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En el instante 25 de junio de 2026, 12:34:05 UTC,
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Modificado el valor del campo
modified
a2026-06-25
en Landscape structure and asymmetrical inter-patch connectivity in a metapopulation of the endangered iberian lynx. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Landscape structure and asymmetrical inter-patch connectivity in a metapopulation of the endangered iberian lynx.
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| 78 | "name": "8ad55e58-86ef-523a-a732-a6af7316ad61", | 92 | "name": "8ad55e58-86ef-523a-a732-a6af7316ad61", | ||
| 79 | "notes": "Among the factors threatening the Iberian lynx, (Lynx | 93 | "notes": "Among the factors threatening the Iberian lynx, (Lynx | ||
| 80 | pardinus) (the most endangered species of all the Felidae), loss and | 94 | pardinus) (the most endangered species of all the Felidae), loss and | ||
| 81 | fragmentation of its habitats are probably the most important. | 95 | fragmentation of its habitats are probably the most important. | ||
| 82 | Connectivity between the remaining populations in the predominantly | 96 | Connectivity between the remaining populations in the predominantly | ||
| 83 | fragmented landscapes is a key factor in the dynamics and persistence | 97 | fragmented landscapes is a key factor in the dynamics and persistence | ||
| 84 | of metapopulations. Based on the data collected during a long-term | 98 | of metapopulations. Based on the data collected during a long-term | ||
| 85 | study on the ecology of this species in a small and fragmented | 99 | study on the ecology of this species in a small and fragmented | ||
| 86 | population in SW Spain, I analyse the factors affecting connectivity | 100 | population in SW Spain, I analyse the factors affecting connectivity | ||
| 87 | between the two main sources and the rest of local populations. | 101 | between the two main sources and the rest of local populations. | ||
| 88 | Connectivity was estimated as the proportion of dispersers from a | 102 | Connectivity was estimated as the proportion of dispersers from a | ||
| 89 | source that reached a given subpopulation. Among the explanatory | 103 | source that reached a given subpopulation. Among the explanatory | ||
| 90 | variables considered, only distance (both straight and effective | 104 | variables considered, only distance (both straight and effective | ||
| 91 | distance, which takes into account habitat quality between local | 105 | distance, which takes into account habitat quality between local | ||
| 92 | populations) and location of the source were clearly related to | 106 | populations) and location of the source were clearly related to | ||
| 93 | connectivity. Some other variables describing landscape features | 107 | connectivity. Some other variables describing landscape features | ||
| 94 | separating sources and target subpopulations (proportion of unsuitable | 108 | separating sources and target subpopulations (proportion of unsuitable | ||
| 95 | habitats, patch cohesion, size of targets, overall size of | 109 | habitats, patch cohesion, size of targets, overall size of | ||
| 96 | subpopulations closer than the target) were not related to | 110 | subpopulations closer than the target) were not related to | ||
| 97 | connectivity. Differences in the landscape surrounding sources help to | 111 | connectivity. Differences in the landscape surrounding sources help to | ||
| 98 | explain the different connectivity from the two sources. An | 112 | explain the different connectivity from the two sources. An | ||
| 99 | asymmetrical connectivity between the two sources and populations | 113 | asymmetrical connectivity between the two sources and populations | ||
| 100 | surrounding them (north and south) is likely explained by the | 114 | surrounding them (north and south) is likely explained by the | ||
| 101 | configuration of habitats encountered by dispersers, which force those | 115 | configuration of habitats encountered by dispersers, which force those | ||
| 102 | from one source to behave as crossers of unsuitable habitats. These | 116 | from one source to behave as crossers of unsuitable habitats. These | ||
| 103 | results have consequences for the conservation of Iberian lynx | 117 | results have consequences for the conservation of Iberian lynx | ||
| 104 | populations and for ecologically similar species. Distance, the factor | 118 | populations and for ecologically similar species. Distance, the factor | ||
| 105 | most affecting connectivity, is difficult to manage, although at least | 119 | most affecting connectivity, is difficult to manage, although at least | ||
| 106 | size and configuration of usable patches can be modified. Connectivity | 120 | size and configuration of usable patches can be modified. Connectivity | ||
| 107 | could also be improved through recovery of habitats with cover, | 121 | could also be improved through recovery of habitats with cover, | ||
| 108 | suitable for dispersing. Reduction of mortality risks would also | 122 | suitable for dispersing. Reduction of mortality risks would also | ||
| 109 | enhance connectivity indirectly, by allowing longer times and larger | 123 | enhance connectivity indirectly, by allowing longer times and larger | ||
| 110 | areas covered during dispersal. In the case of the study population, | 124 | areas covered during dispersal. In the case of the study population, | ||
| 111 | it is urgent to promote connectivity with other Iberian lynx | 125 | it is urgent to promote connectivity with other Iberian lynx | ||
