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en Facilitating permeability of landscapes impacted by roads for protected amphibians: patterns of movement for the great crested newt. -
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) 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 | 93 | "notes": "Amphibian populations are highly vulnerable to road | ||
| 80 | mortality and habitat fragmentation caused by road networks. Wildlife | 94 | mortality and habitat fragmentation caused by road networks. Wildlife | ||
| 81 | road tunnels are considered the most promising road mitigation measure | 95 | road tunnels are considered the most promising road mitigation measure | ||
| 82 | for amphibians yet generally remain inadequately monitored, resulting | 96 | for amphibians yet generally remain inadequately monitored, resulting | ||
| 83 | in mixed success rates in the short-term and uncertain conservation | 97 | in mixed success rates in the short-term and uncertain conservation | ||
| 84 | benefits in the long-term. We monitored a complex multi-tunnel and | 98 | 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 | 99 | fence system over five years and investigated the impact of the scheme | ||
| 86 | on movement patterns of two newt species, including the largest known | 100 | on movement patterns of two newt species, including the largest known | ||
| 87 | UK population of the great crested newt (Triturus cristatus), a | 101 | UK population of the great crested newt (Triturus cristatus), a | ||
| 88 | European Protected Species. We used a stage descriptive approach based | 102 | European Protected Species. We used a stage descriptive approach based | ||
| 89 | on capture positions to quantify newt movement patterns. Newt species | 103 | on capture positions to quantify newt movement patterns. Newt species | ||
| 90 | successfully used the mitigation but the system constituted a | 104 | successfully used the mitigation but the system constituted a | ||
| 91 | bottleneck to movements from the fences to the tunnels. Crossing rates | 105 | bottleneck to movements from the fences to the tunnels. Crossing rates | ||
| 92 | varied widely among years and were skewed towards autumn dispersal | 106 | varied widely among years and were skewed towards autumn dispersal | ||
| 93 | rather than spring breeding migration. There was a substantial | 107 | rather than spring breeding migration. There was a substantial | ||
| 94 | negative bias against adult male great crested newts using the system. | 108 | negative bias against adult male great crested newts using the system. | ||
| 95 | This study indicates that road tunnels could partially mitigate wider | 109 | This study indicates that road tunnels could partially mitigate wider | ||
| 96 | connectivity loss and fragmentation at the landscape scale for newt | 110 | connectivity loss and fragmentation at the landscape scale for newt | ||
| 97 | species. However, the observed bottleneck effects and seasonal bias | 111 | species. However, the observed bottleneck effects and seasonal bias | ||
| 98 | could have population-level effects which must be better understood, | 112 | could have population-level effects which must be better understood, | ||
| 99 | especially for small populations, so that improvements can be made. | 113 | especially for small populations, so that improvements can be made. | ||
| 100 | Current requirements for monitoring mitigation schemes | 114 | Current requirements for monitoring mitigation schemes | ||
| 101 | post-implementation are probably too short to assess their | 115 | post-implementation are probably too short to assess their | ||
| 102 | effectiveness in maintaining connectivity and to adequately understand | 116 | effectiveness in maintaining connectivity and to adequately understand | ||
| 103 | their population-level impacts.\n Palabras clave: Amphibian, | 117 | their population-level impacts.\n Palabras clave: Amphibian, | ||
| 104 | Landscape", | 118 | Landscape", | ||
| 105 | "notes_translated": { | 119 | "notes_translated": { | ||
| 106 | "en": "Amphibian populations are highly vulnerable to road | 120 | "en": "Amphibian populations are highly vulnerable to road | ||
| 107 | mortality and habitat fragmentation caused by road networks. Wildlife | 121 | mortality and habitat fragmentation caused by road networks. Wildlife | ||
| 108 | road tunnels are considered the most promising road mitigation measure | 122 | road tunnels are considered the most promising road mitigation measure | ||
| 109 | for amphibians yet generally remain inadequately monitored, resulting | 123 | for amphibians yet generally remain inadequately monitored, resulting | ||
| 110 | in mixed success rates in the short-term and uncertain conservation | 124 | in mixed success rates in the short-term and uncertain conservation | ||
| 111 | benefits in the long-term. We monitored a complex multi-tunnel and | 125 | 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 | 126 | fence system over five years and investigated the impact of the scheme | ||
| 113 | on movement patterns of two newt species, including the largest known | 127 | on movement patterns of two newt species, including the largest known | ||
