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a2026-06-25
en Landscape connectivity and spatial prioritization in an urbanising world: a network analysis approach for a threatened amphibian. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Landscape connectivity and spatial prioritization in an urbanising world: a network analysis approach for a threatened amphibian.
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| 79 | "notes": "Habitat fragmentation affects amphibian populations | 93 | "notes": "Habitat fragmentation affects amphibian populations | ||
| 80 | worldwide. Urban expansion and associated infrastructure are a main | 94 | worldwide. Urban expansion and associated infrastructure are a main | ||
| 81 | cause of habitat degradation and loss of landscape-scale habitat | 95 | cause of habitat degradation and loss of landscape-scale habitat | ||
| 82 | connectivity. Mitigation measures such as underpasses and associated | 96 | connectivity. Mitigation measures such as underpasses and associated | ||
| 83 | fences are implemented to reduce the impacts of development on | 97 | fences are implemented to reduce the impacts of development on | ||
| 84 | protected species. However, such efforts focus largely on local | 98 | protected species. However, such efforts focus largely on local | ||
| 85 | outcomes rather than envisioning how mitigation may contribute to | 99 | outcomes rather than envisioning how mitigation may contribute to | ||
| 86 | habitat connectivity and population persistence at the landscape | 100 | habitat connectivity and population persistence at the landscape | ||
| 87 | scale. We used a graph-theoretic approach to model structural and | 101 | scale. We used a graph-theoretic approach to model structural and | ||
| 88 | functional connectivity for a widespread but declining pond-breeding | 102 | functional connectivity for a widespread but declining pond-breeding | ||
| 89 | amphibian, the great crested newt (Triturus cristatus). This involved | 103 | amphibian, the great crested newt (Triturus cristatus). This involved | ||
| 90 | assessing species movement among breeding ponds and associated | 104 | assessing species movement among breeding ponds and associated | ||
| 91 | landscapes with different levels of urban and rural development and | 105 | landscapes with different levels of urban and rural development and | ||
| 92 | linear barriers. We used recent regional pond survey data for great | 106 | linear barriers. We used recent regional pond survey data for great | ||
| 93 | crested newts combined with published data on movement and habitat use | 107 | crested newts combined with published data on movement and habitat use | ||
| 94 | to explore connectivity. Landscape connectivity was affected by | 108 | to explore connectivity. Landscape connectivity was affected by | ||
| 95 | factors such as habitat quality and quantity, scale of movement and | 109 | factors such as habitat quality and quantity, scale of movement and | ||
| 96 | different degrees of road permeability. Linear barriers to movement | 110 | different degrees of road permeability. Linear barriers to movement | ||
| 97 | and differences in their permeability were critical for predicting | 111 | and differences in their permeability were critical for predicting | ||
| 98 | their impact on both migratory and dispersal movements in Triturus | 112 | their impact on both migratory and dispersal movements in Triturus | ||
| 99 | cristatus. Incorporating landscape connectivity modelling which | 113 | cristatus. Incorporating landscape connectivity modelling which | ||
| 100 | includes the impact of barriers such as roads would substantially | 114 | includes the impact of barriers such as roads would substantially | ||
| 101 | improve population-level outcomes from mitigation schemes. An accurate | 115 | improve population-level outcomes from mitigation schemes. An accurate | ||
| 102 | understanding of the far-reaching consequences of road mitigation as | 116 | understanding of the far-reaching consequences of road mitigation as | ||
| 103 | well as immediate, local effects, combined with our methods of | 117 | well as immediate, local effects, combined with our methods of | ||
| 104 | assessing road permeability could transform future mitigation efforts | 118 | assessing road permeability could transform future mitigation efforts | ||
| 105 | by directing action to places that not only improve individual | 119 | by directing action to places that not only improve individual | ||
| 106 | survival but also maximise connectivity at the landscape-scale.", | 120 | survival but also maximise connectivity at the landscape-scale.", | ||
| 107 | "notes_translated": { | 121 | "notes_translated": { | ||
| 108 | "en": "Habitat fragmentation\u00a0affects amphibian populations | 122 | "en": "Habitat fragmentation\u00a0affects amphibian populations | ||
| 109 | worldwide. Urban expansion and associated infrastructure are a main | 123 | worldwide. Urban expansion and associated infrastructure are a main | ||
| 110 | cause of habitat degradation and loss of landscape-scale habitat | 124 | cause of habitat degradation and loss of landscape-scale habitat | ||
| 111 | connectivity.\u00a0Mitigation measures\u00a0such as underpasses and | 125 | connectivity.\u00a0Mitigation measures\u00a0such as underpasses and | ||
| 112 | associated fences are implemented to reduce the impacts of development | 126 | associated fences are implemented to reduce the impacts of development | ||
| 113 | on protected species. However, such efforts focus largely on local | 127 | on protected species. However, such efforts focus largely on local | ||
| 114 | outcomes rather than envisioning how mitigation may contribute to | 128 | outcomes rather than envisioning how mitigation may contribute to | ||
| 115 | habitat connectivity and population persistence at the landscape | 129 | habitat connectivity and population persistence at the landscape | ||
| 116 | scale. We used a graph-theoretic approach to model structural and | 130 | scale. We used a graph-theoretic approach to model structural and | ||
| 117 | functional connectivity for a widespread but declining pond-breeding | 131 | functional connectivity for a widespread but declining pond-breeding | ||
| 118 | amphibian, the great crested newt (Triturus\u00a0cristatus). This | 132 | amphibian, the great crested newt (Triturus\u00a0cristatus). This | ||
| 119 | involved assessing species movement among breeding ponds and | 133 | involved assessing species movement among breeding ponds and | ||
| 120 | associated landscapes with different levels of urban and rural | 134 | associated landscapes with different levels of urban and rural | ||