| 112 | populations due to genetic consequences of small population size and | 126 | populations due to genetic consequences of small population size and | ||
| 113 | effective isolation.\n Palabras clave: Connectivity, Habitat | 127 | effective isolation.\n Palabras clave: Connectivity, Habitat | ||
| 114 | fragmentation, Habitat loss, Lynx, Metapopulation", | 128 | fragmentation, Habitat loss, Lynx, Metapopulation", | ||
| 115 | "notes_translated": { | 129 | "notes_translated": { | ||
| 116 | "en": "Among the factors threatening the Iberian lynx, (Lynx | 130 | "en": "Among the factors threatening the Iberian lynx, (Lynx | ||
| 117 | pardinus) (the most endangered species of all the Felidae), loss and | 131 | pardinus) (the most endangered species of all the Felidae), loss and | ||
| 118 | fragmentation of its habitats are probably the most important. | 132 | fragmentation of its habitats are probably the most important. | ||
| 119 | Connectivity between the remaining populations in the predominantly | 133 | Connectivity between the remaining populations in the predominantly | ||
| 120 | fragmented landscapes is a key factor in the dynamics and persistence | 134 | fragmented landscapes is a key factor in the dynamics and persistence | ||
| 121 | of metapopulations. Based on the data collected during a long-term | 135 | of metapopulations. Based on the data collected during a long-term | ||
| 122 | study on the ecology of this species in a small and fragmented | 136 | study on the ecology of this species in a small and fragmented | ||
| 123 | population in SW Spain, I analyse the factors affecting connectivity | 137 | population in SW Spain, I analyse the factors affecting connectivity | ||
| 124 | between the two main sources and the rest of local populations. | 138 | between the two main sources and the rest of local populations. | ||
| 125 | Connectivity was estimated as the proportion of dispersers from a | 139 | Connectivity was estimated as the proportion of dispersers from a | ||
| 126 | source that reached a given subpopulation. Among the explanatory | 140 | source that reached a given subpopulation. Among the explanatory | ||
| 127 | variables considered, only distance (both straight and effective | 141 | variables considered, only distance (both straight and effective | ||
| 128 | distance, which takes into account habitat quality between local | 142 | distance, which takes into account habitat quality between local | ||
| 129 | populations) and location of the source were clearly related to | 143 | populations) and location of the source were clearly related to | ||
| 130 | connectivity. Some other variables describing landscape features | 144 | connectivity. Some other variables describing landscape features | ||
| 131 | separating sources and target subpopulations (proportion of unsuitable | 145 | separating sources and target subpopulations (proportion of unsuitable | ||
| 132 | habitats, patch cohesion, size of targets, overall size of | 146 | habitats, patch cohesion, size of targets, overall size of | ||
| 133 | subpopulations closer than the target) were not related to | 147 | subpopulations closer than the target) were not related to | ||
| 134 | connectivity. Differences in the landscape surrounding sources help to | 148 | connectivity. Differences in the landscape surrounding sources help to | ||
| 135 | explain the different connectivity from the two sources. An | 149 | explain the different connectivity from the two sources. An | ||
| 136 | asymmetrical connectivity between the two sources and populations | 150 | asymmetrical connectivity between the two sources and populations | ||
| 137 | surrounding them (north and south) is likely explained by the | 151 | surrounding them (north and south) is likely explained by the | ||
| 138 | configuration of habitats encountered by dispersers, which force those | 152 | configuration of habitats encountered by dispersers, which force those | ||
| 139 | from one source to behave as crossers of unsuitable habitats. These | 153 | from one source to behave as crossers of unsuitable habitats. These | ||
| 140 | results have consequences for the conservation of Iberian lynx | 154 | results have consequences for the conservation of Iberian lynx | ||
| 141 | populations and for ecologically similar species. Distance, the factor | 155 | populations and for ecologically similar species. Distance, the factor | ||
| 142 | most affecting connectivity, is difficult to manage, although at least | 156 | most affecting connectivity, is difficult to manage, although at least | ||
| 143 | size and configuration of usable patches can be modified. Connectivity | 157 | size and configuration of usable patches can be modified. Connectivity | ||
| 144 | could also be improved through recovery of habitats with cover, | 158 | could also be improved through recovery of habitats with cover, | ||
| 145 | suitable for dispersing. Reduction of mortality risks would also | 159 | suitable for dispersing. Reduction of mortality risks would also | ||
| 146 | enhance connectivity indirectly, by allowing longer times and larger | 160 | enhance connectivity indirectly, by allowing longer times and larger | ||
| 147 | areas covered during dispersal. In the case of the study population, | 161 | areas covered during dispersal. In the case of the study population, | ||
| 148 | it is urgent to promote connectivity with other Iberian lynx | 162 | it is urgent to promote connectivity with other Iberian lynx | ||
| 149 | populations due to genetic consequences of small population size and | 163 | populations due to genetic consequences of small population size and | ||
