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En el instante 23 de junio de 2026, 16:04:36 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 Facilitating permeability of landscapes impacted by roads for protected amphibians: patterns of movement for the great crested newt.
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| 79 | "notes": "Amphibian populations are highly vulnerable to road | 79 | "notes": "Amphibian populations are highly vulnerable to road | ||
| 80 | mortality and habitat fragmentation caused by road networks. Wildlife | 80 | mortality and habitat fragmentation caused by road networks. Wildlife | ||
| 81 | road tunnels are considered the most promising road mitigation measure | 81 | road tunnels are considered the most promising road mitigation measure | ||
| 82 | for amphibians yet generally remain inadequately monitored, resulting | 82 | for amphibians yet generally remain inadequately monitored, resulting | ||
| 83 | in mixed success rates in the short-term and uncertain conservation | 83 | in mixed success rates in the short-term and uncertain conservation | ||
| 84 | benefits in the long-term. We monitored a complex multi-tunnel and | 84 | benefits in the long-term. We monitored a complex multi-tunnel and | ||
| 85 | fence system over five years and investigated the impact of the scheme | 85 | fence system over five years and investigated the impact of the scheme | ||
| 86 | on movement patterns of two newt species, including the largest known | 86 | on movement patterns of two newt species, including the largest known | ||
| 87 | UK population of the great crested newt (Triturus cristatus), a | 87 | UK population of the great crested newt (Triturus cristatus), a | ||
| 88 | European Protected Species. We used a stage descriptive approach based | 88 | European Protected Species. We used a stage descriptive approach based | ||
| 89 | on capture positions to quantify newt movement patterns. Newt species | 89 | on capture positions to quantify newt movement patterns. Newt species | ||
| 90 | successfully used the mitigation but the system constituted a | 90 | successfully used the mitigation but the system constituted a | ||
| 91 | bottleneck to movements from the fences to the tunnels. Crossing rates | 91 | bottleneck to movements from the fences to the tunnels. Crossing rates | ||
| 92 | varied widely among years and were skewed towards autumn dispersal | 92 | varied widely among years and were skewed towards autumn dispersal | ||
| 93 | rather than spring breeding migration. There was a substantial | 93 | rather than spring breeding migration. There was a substantial | ||
| 94 | negative bias against adult male great crested newts using the system. | 94 | negative bias against adult male great crested newts using the system. | ||
| 95 | This study indicates that road tunnels could partially mitigate wider | 95 | This study indicates that road tunnels could partially mitigate wider | ||
| 96 | connectivity loss and fragmentation at the landscape scale for newt | 96 | connectivity loss and fragmentation at the landscape scale for newt | ||
| 97 | species. However, the observed bottleneck effects and seasonal bias | 97 | species. However, the observed bottleneck effects and seasonal bias | ||
| 98 | could have population-level effects which must be better understood, | 98 | could have population-level effects which must be better understood, | ||
| 99 | especially for small populations, so that improvements can be made. | 99 | especially for small populations, so that improvements can be made. | ||
| 100 | Current requirements for monitoring mitigation schemes | 100 | Current requirements for monitoring mitigation schemes | ||
| 101 | post-implementation are probably too short to assess their | 101 | post-implementation are probably too short to assess their | ||
| 102 | effectiveness in maintaining connectivity and to adequately understand | 102 | effectiveness in maintaining connectivity and to adequately understand | ||
| 103 | their population-level impacts.\n Palabras clave: Amphibian, | 103 | their population-level impacts.\n Palabras clave: Amphibian, | ||
| 104 | Landscape", | 104 | Landscape", | ||
| 105 | "notes_translated": { | 105 | "notes_translated": { | ||
| 106 | "en": "Amphibian populations are highly vulnerable to road | 106 | "en": "Amphibian populations are highly vulnerable to road | ||
| 107 | mortality and habitat fragmentation caused by road networks. Wildlife | 107 | mortality and habitat fragmentation caused by road networks. Wildlife | ||
| 108 | road tunnels are considered the most promising road mitigation measure | 108 | road tunnels are considered the most promising road mitigation measure | ||
| 109 | for amphibians yet generally remain inadequately monitored, resulting | 109 | for amphibians yet generally remain inadequately monitored, resulting | ||
| 110 | in mixed success rates in the short-term and uncertain conservation | 110 | in mixed success rates in the short-term and uncertain conservation | ||
| 111 | benefits in the long-term. We monitored a complex multi-tunnel and | 111 | benefits in the long-term. We monitored a complex multi-tunnel and | ||
| 112 | fence system over five years and investigated the impact of the scheme | 112 | fence system over five years and investigated the impact of the scheme | ||
| 113 | on movement patterns of two newt species, including the largest known | 113 | on movement patterns of two newt species, including the largest known | ||
| 114 | UK population of the great crested newt (Triturus cristatus), a | 114 | UK population of the great crested newt (Triturus cristatus), a | ||
| 115 | European Protected Species. We used a stage descriptive approach based | 115 | European Protected Species. We used a stage descriptive approach based | ||
| 116 | on capture positions to quantify newt movement patterns. Newt species | 116 | on capture positions to quantify newt movement patterns. Newt species | ||
