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En el instante 25 de junio de 2026, 12:41:53 UTC,
-
Modificado el valor del campo
modified
a2026-06-25
en Global exposure of carnivores to roads. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Global exposure of carnivores to roads.
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| 82 | "notes": "Land-use change is a major threat to biodiversity | 96 | "notes": "Land-use change is a major threat to biodiversity | ||
| 83 | globally. Roads cause direct mortality and limitation of individual | 97 | globally. Roads cause direct mortality and limitation of individual | ||
| 84 | movements, which may isolate populations and affect their viability in | 98 | movements, which may isolate populations and affect their viability in | ||
| 85 | the long term. Here we provide the first comprehensive global | 99 | the long term. Here we provide the first comprehensive global | ||
| 86 | assessment of the exposure of terrestrial mammalian carnivores to | 100 | assessment of the exposure of terrestrial mammalian carnivores to | ||
| 87 | roads using an integrated modelling framework. We estimated critical | 101 | roads using an integrated modelling framework. We estimated critical | ||
| 88 | road densities and critical patch sizes for each species based on a | 102 | road densities and critical patch sizes for each species based on a | ||
| 89 | spatially explicit model and life-history traits. We calculated the | 103 | spatially explicit model and life-history traits. We calculated the | ||
| 90 | distribution of landscape fragment sizes for each carnivore species by | 104 | distribution of landscape fragment sizes for each carnivore species by | ||
| 91 | intersecting global road density with each species range. The | 105 | intersecting global road density with each species range. The | ||
| 92 | proportion of a species\u2019 geographical range with fragments below | 106 | proportion of a species\u2019 geographical range with fragments below | ||
| 93 | the critical patch size is used as an index of the vulnerability to | 107 | the critical patch size is used as an index of the vulnerability to | ||
| 94 | roads. We found that the carnivores expected to be most exposed to | 108 | roads. We found that the carnivores expected to be most exposed to | ||
| 95 | roads belong to families Felidae, Ursidae, Mustelidae, Canidae and | 109 | roads belong to families Felidae, Ursidae, Mustelidae, Canidae and | ||
| 96 | Procyonidae. Approximately one-third of the species most affected have | 110 | Procyonidae. Approximately one-third of the species most affected have | ||
| 97 | not been identified by the IUCN as threatened by roads. Our model | 111 | not been identified by the IUCN as threatened by roads. Our model | ||
| 98 | projects time to extinction that may be as low as one century for some | 112 | projects time to extinction that may be as low as one century for some | ||
| 99 | species, such as the endangered Iberian lynx. Species are expected to | 113 | species, such as the endangered Iberian lynx. Species are expected to | ||
| 100 | be more exposed in areas with medium to high road density but, | 114 | be more exposed in areas with medium to high road density but, | ||
| 101 | surprisingly, also in areas where road density is relatively low. | 115 | surprisingly, also in areas where road density is relatively low. | ||
| 102 | Hotspots of the number of species locally endangered by roads occur in | 116 | Hotspots of the number of species locally endangered by roads occur in | ||
| 103 | North America and Asia. Our results suggest the need to reassess the | 117 | North America and Asia. Our results suggest the need to reassess the | ||
| 104 | status and threats of those species that have not been previously | 118 | status and threats of those species that have not been previously | ||
| 105 | recognized as strongly affected by roads. Our framework can be applied | 119 | recognized as strongly affected by roads. Our framework can be applied | ||
| 106 | at different spatial scales, to assess the effects of the development | 120 | at different spatial scales, to assess the effects of the development | ||
| 107 | of the road network and inform prioritization schemes for road | 121 | of the road network and inform prioritization schemes for road | ||
| 108 | building, and to identify areas for conservation, and species | 122 | building, and to identify areas for conservation, and species | ||
| 109 | requiring particular mitigation and restoration measures.", | 123 | requiring particular mitigation and restoration measures.", | ||
| 110 | "notes_translated": { | 124 | "notes_translated": { | ||
| 111 | "en": "Land-use change is a major threat to biodiversity globally. | 125 | "en": "Land-use change is a major threat to biodiversity globally. | ||
| 112 | Roads cause direct mortality and limitation of individual movements, | 126 | Roads cause direct mortality and limitation of individual movements, | ||
| 113 | which may isolate populations and affect their viability in the long | 127 | which may isolate populations and affect their viability in the long | ||
| 114 | term. Here we provide the first comprehensive global assessment of the | 128 | term. Here we provide the first comprehensive global assessment of the | ||
| 115 | exposure of terrestrial mammalian carnivores to roads using an | 129 | exposure of terrestrial mammalian carnivores to roads using an | ||
| 116 | integrated modelling framework. We estimated critical road densities | 130 | integrated modelling framework. We estimated critical road densities | ||
| 117 | and critical patch sizes for each species based on a spatially | 131 | and critical patch sizes for each species based on a spatially | ||
| 118 | explicit model and life-history traits. We calculated the distribution | 132 | explicit model and life-history traits. We calculated the distribution | ||
| 119 | of landscape fragment sizes for each carnivore species by intersecting | 133 | of landscape fragment sizes for each carnivore species by intersecting | ||
| 120 | global road density with each species range. The proportion of a | 134 | global road density with each species range. The proportion of a | ||
| 121 | species\u2019 geographical range with fragments below the critical | 135 | species\u2019 geographical range with fragments below the critical | ||
| 122 | patch size is used as an index of the vulnerability to roads. We found | 136 | patch size is used as an index of the vulnerability to roads. We found | ||
| 123 | that the carnivores expected to be most exposed to roads belong to | 137 | that the carnivores expected to be most exposed to roads belong to | ||
