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En el instante 23 de junio de 2026, 16:09:40 UTC,
-
Modificado el valor del campo
spatial_coverage
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en Natura 2000 sites, public forests and riparian corridors: the connectivity backbone of forest green infrastructure.
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| 83 | "name": "40e79341-3b87-5927-91ee-2dab140533f6", | 83 | "name": "40e79341-3b87-5927-91ee-2dab140533f6", | ||
| 84 | "notes": "The connectivity of protected areas, such as the Natura | 84 | "notes": "The connectivity of protected areas, such as the Natura | ||
| 85 | 2000 network, is crucial for maintaining healthy ecosystems and for | 85 | 2000 network, is crucial for maintaining healthy ecosystems and for | ||
| 86 | the delivery of ecosystem services into the wider landscapes in which | 86 | the delivery of ecosystem services into the wider landscapes in which | ||
| 87 | they are embedded. We here present a novel combination of methods for | 87 | they are embedded. We here present a novel combination of methods for | ||
| 88 | connectivity analysis across heterogeneous landscapes, integrating | 88 | connectivity analysis across heterogeneous landscapes, integrating | ||
| 89 | graph-based analyses, least-cost path modelling and the Probability of | 89 | graph-based analyses, least-cost path modelling and the Probability of | ||
| 90 | Connectivity metric, and apply these methods to the network of Natura | 90 | Connectivity metric, and apply these methods to the network of Natura | ||
| 91 | 2000 woodland sites in mainland Spain. We deliver key insights on the | 91 | 2000 woodland sites in mainland Spain. We deliver key insights on the | ||
| 92 | connectors between Natura 2000 sites: their location and width | 92 | connectors between Natura 2000 sites: their location and width | ||
| 93 | (including transboundary ones), their prioritization in conservation | 93 | (including transboundary ones), their prioritization in conservation | ||
| 94 | and restoration scenarios involving different land uses, and the | 94 | and restoration scenarios involving different land uses, and the | ||
| 95 | bottlenecks (weak points due to land use pressures) found along them. | 95 | bottlenecks (weak points due to land use pressures) found along them. | ||
| 96 | Based on these results, we characterize the landscapes traversed by | 96 | Based on these results, we characterize the landscapes traversed by | ||
| 97 | the connectors within and outside the protected sites to inform | 97 | the connectors within and outside the protected sites to inform | ||
| 98 | related land management decisions.\n We show that forests of public | 98 | related land management decisions.\n We show that forests of public | ||
| 99 | utility play a key role in sustaining Natura 2000 connectivity in | 99 | utility play a key role in sustaining Natura 2000 connectivity in | ||
| 100 | Spain. They may qualify as an effective area-based conservation | 100 | Spain. They may qualify as an effective area-based conservation | ||
| 101 | measure significantly contributing to the connectivity element of | 101 | measure significantly contributing to the connectivity element of | ||
| 102 | Aichi Target 11. Riparian forests were part of the identified | 102 | Aichi Target 11. Riparian forests were part of the identified | ||
| 103 | connectors much more frequently than expected by their area. They | 103 | connectors much more frequently than expected by their area. They | ||
| 104 | stand out as a crucial green infrastructure safeguarding the | 104 | stand out as a crucial green infrastructure safeguarding the | ||
| 105 | connectivity of Natura 2000 woodland habitats, particularly when | 105 | connectivity of Natura 2000 woodland habitats, particularly when | ||
| 106 | forest species need to traverse landscapes dominated by agricultural | 106 | forest species need to traverse landscapes dominated by agricultural | ||
| 107 | and artificial land uses.\n Natura 2000 sites have good connectivity | 107 | and artificial land uses.\n Natura 2000 sites have good connectivity | ||
| 108 | conditions compared to unprotected lands. First, the identified | 108 | conditions compared to unprotected lands. First, the identified | ||
| 109 | woodland connectors preferentially traversed Natura 2000 lands. | 109 | woodland connectors preferentially traversed Natura 2000 lands. | ||
| 110 | Second, the large majority of bottlenecks occurred outside Natura | 110 | Second, the large majority of bottlenecks occurred outside Natura | ||
| 111 | 2000. Natura 2000 sites cannot, however, be considered free from | 111 | 2000. Natura 2000 sites cannot, however, be considered free from | ||
| 112 | connectivity limitations; they still contained a significant number of | 112 | connectivity limitations; they still contained a significant number of | ||
| 113 | bottlenecks that would need to be addressed in the site-level | 113 | bottlenecks that would need to be addressed in the site-level | ||
| 114 | management plans.\n The priority connectors for conservation were | 114 | management plans.\n The priority connectors for conservation were | ||
