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a2026-06-25
en Identification of strategic corridors for restoring landscape connectivity: application to the Iberian lynx. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Identification of strategic corridors for restoring landscape connectivity: application to the Iberian lynx.
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| 5 | "author": "Bl\u00e1zquez-Cabrera, S., Ciudad, C., Gast\u00f3n, A., | 5 | "author": "Bl\u00e1zquez-Cabrera, S., Ciudad, C., Gast\u00f3n, A., | ||
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| 81 | "name": "d248f722-aee7-5c7a-b51d-5e96aa18077d", | 95 | "name": "d248f722-aee7-5c7a-b51d-5e96aa18077d", | ||
| 82 | "notes": "The conservation or creation of ecological corridors is a | 96 | "notes": "The conservation or creation of ecological corridors is a | ||
| 83 | key to support species persistence in fragmented landscapes. However, | 97 | key to support species persistence in fragmented landscapes. However, | ||
| 84 | little guidance exists on where to concentrate the restoration | 98 | little guidance exists on where to concentrate the restoration | ||
| 85 | measures to improve corridor quality and functionality. Focusing on | 99 | measures to improve corridor quality and functionality. Focusing on | ||
| 86 | the emblematic Iberian lynx Lynx pardinus as the target species, and | 100 | the emblematic Iberian lynx Lynx pardinus as the target species, and | ||
| 87 | using a resistance surface parameterized through detailed telemetry | 101 | using a resistance surface parameterized through detailed telemetry | ||
| 88 | data for the species, we applied a modeling approach that identifies | 102 | data for the species, we applied a modeling approach that identifies | ||
| 89 | corridors whose restoration would be more beneficial for enhancing | 103 | corridors whose restoration would be more beneficial for enhancing | ||
| 90 | landscape connectivity. Connectivity benefits were quantified, first, | 104 | landscape connectivity. Connectivity benefits were quantified, first, | ||
| 91 | as the increase in the Probability of Connectivity metric (dPC) that | 105 | as the increase in the Probability of Connectivity metric (dPC) that | ||
| 92 | results for the entire population network after reducing the effective | 106 | results for the entire population network after reducing the effective | ||
| 93 | distance along a particular corridor to its minimum possible value | 107 | distance along a particular corridor to its minimum possible value | ||
| 94 | through restoration, and second, as dPC normalized by a proxy of the | 108 | through restoration, and second, as dPC normalized by a proxy of the | ||
| 95 | total restoration effort that would be required in each corridor. | 109 | total restoration effort that would be required in each corridor. | ||
| 96 | Results showed that the corridor restoration benefits were related to | 110 | Results showed that the corridor restoration benefits were related to | ||
| 97 | their effective distance (accumulated cost of movement along the | 111 | their effective distance (accumulated cost of movement along the | ||
| 98 | corridor) and network centrality (potential frequency of use by | 112 | corridor) and network centrality (potential frequency of use by | ||
| 99 | dispersing individuals) in the current landscapes. Two corridors in | 113 | dispersing individuals) in the current landscapes. Two corridors in | ||
| 100 | which restoration efforts may be more desirable for the Iberian lynx | 114 | which restoration efforts may be more desirable for the Iberian lynx | ||
| 101 | were highlighted: the one linking the Do\u00f1ana-Aljarafe population | 115 | were highlighted: the one linking the Do\u00f1ana-Aljarafe population | ||
| 102 | with other populations and reintroduction areas further north, and a | 116 | with other populations and reintroduction areas further north, and a | ||
| 103 | west-east axis connecting the different populations in Sierra Morena. | 117 | west-east axis connecting the different populations in Sierra Morena. | ||
| 104 | In general, the applied approach is a valuable tool to estimate how | 118 | In general, the applied approach is a valuable tool to estimate how | ||
| 105 | landscape connectivity may be affected when changes in the landscape | 119 | landscape connectivity may be affected when changes in the landscape | ||
| 106 | are planned or can be predicted. This approach can be applied to | 120 | are planned or can be predicted. This approach can be applied to | ||
| 107 | potential corridors linking future reintroduction areas of the Iberian | 121 | potential corridors linking future reintroduction areas of the Iberian | ||