| 124 | families Felidae, Ursidae, Mustelidae, Canidae and Procyonidae. | 138 | families Felidae, Ursidae, Mustelidae, Canidae and Procyonidae. | ||
| 125 | Approximately one-third of the species most affected have not been | 139 | Approximately one-third of the species most affected have not been | ||
| 126 | identified by the IUCN as threatened by roads. Our model projects time | 140 | identified by the IUCN as threatened by roads. Our model projects time | ||
| 127 | to extinction that may be as low as one century for some species, such | 141 | to extinction that may be as low as one century for some species, such | ||
| 128 | as the endangered Iberian lynx. Species are expected to be more | 142 | as the endangered Iberian lynx. Species are expected to be more | ||
| 129 | exposed in areas with medium to high road density but, surprisingly, | 143 | exposed in areas with medium to high road density but, surprisingly, | ||
| 130 | also in areas where road density is relatively low. Hotspots of the | 144 | also in areas where road density is relatively low. Hotspots of the | ||
| 131 | number of species locally endangered by roads occur in North America | 145 | number of species locally endangered by roads occur in North America | ||
| 132 | and Asia. Our results suggest the need to reassess the status and | 146 | and Asia. Our results suggest the need to reassess the status and | ||
| 133 | threats of those species that have not been previously recognized as | 147 | threats of those species that have not been previously recognized as | ||
| 134 | strongly affected by roads. Our framework can be applied at different | 148 | strongly affected by roads. Our framework can be applied at different | ||
| 135 | spatial scales, to assess the effects of the development of the road | 149 | spatial scales, to assess the effects of the development of the road | ||
| 136 | network and inform prioritization schemes for road building, and to | 150 | network and inform prioritization schemes for road building, and to | ||
| 137 | identify areas for conservation, and species requiring particular | 151 | identify areas for conservation, and species requiring particular | ||
| 138 | mitigation and restoration measures.", | 152 | mitigation and restoration measures.", | ||
| 139 | "es": "Land-use change is a major threat to biodiversity globally. | 153 | "es": "Land-use change is a major threat to biodiversity globally. | ||
| 140 | Roads cause direct mortality and limitation of individual movements, | 154 | Roads cause direct mortality and limitation of individual movements, | ||
| 141 | which may isolate populations and affect their viability in the long | 155 | which may isolate populations and affect their viability in the long | ||
| 142 | term. Here we provide the first comprehensive global assessment of the | 156 | term. Here we provide the first comprehensive global assessment of the | ||
| 143 | exposure of terrestrial mammalian carnivores to roads using an | 157 | exposure of terrestrial mammalian carnivores to roads using an | ||
| 144 | integrated modelling framework. We estimated critical road densities | 158 | integrated modelling framework. We estimated critical road densities | ||
| 145 | and critical patch sizes for each species based on a spatially | 159 | and critical patch sizes for each species based on a spatially | ||
| 146 | explicit model and life-history traits. We calculated the distribution | 160 | explicit model and life-history traits. We calculated the distribution | ||
| 147 | of landscape fragment sizes for each carnivore species by intersecting | 161 | of landscape fragment sizes for each carnivore species by intersecting | ||
| 148 | global road density with each species range. The proportion of a | 162 | global road density with each species range. The proportion of a | ||
| 149 | species\u2019 geographical range with fragments below the critical | 163 | species\u2019 geographical range with fragments below the critical | ||
| 150 | patch size is used as an index of the vulnerability to roads. We found | 164 | patch size is used as an index of the vulnerability to roads. We found | ||
| 151 | that the carnivores expected to be most exposed to roads belong to | 165 | that the carnivores expected to be most exposed to roads belong to | ||
| 152 | families Felidae, Ursidae, Mustelidae, Canidae and Procyonidae. | 166 | families Felidae, Ursidae, Mustelidae, Canidae and Procyonidae. | ||
| 153 | Approximately one-third of the species most affected have not been | 167 | Approximately one-third of the species most affected have not been | ||
| 154 | identified by the IUCN as threatened by roads. Our model projects time | 168 | identified by the IUCN as threatened by roads. Our model projects time | ||
| 155 | to extinction that may be as low as one century for some species, such | 169 | to extinction that may be as low as one century for some species, such | ||
| 156 | as the endangered Iberian lynx. Species are expected to be more | 170 | as the endangered Iberian lynx. Species are expected to be more | ||
| 157 | exposed in areas with medium to high road density but, surprisingly, | 171 | exposed in areas with medium to high road density but, surprisingly, | ||
| 158 | also in areas where road density is relatively low. Hotspots of the | 172 | also in areas where road density is relatively low. Hotspots of the | ||
| 159 | number of species locally endangered by roads occur in North America | 173 | number of species locally endangered by roads occur in North America | ||
| 160 | and Asia. Our results suggest the need to reassess the status and | 174 | and Asia. Our results suggest the need to reassess the status and | ||
| 161 | threats of those species that have not been previously recognized as | 175 | threats of those species that have not been previously recognized as | ||
| 162 | strongly affected by roads. Our framework can be applied at different | 176 | strongly affected by roads. Our framework can be applied at different | ||
| 163 | spatial scales, to assess the effects of the development of the road | 177 | spatial scales, to assess the effects of the development of the road | ||
| 164 | network and inform prioritization schemes for road building, and to | 178 | network and inform prioritization schemes for road building, and to | ||
| 165 | identify areas for conservation, and species requiring particular | 179 | identify areas for conservation, and species requiring particular | ||
| 166 | mitigation and restoration measures." | 180 | mitigation and restoration measures." | ||
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