| 115 | preferentially found in the well-forested and well-protected | 115 | preferentially found in the well-forested and well-protected | ||
| 116 | landscapes in the main mountain ranges of Spain. On the contrary, the | 116 | landscapes in the main mountain ranges of Spain. On the contrary, the | ||
| 117 | priority connectors for restoration traversed much more frequently | 117 | priority connectors for restoration traversed much more frequently | ||
| 118 | landscapes dominated by agriculture. In these landscapes, connectivity | 118 | landscapes dominated by agriculture. In these landscapes, connectivity | ||
| 119 | improvements largely depend on the restoration of riparian forests and | 119 | improvements largely depend on the restoration of riparian forests and | ||
| 120 | on measures that mitigate the intensification of agriculture by | 120 | on measures that mitigate the intensification of agriculture by | ||
| 121 | promoting landscape complexity and natural vegetation remnants. The | 121 | promoting landscape complexity and natural vegetation remnants. The | ||
| 122 | remarkable spatial segregation found between the priority landscapes | 122 | remarkable spatial segregation found between the priority landscapes | ||
| 123 | for connectivity conservation and those of priority for restoration | 123 | for connectivity conservation and those of priority for restoration | ||
| 124 | highlights the need for an integrated perspective for land use | 124 | highlights the need for an integrated perspective for land use | ||
| 125 | planning and for the management of the Natura 2000 network in | 125 | planning and for the management of the Natura 2000 network in | ||
| 126 | Europe.\n Palabras clave: Connectivity, Corridor, Forest, | 126 | Europe.\n Palabras clave: Connectivity, Corridor, Forest, | ||
| 127 | Infrastructure planning", | 127 | Infrastructure planning", | ||
| 128 | "notes_translated": { | 128 | "notes_translated": { | ||
| 129 | "en": "The connectivity of protected areas, such as the Natura | 129 | "en": "The connectivity of protected areas, such as the Natura | ||
| 130 | 2000 network, is crucial for maintaining healthy ecosystems and for | 130 | 2000 network, is crucial for maintaining healthy ecosystems and for | ||
| 131 | the delivery of ecosystem services into the wider landscapes in which | 131 | the delivery of ecosystem services into the wider landscapes in which | ||
| 132 | they are embedded. We here present a novel combination of methods for | 132 | they are embedded. We here present a novel combination of methods for | ||
| 133 | connectivity analysis across heterogeneous landscapes, integrating | 133 | connectivity analysis across heterogeneous landscapes, integrating | ||
| 134 | graph-based analyses, least-cost path modelling and the Probability of | 134 | graph-based analyses, least-cost path modelling and the Probability of | ||
| 135 | Connectivity metric, and apply these methods to the network of Natura | 135 | Connectivity metric, and apply these methods to the network of Natura | ||
| 136 | 2000 woodland sites in mainland Spain. We deliver key insights on the | 136 | 2000 woodland sites in mainland Spain. We deliver key insights on the | ||
| 137 | connectors between Natura 2000 sites: their location and width | 137 | connectors between Natura 2000 sites: their location and width | ||
| 138 | (including transboundary ones), their prioritization in conservation | 138 | (including transboundary ones), their prioritization in conservation | ||
| 139 | and restoration scenarios involving different land uses, and the | 139 | and restoration scenarios involving different land uses, and the | ||
| 140 | bottlenecks (weak points due to land use pressures) found along them. | 140 | bottlenecks (weak points due to land use pressures) found along them. | ||
| 141 | Based on these results, we characterize the landscapes traversed by | 141 | Based on these results, we characterize the landscapes traversed by | ||
| 142 | the connectors within and outside the protected sites to inform | 142 | the connectors within and outside the protected sites to inform | ||
| 143 | related land management decisions.\n We show that forests of public | 143 | related land management decisions.\n We show that forests of public | ||
| 144 | utility play a key role in sustaining Natura 2000 connectivity in | 144 | utility play a key role in sustaining Natura 2000 connectivity in | ||
| 145 | Spain. They may qualify as an effective area-based conservation | 145 | Spain. They may qualify as an effective area-based conservation | ||
| 146 | measure significantly contributing to the connectivity element of | 146 | measure significantly contributing to the connectivity element of | ||
| 147 | Aichi Target 11. Riparian forests were part of the identified | 147 | Aichi Target 11. Riparian forests were part of the identified | ||
| 148 | connectors much more frequently than expected by their area. They | 148 | connectors much more frequently than expected by their area. They | ||