| 108 | lynx, to case studies focusing on other landscapes and animal species, | 122 | lynx, to case studies focusing on other landscapes and animal species, | ||
| 109 | or to evaluate the impacts of corridor degradation or loss due to land | 123 | or to evaluate the impacts of corridor degradation or loss due to land | ||
| 110 | use changes and other pressures.", | 124 | use changes and other pressures.", | ||
| 111 | "notes_translated": { | 125 | "notes_translated": { | ||
| 112 | "en": "The conservation or creation of ecological corridors is a | 126 | "en": "The conservation or creation of ecological corridors is a | ||
| 113 | key to support species persistence in fragmented landscapes. However, | 127 | key to support species persistence in fragmented landscapes. However, | ||
| 114 | little guidance exists on where to concentrate the restoration | 128 | little guidance exists on where to concentrate the restoration | ||
| 115 | measures to improve corridor quality and functionality. Focusing on | 129 | measures to improve corridor quality and functionality. Focusing on | ||
| 116 | the emblematic Iberian lynx\u00a0Lynx pardinus\u00a0as the target | 130 | the emblematic Iberian lynx\u00a0Lynx pardinus\u00a0as the target | ||
| 117 | species, and using a resistance surface parameterized through detailed | 131 | species, and using a resistance surface parameterized through detailed | ||
| 118 | telemetry data for the species, we applied a modeling approach that | 132 | telemetry data for the species, we applied a modeling approach that | ||
| 119 | identifies corridors whose restoration would be more beneficial for | 133 | identifies corridors whose restoration would be more beneficial for | ||
| 120 | enhancing landscape connectivity. Connectivity benefits were | 134 | enhancing landscape connectivity. Connectivity benefits were | ||
| 121 | quantified, first, as the increase in the Probability of Connectivity | 135 | quantified, first, as the increase in the Probability of Connectivity | ||
| 122 | metric (dPC) that results for the entire population network after | 136 | metric (dPC) that results for the entire population network after | ||
| 123 | reducing the effective distance along a particular corridor to its | 137 | reducing the effective distance along a particular corridor to its | ||
| 124 | minimum possible value through restoration, and second, as dPC | 138 | minimum possible value through restoration, and second, as dPC | ||
| 125 | normalized by a proxy of the total restoration effort that would be | 139 | normalized by a proxy of the total restoration effort that would be | ||
| 126 | required in each corridor. Results showed that the corridor | 140 | required in each corridor. Results showed that the corridor | ||
| 127 | restoration benefits were related to their effective distance | 141 | restoration benefits were related to their effective distance | ||
| 128 | (accumulated cost of movement along the corridor) and network | 142 | (accumulated cost of movement along the corridor) and network | ||
| 129 | centrality (potential frequency of use by dispersing individuals) in | 143 | centrality (potential frequency of use by dispersing individuals) in | ||
| 130 | the current landscapes. Two corridors in which restoration efforts may | 144 | the current landscapes. Two corridors in which restoration efforts may | ||
| 131 | be more desirable for the Iberian lynx were highlighted: the one | 145 | be more desirable for the Iberian lynx were highlighted: the one | ||
| 132 | linking the Do\u00f1ana-Aljarafe population with other populations and | 146 | linking the Do\u00f1ana-Aljarafe population with other populations and | ||
| 133 | reintroduction areas further north, and a west-east axis connecting | 147 | reintroduction areas further north, and a west-east axis connecting | ||
| 134 | the different populations in Sierra Morena. In general, the applied | 148 | the different populations in Sierra Morena. In general, the applied | ||
| 135 | approach is a valuable tool to estimate how landscape connectivity may | 149 | approach is a valuable tool to estimate how landscape connectivity may | ||
| 136 | be affected when changes in the landscape are planned or can be | 150 | be affected when changes in the landscape are planned or can be | ||
| 137 | predicted. This approach can be applied to potential corridors linking | 151 | predicted. This approach can be applied to potential corridors linking | ||
| 138 | future reintroduction areas of the Iberian lynx, to case studies | 152 | future reintroduction areas of the Iberian lynx, to case studies | ||
| 139 | focusing on other landscapes and animal species, or to evaluate the | 153 | focusing on other landscapes and animal species, or to evaluate the | ||
