modified such | ||
| 127 | elevational diversity patterns. Globally, native and total species | 127 | elevational diversity patterns. Globally, native and total species | ||
| 128 | richness showed a unimodal relationship with elevation that peaked at | 128 | richness showed a unimodal relationship with elevation that peaked at | ||
| 129 | lower-mid elevations, but these patterns were altered along roads and | 129 | lower-mid elevations, but these patterns were altered along roads and | ||
| 130 | due to non-native species. Differences in elevational species richness | 130 | due to non-native species. Differences in elevational species richness | ||
| 131 | patterns between regions disappeared along roadsides, and non-native | 131 | patterns between regions disappeared along roadsides, and non-native | ||
| 132 | species changed the patterns\u2019 character in all study regions. | 132 | species changed the patterns\u2019 character in all study regions. | ||
| 133 | Community dissimilarity was reduced along roadsides and through | 133 | Community dissimilarity was reduced along roadsides and through | ||
| 134 | non-native species. We also found a significant elevational decay of | 134 | non-native species. We also found a significant elevational decay of | ||
| 135 | beta-diversity, which however was not affected by roads or non-native | 135 | beta-diversity, which however was not affected by roads or non-native | ||
| 136 | species. Idiosyncratic native species richness patterns in plots away | 136 | species. Idiosyncratic native species richness patterns in plots away | ||
| 137 | from roads implicate region-specific mechanisms underlying these | 137 | from roads implicate region-specific mechanisms underlying these | ||
| 138 | patterns. However, along roadsides a clearer elevational signal | 138 | patterns. However, along roadsides a clearer elevational signal | ||
| 139 | emerged and species richness mostly peaked at mid-elevations. We | 139 | emerged and species richness mostly peaked at mid-elevations. We | ||
| 140 | conclude that both roads and non-native species lead to a | 140 | conclude that both roads and non-native species lead to a | ||
| 141 | homogenization of species richness patterns and plant communities in | 141 | homogenization of species richness patterns and plant communities in | ||
| 142 | mountains.", | 142 | mountains.", | ||
| 143 | "es": "We investigated patterns of species richness and community | 143 | "es": "We investigated patterns of species richness and community | ||
| 144 | dissimilarity along elevation gradients using globally replicated, | 144 | dissimilarity along elevation gradients using globally replicated, | ||
| 145 | standardized surveys of vascular plants. We asked how these patterns | 145 | standardized surveys of vascular plants. We asked how these patterns | ||
| 146 | of diversity are influenced by anthropogenic pressures (road | 146 | of diversity are influenced by anthropogenic pressures (road | ||
| 147 | construction and non-native species). Global. 2008\u20132015. Vascular | 147 | construction and non-native species). Global. 2008\u20132015. Vascular | ||
| 148 | plants. Native and non-native vascular plant species were recorded in | 148 | plants. Native and non-native vascular plant species were recorded in | ||
| 149 | 943 plots along 25 elevation gradients, in nine mountain regions, on | 149 | 943 plots along 25 elevation gradients, in nine mountain regions, on | ||
| 150 | four continents. Sampling took place in plots along and away from | 150 | four continents. Sampling took place in plots along and away from | ||
| 151 | roads. We analysed the effects of elevation and distance from road on | 151 | roads. We analysed the effects of elevation and distance from road on | ||
| 152 | species richness patterns and community dissimilarity | 152 | species richness patterns and community dissimilarity | ||
| 153 | (beta-diversity), and assessed how non-native species modified such | 153 | (beta-diversity), and assessed how non-native species modified such | ||
| 154 | elevational diversity patterns. Globally, native and total species | 154 | elevational diversity patterns. Globally, native and total species | ||
| 155 | richness showed a unimodal relationship with elevation that peaked at | 155 | richness showed a unimodal relationship with elevation that peaked at | ||
| 156 | lower-mid elevations, but these patterns were altered along roads and | 156 | lower-mid elevations, but these patterns were altered along roads and | ||
| 157 | due to non-native species. Differences in elevational species richness | 157 | due to non-native species. Differences in elevational species richness | ||
| 158 | patterns between regions disappeared along roadsides, and non-native | 158 | patterns between regions disappeared along roadsides, and non-native | ||
| 159 | species changed the patterns\u2019 character in all study regions. | 159 | species changed the patterns\u2019 character in all study regions. | ||
| 160 | Community dissimilarity was reduced along roadsides and through | 160 | Community dissimilarity was reduced along roadsides and through | ||
| 161 | non-native species. We also found a significant elevational decay of | 161 | non-native species. We also found a significant elevational decay of | ||
| 162 | beta-diversity, which however was not affected by roads or non-native | 162 | beta-diversity, which however was not affected by roads or non-native | ||
| 163 | species. Idiosyncratic native species richness patterns in plots away | 163 | species. Idiosyncratic native species richness patterns in plots away | ||
| 164 | from roads implicate region-specific mechanisms underlying these | 164 | from roads implicate region-specific mechanisms underlying these | ||
| 165 | patterns. However, along roadsides a clearer elevational signal | 165 | patterns. However, along roadsides a clearer elevational signal | ||
| 166 | emerged and species richness mostly peaked at mid-elevations. We | 166 | emerged and species richness mostly peaked at mid-elevations. We | ||
| 167 | conclude that both roads and non-native species lead to a | 167 | conclude that both roads and non-native species lead to a | ||
| 168 | homogenization of species richness patterns and plant communities in | 168 | homogenization of species richness patterns and plant communities in | ||
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