| 149 | stand out as a crucial green infrastructure safeguarding the | 149 | stand out as a crucial green infrastructure safeguarding the | ||
| 150 | connectivity of Natura 2000 woodland habitats, particularly when | 150 | connectivity of Natura 2000 woodland habitats, particularly when | ||
| 151 | forest species need to traverse landscapes dominated by agricultural | 151 | forest species need to traverse landscapes dominated by agricultural | ||
| 152 | and artificial land uses.\n Natura 2000 sites have good connectivity | 152 | and artificial land uses.\n Natura 2000 sites have good connectivity | ||
| 153 | conditions compared to unprotected lands. First, the identified | 153 | conditions compared to unprotected lands. First, the identified | ||
| 154 | woodland connectors preferentially traversed Natura 2000 lands. | 154 | woodland connectors preferentially traversed Natura 2000 lands. | ||
| 155 | Second, the large majority of bottlenecks occurred outside Natura | 155 | Second, the large majority of bottlenecks occurred outside Natura | ||
| 156 | 2000. Natura 2000 sites cannot, however, be considered free from | 156 | 2000. Natura 2000 sites cannot, however, be considered free from | ||
| 157 | connectivity limitations; they still contained a significant number of | 157 | connectivity limitations; they still contained a significant number of | ||
| 158 | bottlenecks that would need to be addressed in the site-level | 158 | bottlenecks that would need to be addressed in the site-level | ||
| 159 | management plans.\n The priority connectors for conservation were | 159 | management plans.\n The priority connectors for conservation were | ||
| 160 | preferentially found in the well-forested and well-protected | 160 | preferentially found in the well-forested and well-protected | ||
| 161 | landscapes in the main mountain ranges of Spain. On the contrary, the | 161 | landscapes in the main mountain ranges of Spain. On the contrary, the | ||
| 162 | priority connectors for restoration traversed much more frequently | 162 | priority connectors for restoration traversed much more frequently | ||
| 163 | landscapes dominated by agriculture. In these landscapes, connectivity | 163 | landscapes dominated by agriculture. In these landscapes, connectivity | ||
| 164 | improvements largely depend on the restoration of riparian forests and | 164 | improvements largely depend on the restoration of riparian forests and | ||
| 165 | on measures that mitigate the intensification of agriculture by | 165 | on measures that mitigate the intensification of agriculture by | ||
| 166 | promoting landscape complexity and natural vegetation remnants. The | 166 | promoting landscape complexity and natural vegetation remnants. The | ||
| 167 | remarkable spatial segregation found between the priority landscapes | 167 | remarkable spatial segregation found between the priority landscapes | ||
| 168 | for connectivity conservation and those of priority for restoration | 168 | for connectivity conservation and those of priority for restoration | ||
| 169 | highlights the need for an integrated perspective for land use | 169 | highlights the need for an integrated perspective for land use | ||
| 170 | planning and for the management of the Natura 2000 network in | 170 | planning and for the management of the Natura 2000 network in | ||
| 171 | Europe.\n Palabras clave: Connectivity, Corridor, Forest, | 171 | Europe.\n Palabras clave: Connectivity, Corridor, Forest, | ||
| 172 | Infrastructure planning", | 172 | Infrastructure planning", | ||
| 173 | "es": "The connectivity of protected areas, such as the Natura | 173 | "es": "The connectivity of protected areas, such as the Natura | ||
| 174 | 2000 network, is crucial for maintaining healthy ecosystems and for | 174 | 2000 network, is crucial for maintaining healthy ecosystems and for | ||
| 175 | the delivery of ecosystem services into the wider landscapes in which | 175 | the delivery of ecosystem services into the wider landscapes in which | ||
| 176 | they are embedded. We here present a novel combination of methods for | 176 | they are embedded. We here present a novel combination of methods for | ||
| 177 | connectivity analysis across heterogeneous landscapes, integrating | 177 | connectivity analysis across heterogeneous landscapes, integrating | ||
| 178 | graph-based analyses, least-cost path modelling and the Probability of | 178 | graph-based analyses, least-cost path modelling and the Probability of | ||
| 179 | Connectivity metric, and apply these methods to the network of Natura | 179 | Connectivity metric, and apply these methods to the network of Natura | ||
| 180 | 2000 woodland sites in mainland Spain. We deliver key insights on the | 180 | 2000 woodland sites in mainland Spain. We deliver key insights on the | ||
| 181 | connectors between Natura 2000 sites: their location and width | 181 | connectors between Natura 2000 sites: their location and width | ||
| 182 | (including transboundary ones), their prioritization in conservation | 182 | (including transboundary ones), their prioritization in conservation | ||
