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En el instante 23 de junio de 2026, 16:07:04 UTC,
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Modificado el valor del campo
spatial_coverage
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en Risks and opportunities for wildlife living in road dominated environments. What pieces are missing to complete the puzzle?
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| 82 | "notes": "A living on the roadside involves serious risks including | 82 | "notes": "A living on the roadside involves serious risks including | ||
| 83 | restrictions to movements, disturbance of resting and feeding places, | 83 | restrictions to movements, disturbance of resting and feeding places, | ||
| 84 | and roadkill menace. However, when crossing highly human modified | 84 | and roadkill menace. However, when crossing highly human modified | ||
| 85 | areas such as simplified intensive agricultural landscapes or highly | 85 | areas such as simplified intensive agricultural landscapes or highly | ||
| 86 | grazed areas, remnant natural habitats associated to roads (verges, | 86 | grazed areas, remnant natural habitats associated to roads (verges, | ||
| 87 | roundabouts, bypasses, etc.) may be the only leftover natural areas | 87 | roundabouts, bypasses, etc.) may be the only leftover natural areas | ||
| 88 | acting as a last refuge for rare plants and small fauna. In these | 88 | acting as a last refuge for rare plants and small fauna. In these | ||
| 89 | circumstances, there may be a positive contribution of roads and | 89 | circumstances, there may be a positive contribution of roads and | ||
| 90 | associated vegetated areas for biodiversity conservation may be | 90 | associated vegetated areas for biodiversity conservation may be | ||
| 91 | considered. In Europe, remnants of natural habits on roadsidesmay be | 91 | considered. In Europe, remnants of natural habits on roadsidesmay be | ||
| 92 | particularly relevant for the implementation of the \u201cEuropean | 92 | particularly relevant for the implementation of the \u201cEuropean | ||
| 93 | Green Infrastructure\u201d (EGI) , defined as \u201c\u2026 an | 93 | Green Infrastructure\u201d (EGI) , defined as \u201c\u2026 an | ||
| 94 | interconnected network of green spaces in urban and infrastructure | 94 | interconnected network of green spaces in urban and infrastructure | ||
| 95 | dominated environments that preserves the natural value and functions | 95 | dominated environments that preserves the natural value and functions | ||
| 96 | of the ecosystems and provide humans with the benefits associated with | 96 | of the ecosystems and provide humans with the benefits associated with | ||
| 97 | them\u201d.However, to enhancethe role of road vegetated marginal | 97 | them\u201d.However, to enhancethe role of road vegetated marginal | ||
| 98 | areas in the EGI there is still a long way to go and many fundamental | 98 | areas in the EGI there is still a long way to go and many fundamental | ||
| 99 | questions need to be more deeply addressed:i) are road verges refuges | 99 | questions need to be more deeply addressed:i) are road verges refuges | ||
| 100 | or ecological traps for fauna?; (ii) what species traits makes them | 100 | or ecological traps for fauna?; (ii) what species traits makes them | ||
| 101 | more suited to persist in road natural habitats remnants?; (iii) what | 101 | more suited to persist in road natural habitats remnants?; (iii) what | ||
| 102 | is the relevance of verges as corridors?; (v) what surrounding | 102 | is the relevance of verges as corridors?; (v) what surrounding | ||
| 103 | landscape features are key to define the ecological role of road | 103 | landscape features are key to define the ecological role of road | ||
| 104 | natural habitats remnants? What are the effects of roads on | 104 | natural habitats remnants? What are the effects of roads on | ||
| 105 | demographicparameters of populations living on the roadside? We have | 105 | demographicparameters of populations living on the roadside? We have | ||
| 106 | accessed the role of verges as providing foraging opportunities for | 106 | accessed the role of verges as providing foraging opportunities for | ||
| 107 | bats, refuges and corridors for small mammals, and ecological traps | 107 | bats, refuges and corridors for small mammals, and ecological traps | ||
| 108 | for small mammal predators. We found that when roads cross lower | 108 | for small mammal predators. We found that when roads cross lower | ||
| 109 | suitable habitat, roads verges canbe an important last remnant feeding | 109 | suitable habitat, roads verges canbe an important last remnant feeding | ||
| 110 | habitat for bats.In highly grazed areas we have shown that verges are | 110 | habitat for bats.In highly grazed areas we have shown that verges are | ||
| 111 | a critical refuge for small mammals, as important as riparian | 111 | a critical refuge for small mammals, as important as riparian | ||
| 112 | galleries, considered one of the most relevant habitats for fauna in | 112 | galleries, considered one of the most relevant habitats for fauna in | ||
| 113 | the Mediterranean landscape. Using graph-theory-based connectivity | 113 | the Mediterranean landscape. Using graph-theory-based connectivity | ||
| 114 | metrics we demonstrated that verges contributed significantly more to | 114 | metrics we demonstrated that verges contributed significantly more to | ||
| 115 | the overall landscape connectivity than surrounding areas. This shows | 115 | the overall landscape connectivity than surrounding areas. This shows | ||
| 116 | the high importance of verges as small mammal corridors, even in well | 116 | the high importance of verges as small mammal corridors, even in well | ||
| 117 | preserved landscapes. We also show a strong positive association | 117 | preserved landscapes. We also show a strong positive association | ||
| 118 | between locations of snakes, owls and mammal carnivores road | 118 | between locations of snakes, owls and mammal carnivores road | ||
| 119 | casualties and the abundance on verges of wood mice and rabbits, the | 119 | casualties and the abundance on verges of wood mice and rabbits, the | ||