| 114 | UK population of the great crested newt (Triturus cristatus), a | 128 | UK population of the great crested newt (Triturus cristatus), a | ||
| 115 | European Protected Species. We used a stage descriptive approach based | 129 | European Protected Species. We used a stage descriptive approach based | ||
| 116 | on capture positions to quantify newt movement patterns. Newt species | 130 | on capture positions to quantify newt movement patterns. Newt species | ||
| 117 | successfully used the mitigation but the system constituted a | 131 | successfully used the mitigation but the system constituted a | ||
| 118 | bottleneck to movements from the fences to the tunnels. Crossing rates | 132 | bottleneck to movements from the fences to the tunnels. Crossing rates | ||
| 119 | varied widely among years and were skewed towards autumn dispersal | 133 | varied widely among years and were skewed towards autumn dispersal | ||
| 120 | rather than spring breeding migration. There was a substantial | 134 | rather than spring breeding migration. There was a substantial | ||
| 121 | negative bias against adult male great crested newts using the system. | 135 | negative bias against adult male great crested newts using the system. | ||
| 122 | This study indicates that road tunnels could partially mitigate wider | 136 | This study indicates that road tunnels could partially mitigate wider | ||
| 123 | connectivity loss and fragmentation at the landscape scale for newt | 137 | connectivity loss and fragmentation at the landscape scale for newt | ||
| 124 | species. However, the observed bottleneck effects and seasonal bias | 138 | species. However, the observed bottleneck effects and seasonal bias | ||
| 125 | could have population-level effects which must be better understood, | 139 | could have population-level effects which must be better understood, | ||
| 126 | especially for small populations, so that improvements can be made. | 140 | especially for small populations, so that improvements can be made. | ||
| 127 | Current requirements for monitoring mitigation schemes | 141 | Current requirements for monitoring mitigation schemes | ||
| 128 | post-implementation are probably too short to assess their | 142 | post-implementation are probably too short to assess their | ||
| 129 | effectiveness in maintaining connectivity and to adequately understand | 143 | effectiveness in maintaining connectivity and to adequately understand | ||
| 130 | their population-level impacts.", | 144 | their population-level impacts.", | ||
| 131 | "es": "Amphibian populations are highly vulnerable to road | 145 | "es": "Amphibian populations are highly vulnerable to road | ||
| 132 | mortality and habitat fragmentation caused by road networks. Wildlife | 146 | mortality and habitat fragmentation caused by road networks. Wildlife | ||
| 133 | road tunnels are considered the most promising road mitigation measure | 147 | road tunnels are considered the most promising road mitigation measure | ||
| 134 | for amphibians yet generally remain inadequately monitored, resulting | 148 | for amphibians yet generally remain inadequately monitored, resulting | ||
| 135 | in mixed success rates in the short-term and uncertain conservation | 149 | in mixed success rates in the short-term and uncertain conservation | ||
| 136 | benefits in the long-term. We monitored a complex multi-tunnel and | 150 | 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 | 151 | fence system over five years and investigated the impact of the scheme | ||
| 138 | on movement patterns of two newt species, including the largest known | 152 | on movement patterns of two newt species, including the largest known | ||
| 139 | UK population of the great crested newt (Triturus cristatus), a | 153 | UK population of the great crested newt (Triturus cristatus), a | ||
| 140 | European Protected Species. We used a stage descriptive approach based | 154 | European Protected Species. We used a stage descriptive approach based | ||
| 141 | on capture positions to quantify newt movement patterns. Newt species | 155 | on capture positions to quantify newt movement patterns. Newt species | ||
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| 143 | bottleneck to movements from the fences to the tunnels. Crossing rates | 157 | bottleneck to movements from the fences to the tunnels. Crossing rates | ||
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| 145 | rather than spring breeding migration. There was a substantial | 159 | rather than spring breeding migration. There was a substantial | ||
| 146 | negative bias against adult male great crested newts using the system. | 160 | negative bias against adult male great crested newts using the system. | ||
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| 150 | could have population-level effects which must be better understood, | 164 | could have population-level effects which must be better understood, | ||
| 151 | especially for small populations, so that improvements can be made. | 165 | especially for small populations, so that improvements can be made. | ||
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| 314 | for protected amphibians: patterns of movement for the great crested | 328 | for protected amphibians: patterns of movement for the great crested | ||
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