| 183 | and restoration scenarios involving different land uses, and the | 183 | and restoration scenarios involving different land uses, and the | ||
| 184 | bottlenecks (weak points due to land use pressures) found along them. | 184 | bottlenecks (weak points due to land use pressures) found along them. | ||
| 185 | Based on these results, we characterize the landscapes traversed by | 185 | Based on these results, we characterize the landscapes traversed by | ||
| 186 | the connectors within and outside the protected sites to inform | 186 | the connectors within and outside the protected sites to inform | ||
| 187 | related land management decisions.\n We show that forests of public | 187 | related land management decisions.\n We show that forests of public | ||
| 188 | utility play a key role in sustaining Natura 2000 connectivity in | 188 | utility play a key role in sustaining Natura 2000 connectivity in | ||
| 189 | Spain. They may qualify as an effective area-based conservation | 189 | Spain. They may qualify as an effective area-based conservation | ||
| 190 | measure significantly contributing to the connectivity element of | 190 | measure significantly contributing to the connectivity element of | ||
| 191 | Aichi Target 11. Riparian forests were part of the identified | 191 | Aichi Target 11. Riparian forests were part of the identified | ||
| 192 | connectors much more frequently than expected by their area. They | 192 | connectors much more frequently than expected by their area. They | ||
| 193 | stand out as a crucial green infrastructure safeguarding the | 193 | stand out as a crucial green infrastructure safeguarding the | ||
| 194 | connectivity of Natura 2000 woodland habitats, particularly when | 194 | connectivity of Natura 2000 woodland habitats, particularly when | ||
| 195 | forest species need to traverse landscapes dominated by agricultural | 195 | forest species need to traverse landscapes dominated by agricultural | ||
| 196 | and artificial land uses.\n Natura 2000 sites have good connectivity | 196 | and artificial land uses.\n Natura 2000 sites have good connectivity | ||
| 197 | conditions compared to unprotected lands. First, the identified | 197 | conditions compared to unprotected lands. First, the identified | ||
| 198 | woodland connectors preferentially traversed Natura 2000 lands. | 198 | woodland connectors preferentially traversed Natura 2000 lands. | ||
| 199 | Second, the large majority of bottlenecks occurred outside Natura | 199 | Second, the large majority of bottlenecks occurred outside Natura | ||
| 200 | 2000. Natura 2000 sites cannot, however, be considered free from | 200 | 2000. Natura 2000 sites cannot, however, be considered free from | ||
| 201 | connectivity limitations; they still contained a significant number of | 201 | connectivity limitations; they still contained a significant number of | ||
| 202 | bottlenecks that would need to be addressed in the site-level | 202 | bottlenecks that would need to be addressed in the site-level | ||
| 203 | management plans.\n The priority connectors for conservation were | 203 | management plans.\n The priority connectors for conservation were | ||
| 204 | preferentially found in the well-forested and well-protected | 204 | preferentially found in the well-forested and well-protected | ||
| 205 | landscapes in the main mountain ranges of Spain. On the contrary, the | 205 | landscapes in the main mountain ranges of Spain. On the contrary, the | ||
| 206 | priority connectors for restoration traversed much more frequently | 206 | priority connectors for restoration traversed much more frequently | ||
| 207 | landscapes dominated by agriculture. In these landscapes, connectivity | 207 | landscapes dominated by agriculture. In these landscapes, connectivity | ||
| 208 | improvements largely depend on the restoration of riparian forests and | 208 | improvements largely depend on the restoration of riparian forests and | ||
| 209 | on measures that mitigate the intensification of agriculture by | 209 | on measures that mitigate the intensification of agriculture by | ||
| 210 | promoting landscape complexity and natural vegetation remnants. The | 210 | promoting landscape complexity and natural vegetation remnants. The | ||
| 211 | remarkable spatial segregation found between the priority landscapes | 211 | remarkable spatial segregation found between the priority landscapes | ||
| 212 | for connectivity conservation and those of priority for restoration | 212 | for connectivity conservation and those of priority for restoration | ||
| 213 | highlights the need for an integrated perspective for land use | 213 | highlights the need for an integrated perspective for land use | ||
| 214 | planning and for the management of the Natura 2000 network in | 214 | planning and for the management of the Natura 2000 network in | ||
| 215 | Europe.\n Palabras clave: Connectivity, Corridor, Forest, | 215 | Europe.\n Palabras clave: Connectivity, Corridor, Forest, | ||
| 216 | Infrastructure planning" | 216 | Infrastructure planning" | ||
| 217 | }, | 217 | }, | ||
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