| 121 | development and linear barriers. We used recent regional pond survey | 135 | development and linear barriers. We used recent regional pond survey | ||
| 122 | data for great crested newts combined with published data on movement | 136 | data for great crested newts combined with published data on movement | ||
| 123 | and habitat use to explore connectivity. Landscape connectivity was | 137 | and habitat use to explore connectivity. Landscape connectivity was | ||
| 124 | affected by factors such as habitat quality and quantity, scale of | 138 | affected by factors such as habitat quality and quantity, scale of | ||
| 125 | movement and different degrees of road permeability. Linear barriers | 139 | movement and different degrees of road permeability. Linear barriers | ||
| 126 | to movement and differences in their permeability were critical for | 140 | to movement and differences in their permeability were critical for | ||
| 127 | predicting their impact on both migratory and dispersal movements | 141 | predicting their impact on both migratory and dispersal movements | ||
| 128 | in\u00a0Triturus cristatus. Incorporating landscape connectivity | 142 | in\u00a0Triturus cristatus. Incorporating landscape connectivity | ||
| 129 | modelling which includes the impact of barriers such as roads would | 143 | modelling which includes the impact of barriers such as roads would | ||
| 130 | substantially improve population-level outcomes from mitigation | 144 | substantially improve population-level outcomes from mitigation | ||
| 131 | schemes. An accurate understanding of the far-reaching consequences of | 145 | schemes. An accurate understanding of the far-reaching consequences of | ||
| 132 | road mitigation as well as immediate, local effects, combined with our | 146 | road mitigation as well as immediate, local effects, combined with our | ||
| 133 | methods of assessing road permeability could transform future | 147 | methods of assessing road permeability could transform future | ||
| 134 | mitigation efforts by directing action to places that not only improve | 148 | mitigation efforts by directing action to places that not only improve | ||
| 135 | individual survival but also maximise connectivity at the | 149 | individual survival but also maximise connectivity at the | ||
| 136 | landscape-scale.", | 150 | landscape-scale.", | ||
| 137 | "es": "Habitat fragmentation affects amphibian populations | 151 | "es": "Habitat fragmentation affects amphibian populations | ||
| 138 | worldwide. Urban expansion and associated infrastructure are a main | 152 | worldwide. Urban expansion and associated infrastructure are a main | ||
| 139 | cause of habitat degradation and loss of landscape-scale habitat | 153 | cause of habitat degradation and loss of landscape-scale habitat | ||
| 140 | connectivity. Mitigation measures such as underpasses and associated | 154 | connectivity. Mitigation measures such as underpasses and associated | ||
| 141 | fences are implemented to reduce the impacts of development on | 155 | fences are implemented to reduce the impacts of development on | ||
| 142 | protected species. However, such efforts focus largely on local | 156 | protected species. However, such efforts focus largely on local | ||
| 143 | outcomes rather than envisioning how mitigation may contribute to | 157 | outcomes rather than envisioning how mitigation may contribute to | ||
| 144 | habitat connectivity and population persistence at the landscape | 158 | habitat connectivity and population persistence at the landscape | ||
| 145 | scale. We used a graph-theoretic approach to model structural and | 159 | scale. We used a graph-theoretic approach to model structural and | ||
| 146 | functional connectivity for a widespread but declining pond-breeding | 160 | functional connectivity for a widespread but declining pond-breeding | ||
| 147 | amphibian, the great crested newt (Triturus cristatus). This involved | 161 | amphibian, the great crested newt (Triturus cristatus). This involved | ||
| 148 | assessing species movement among breeding ponds and associated | 162 | assessing species movement among breeding ponds and associated | ||
| 149 | landscapes with different levels of urban and rural development and | 163 | landscapes with different levels of urban and rural development and | ||
| 150 | linear barriers. We used recent regional pond survey data for great | 164 | linear barriers. We used recent regional pond survey data for great | ||
| 151 | crested newts combined with published data on movement and habitat use | 165 | crested newts combined with published data on movement and habitat use | ||
| 152 | to explore connectivity. Landscape connectivity was affected by | 166 | to explore connectivity. Landscape connectivity was affected by | ||
| 153 | factors such as habitat quality and quantity, scale of movement and | 167 | factors such as habitat quality and quantity, scale of movement and | ||
| 154 | different degrees of road permeability. Linear barriers to movement | 168 | different degrees of road permeability. Linear barriers to movement | ||
| 155 | and differences in their permeability were critical for predicting | 169 | and differences in their permeability were critical for predicting | ||
| 156 | their impact on both migratory and dispersal movements in Triturus | 170 | their impact on both migratory and dispersal movements in Triturus | ||
| 157 | cristatus. Incorporating landscape connectivity modelling which | 171 | cristatus. Incorporating landscape connectivity modelling which | ||
| 158 | includes the impact of barriers such as roads would substantially | 172 | includes the impact of barriers such as roads would substantially | ||
| 159 | improve population-level outcomes from mitigation schemes. An accurate | 173 | improve population-level outcomes from mitigation schemes. An accurate | ||
| 160 | understanding of the far-reaching consequences of road mitigation as | 174 | understanding of the far-reaching consequences of road mitigation as | ||
| 161 | well as immediate, local effects, combined with our methods of | 175 | well as immediate, local effects, combined with our methods of | ||
| 162 | assessing road permeability could transform future mitigation efforts | 176 | assessing road permeability could transform future mitigation efforts | ||
| 163 | by directing action to places that not only improve individual | 177 | by directing action to places that not only improve individual | ||
| 164 | survival but also maximise connectivity at the landscape-scale." | 178 | survival but also maximise connectivity at the landscape-scale." | ||
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