| 150 | effective isolation.", | 164 | effective isolation.", | ||
| 151 | "es": "Among the factors threatening the Iberian lynx, (Lynx | 165 | "es": "Among the factors threatening the Iberian lynx, (Lynx | ||
| 152 | pardinus) (the most endangered species of all the Felidae), loss and | 166 | pardinus) (the most endangered species of all the Felidae), loss and | ||
| 153 | fragmentation of its habitats are probably the most important. | 167 | fragmentation of its habitats are probably the most important. | ||
| 154 | Connectivity between the remaining populations in the predominantly | 168 | Connectivity between the remaining populations in the predominantly | ||
| 155 | fragmented landscapes is a key factor in the dynamics and persistence | 169 | fragmented landscapes is a key factor in the dynamics and persistence | ||
| 156 | of metapopulations. Based on the data collected during a long-term | 170 | of metapopulations. Based on the data collected during a long-term | ||
| 157 | study on the ecology of this species in a small and fragmented | 171 | study on the ecology of this species in a small and fragmented | ||
| 158 | population in SW Spain, I analyse the factors affecting connectivity | 172 | population in SW Spain, I analyse the factors affecting connectivity | ||
| 159 | between the two main sources and the rest of local populations. | 173 | between the two main sources and the rest of local populations. | ||
| 160 | Connectivity was estimated as the proportion of dispersers from a | 174 | Connectivity was estimated as the proportion of dispersers from a | ||
| 161 | source that reached a given subpopulation. Among the explanatory | 175 | source that reached a given subpopulation. Among the explanatory | ||
| 162 | variables considered, only distance (both straight and effective | 176 | variables considered, only distance (both straight and effective | ||
| 163 | distance, which takes into account habitat quality between local | 177 | distance, which takes into account habitat quality between local | ||
| 164 | populations) and location of the source were clearly related to | 178 | populations) and location of the source were clearly related to | ||
| 165 | connectivity. Some other variables describing landscape features | 179 | connectivity. Some other variables describing landscape features | ||
| 166 | separating sources and target subpopulations (proportion of unsuitable | 180 | separating sources and target subpopulations (proportion of unsuitable | ||
| 167 | habitats, patch cohesion, size of targets, overall size of | 181 | habitats, patch cohesion, size of targets, overall size of | ||
| 168 | subpopulations closer than the target) were not related to | 182 | subpopulations closer than the target) were not related to | ||
| 169 | connectivity. Differences in the landscape surrounding sources help to | 183 | connectivity. Differences in the landscape surrounding sources help to | ||
| 170 | explain the different connectivity from the two sources. An | 184 | explain the different connectivity from the two sources. An | ||
| 171 | asymmetrical connectivity between the two sources and populations | 185 | asymmetrical connectivity between the two sources and populations | ||
| 172 | surrounding them (north and south) is likely explained by the | 186 | surrounding them (north and south) is likely explained by the | ||
| 173 | configuration of habitats encountered by dispersers, which force those | 187 | configuration of habitats encountered by dispersers, which force those | ||
| 174 | from one source to behave as crossers of unsuitable habitats. These | 188 | from one source to behave as crossers of unsuitable habitats. These | ||
| 175 | results have consequences for the conservation of Iberian lynx | 189 | results have consequences for the conservation of Iberian lynx | ||
| 176 | populations and for ecologically similar species. Distance, the factor | 190 | populations and for ecologically similar species. Distance, the factor | ||
| 177 | most affecting connectivity, is difficult to manage, although at least | 191 | most affecting connectivity, is difficult to manage, although at least | ||
| 178 | size and configuration of usable patches can be modified. Connectivity | 192 | size and configuration of usable patches can be modified. Connectivity | ||
| 179 | could also be improved through recovery of habitats with cover, | 193 | could also be improved through recovery of habitats with cover, | ||
| 180 | suitable for dispersing. Reduction of mortality risks would also | 194 | suitable for dispersing. Reduction of mortality risks would also | ||
| 181 | enhance connectivity indirectly, by allowing longer times and larger | 195 | enhance connectivity indirectly, by allowing longer times and larger | ||
| 182 | areas covered during dispersal. In the case of the study population, | 196 | areas covered during dispersal. In the case of the study population, | ||
| 183 | it is urgent to promote connectivity with other Iberian lynx | 197 | it is urgent to promote connectivity with other Iberian lynx | ||
| 184 | populations due to genetic consequences of small population size and | 198 | populations due to genetic consequences of small population size and | ||
| 185 | effective isolation.\n Palabras clave: Connectivity, Habitat | 199 | effective isolation.\n Palabras clave: Connectivity, Habitat | ||
| 186 | fragmentation, Habitat loss, Lynx, Metapopulation" | 200 | fragmentation, Habitat loss, Lynx, Metapopulation" | ||
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