| 140 | impacts of corridor degradation or loss due to land use changes and | 154 | impacts of corridor degradation or loss due to land use changes and | ||
| 141 | other pressures.", | 155 | other pressures.", | ||
| 142 | "es": "The conservation or creation of ecological corridors is a | 156 | "es": "The conservation or creation of ecological corridors is a | ||
| 143 | key to support species persistence in fragmented landscapes. However, | 157 | key to support species persistence in fragmented landscapes. However, | ||
| 144 | little guidance exists on where to concentrate the restoration | 158 | little guidance exists on where to concentrate the restoration | ||
| 145 | measures to improve corridor quality and functionality. Focusing on | 159 | measures to improve corridor quality and functionality. Focusing on | ||
| 146 | the emblematic Iberian lynx Lynx pardinus as the target species, and | 160 | the emblematic Iberian lynx Lynx pardinus as the target species, and | ||
| 147 | using a resistance surface parameterized through detailed telemetry | 161 | using a resistance surface parameterized through detailed telemetry | ||
| 148 | data for the species, we applied a modeling approach that identifies | 162 | data for the species, we applied a modeling approach that identifies | ||
| 149 | corridors whose restoration would be more beneficial for enhancing | 163 | corridors whose restoration would be more beneficial for enhancing | ||
| 150 | landscape connectivity. Connectivity benefits were quantified, first, | 164 | landscape connectivity. Connectivity benefits were quantified, first, | ||
| 151 | as the increase in the Probability of Connectivity metric (dPC) that | 165 | as the increase in the Probability of Connectivity metric (dPC) that | ||
| 152 | results for the entire population network after reducing the effective | 166 | results for the entire population network after reducing the effective | ||
| 153 | distance along a particular corridor to its minimum possible value | 167 | distance along a particular corridor to its minimum possible value | ||
| 154 | through restoration, and second, as dPC normalized by a proxy of the | 168 | through restoration, and second, as dPC normalized by a proxy of the | ||
| 155 | total restoration effort that would be required in each corridor. | 169 | total restoration effort that would be required in each corridor. | ||
| 156 | Results showed that the corridor restoration benefits were related to | 170 | Results showed that the corridor restoration benefits were related to | ||
| 157 | their effective distance (accumulated cost of movement along the | 171 | their effective distance (accumulated cost of movement along the | ||
| 158 | corridor) and network centrality (potential frequency of use by | 172 | corridor) and network centrality (potential frequency of use by | ||
| 159 | dispersing individuals) in the current landscapes. Two corridors in | 173 | dispersing individuals) in the current landscapes. Two corridors in | ||
| 160 | which restoration efforts may be more desirable for the Iberian lynx | 174 | which restoration efforts may be more desirable for the Iberian lynx | ||
| 161 | were highlighted: the one linking the Do\u00f1ana-Aljarafe population | 175 | were highlighted: the one linking the Do\u00f1ana-Aljarafe population | ||
| 162 | with other populations and reintroduction areas further north, and a | 176 | with other populations and reintroduction areas further north, and a | ||
| 163 | west-east axis connecting the different populations in Sierra Morena. | 177 | west-east axis connecting the different populations in Sierra Morena. | ||
| 164 | In general, the applied approach is a valuable tool to estimate how | 178 | In general, the applied approach is a valuable tool to estimate how | ||
| 165 | landscape connectivity may be affected when changes in the landscape | 179 | landscape connectivity may be affected when changes in the landscape | ||
| 166 | are planned or can be predicted. This approach can be applied to | 180 | are planned or can be predicted. This approach can be applied to | ||
| 167 | potential corridors linking future reintroduction areas of the Iberian | 181 | potential corridors linking future reintroduction areas of the Iberian | ||
| 168 | lynx, to case studies focusing on other landscapes and animal species, | 182 | lynx, to case studies focusing on other landscapes and animal species, | ||
| 169 | or to evaluate the impacts of corridor degradation or loss due to land | 183 | or to evaluate the impacts of corridor degradation or loss due to land | ||
| 170 | use changes and other pressures." | 184 | use changes and other pressures." | ||
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