| 117 | successfully used the mitigation but the system constituted a | 117 | successfully used the mitigation but the system constituted a | ||
| 118 | bottleneck to movements from the fences to the tunnels. Crossing rates | 118 | bottleneck to movements from the fences to the tunnels. Crossing rates | ||
| 119 | varied widely among years and were skewed towards autumn dispersal | 119 | varied widely among years and were skewed towards autumn dispersal | ||
| 120 | rather than spring breeding migration. There was a substantial | 120 | rather than spring breeding migration. There was a substantial | ||
| 121 | negative bias against adult male great crested newts using the system. | 121 | negative bias against adult male great crested newts using the system. | ||
| 122 | This study indicates that road tunnels could partially mitigate wider | 122 | This study indicates that road tunnels could partially mitigate wider | ||
| 123 | connectivity loss and fragmentation at the landscape scale for newt | 123 | connectivity loss and fragmentation at the landscape scale for newt | ||
| 124 | species. However, the observed bottleneck effects and seasonal bias | 124 | species. However, the observed bottleneck effects and seasonal bias | ||
| 125 | could have population-level effects which must be better understood, | 125 | could have population-level effects which must be better understood, | ||
| 126 | especially for small populations, so that improvements can be made. | 126 | especially for small populations, so that improvements can be made. | ||
| 127 | Current requirements for monitoring mitigation schemes | 127 | Current requirements for monitoring mitigation schemes | ||
| 128 | post-implementation are probably too short to assess their | 128 | post-implementation are probably too short to assess their | ||
| 129 | effectiveness in maintaining connectivity and to adequately understand | 129 | effectiveness in maintaining connectivity and to adequately understand | ||
| 130 | their population-level impacts.", | 130 | their population-level impacts.", | ||
| 131 | "es": "Amphibian populations are highly vulnerable to road | 131 | "es": "Amphibian populations are highly vulnerable to road | ||
| 132 | mortality and habitat fragmentation caused by road networks. Wildlife | 132 | mortality and habitat fragmentation caused by road networks. Wildlife | ||
| 133 | road tunnels are considered the most promising road mitigation measure | 133 | road tunnels are considered the most promising road mitigation measure | ||
| 134 | for amphibians yet generally remain inadequately monitored, resulting | 134 | for amphibians yet generally remain inadequately monitored, resulting | ||
| 135 | in mixed success rates in the short-term and uncertain conservation | 135 | in mixed success rates in the short-term and uncertain conservation | ||
| 136 | benefits in the long-term. We monitored a complex multi-tunnel and | 136 | benefits in the long-term. We monitored a complex multi-tunnel and | ||
| 137 | fence system over five years and investigated the impact of the scheme | 137 | fence system over five years and investigated the impact of the scheme | ||
| 138 | on movement patterns of two newt species, including the largest known | 138 | on movement patterns of two newt species, including the largest known | ||
| 139 | UK population of the great crested newt (Triturus cristatus), a | 139 | UK population of the great crested newt (Triturus cristatus), a | ||
| 140 | European Protected Species. We used a stage descriptive approach based | 140 | European Protected Species. We used a stage descriptive approach based | ||
| 141 | on capture positions to quantify newt movement patterns. Newt species | 141 | on capture positions to quantify newt movement patterns. Newt species | ||
| 142 | successfully used the mitigation but the system constituted a | 142 | successfully used the mitigation but the system constituted a | ||
| 143 | bottleneck to movements from the fences to the tunnels. Crossing rates | 143 | bottleneck to movements from the fences to the tunnels. Crossing rates | ||
| 144 | varied widely among years and were skewed towards autumn dispersal | 144 | varied widely among years and were skewed towards autumn dispersal | ||
| 145 | rather than spring breeding migration. There was a substantial | 145 | rather than spring breeding migration. There was a substantial | ||
| 146 | negative bias against adult male great crested newts using the system. | 146 | negative bias against adult male great crested newts using the system. | ||
| 147 | This study indicates that road tunnels could partially mitigate wider | 147 | This study indicates that road tunnels could partially mitigate wider | ||
| 148 | connectivity loss and fragmentation at the landscape scale for newt | 148 | connectivity loss and fragmentation at the landscape scale for newt | ||
| 149 | species. However, the observed bottleneck effects and seasonal bias | 149 | species. However, the observed bottleneck effects and seasonal bias | ||
| 150 | could have population-level effects which must be better understood, | 150 | could have population-level effects which must be better understood, | ||
| 151 | especially for small populations, so that improvements can be made. | 151 | especially for small populations, so that improvements can be made. | ||
| 152 | Current requirements for monitoring mitigation schemes | 152 | Current requirements for monitoring mitigation schemes | ||
| 153 | post-implementation are probably too short to assess their | 153 | post-implementation are probably too short to assess their | ||
| 154 | effectiveness in maintaining connectivity and to adequately understand | 154 | effectiveness in maintaining connectivity and to adequately understand | ||
| 155 | their population-level impacts.\n Palabras clave: Amphibian, | 155 | their population-level impacts.\n Palabras clave: Amphibian, | ||
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