| 120 | two main prey in the studied area. These results support the | 120 | two main prey in the studied area. These results support the | ||
| 121 | hypothesis that prey abundance on road verges may be a major driver | 121 | hypothesis that prey abundance on road verges may be a major driver | ||
| 122 | explaining predator roadkills. In Portugal, road verges and other road | 122 | explaining predator roadkills. In Portugal, road verges and other road | ||
| 123 | remnants of natural habitats are estimated to cover more than 140 | 123 | remnants of natural habitats are estimated to cover more than 140 | ||
| 124 | thousand hectares, an area larger than any terrestrial protected area | 124 | thousand hectares, an area larger than any terrestrial protected area | ||
| 125 | in the country. Similar or larger areas of remnant habitats along | 125 | in the country. Similar or larger areas of remnant habitats along | ||
| 126 | roads occur in many other countries. Thus, gathering further knowledge | 126 | roads occur in many other countries. Thus, gathering further knowledge | ||
| 127 | aiming to quantify and identify their role in biodiversity | 127 | aiming to quantify and identify their role in biodiversity | ||
| 128 | conservation is key to properly offset road impacts on wildlife.", | 128 | conservation is key to properly offset road impacts on wildlife.", | ||
| 129 | "notes_translated": { | 129 | "notes_translated": { | ||
| 130 | "en": "A Living on the roadside involves serious risks including | 130 | "en": "A Living on the roadside involves serious risks including | ||
| 131 | restrictions to movements, disturbance of resting and feeding places, | 131 | restrictions to movements, disturbance of resting and feeding places, | ||
| 132 | and roadkill menace. However, when crossing highly human modified | 132 | and roadkill menace. However, when crossing highly human modified | ||
| 133 | areas such as simplified intensive agricultural landscapes or highly | 133 | areas such as simplified intensive agricultural landscapes or highly | ||
| 134 | grazed areas, remnant natural habitats associated to roads (verges, | 134 | grazed areas, remnant natural habitats associated to roads (verges, | ||
| 135 | roundabouts, bypasses, etc.) may be the only leftover natural areas | 135 | roundabouts, bypasses, etc.) may be the only leftover natural areas | ||
| 136 | acting as a last refuge for rare plants and small fauna. In these | 136 | acting as a last refuge for rare plants and small fauna. In these | ||
| 137 | circumstances, there may be a positive contribution of roads and | 137 | circumstances, there may be a positive contribution of roads and | ||
| 138 | associated vegetated areas for biodiversity conservation may be | 138 | associated vegetated areas for biodiversity conservation may be | ||
| 139 | considered. In Europe, remnants of natural habits on roadsidesmay be | 139 | considered. In Europe, remnants of natural habits on roadsidesmay be | ||
| 140 | particularly relevant for the implementation of the \u201cEuropean | 140 | particularly relevant for the implementation of the \u201cEuropean | ||
| 141 | Green Infrastructure\u201d (EGI) , defined as \u201c\u2026 an | 141 | Green Infrastructure\u201d (EGI) , defined as \u201c\u2026 an | ||
| 142 | interconnected network of green spaces in urban and infrastructure | 142 | interconnected network of green spaces in urban and infrastructure | ||
| 143 | dominated environments that preserves the natural value and functions | 143 | dominated environments that preserves the natural value and functions | ||
| 144 | of the ecosystems and provide humans with the benefits associated with | 144 | of the ecosystems and provide humans with the benefits associated with | ||
| 145 | them\u201d.However, to enhancethe role of road vegetated marginal | 145 | them\u201d.However, to enhancethe role of road vegetated marginal | ||
| 146 | areas in the EGI there is still a long way to go and many fundamental | 146 | areas in the EGI there is still a long way to go and many fundamental | ||
| 147 | questions need to be more deeply addressed:i) are road verges refuges | 147 | questions need to be more deeply addressed:i) are road verges refuges | ||
| 148 | or ecological traps for fauna?; (ii) what species traits makes them | 148 | or ecological traps for fauna?; (ii) what species traits makes them | ||
| 149 | more suited to persist in road natural habitats remnants?; (iii) what | 149 | more suited to persist in road natural habitats remnants?; (iii) what | ||
| 150 | is the relevance of verges as corridors?; (v) what surrounding | 150 | is the relevance of verges as corridors?; (v) what surrounding | ||
| 151 | landscape features are key to define the ecological role of road | 151 | landscape features are key to define the ecological role of road | ||
| 152 | natural habitats remnants? What are the effects of roads on | 152 | natural habitats remnants? What are the effects of roads on | ||
| 153 | demographicparameters of populations living on the roadside? We have | 153 | demographicparameters of populations living on the roadside? We have | ||
| 154 | accessed the role of verges as providing foraging opportunities for | 154 | accessed the role of verges as providing foraging opportunities for | ||
| 155 | bats, refuges and corridors for small mammals, and ecological traps | 155 | bats, refuges and corridors for small mammals, and ecological traps | ||
| 156 | for small mammal predators. We found that when roads cross lower | 156 | for small mammal predators. We found that when roads cross lower | ||
| 157 | suitable habitat, roads verges canbe an important last remnant feeding | 157 | suitable habitat, roads verges canbe an important last remnant feeding | ||
| 158 | habitat for bats.In highly grazed areas we have shown that verges are | 158 | habitat for bats.In highly grazed areas we have shown that verges are | ||
| 159 | a critical refuge for small mammals, as important as riparian | 159 | a critical refuge for small mammals, as important as riparian | ||
| 160 | galleries, considered one of the most relevant habitats for fauna in | 160 | galleries, considered one of the most relevant habitats for fauna in | ||
| 161 | the Mediterranean landscape. Using graph-theory-based connectivity | 161 | the Mediterranean landscape. Using graph-theory-based connectivity | ||
| 162 | metrics we demonstrated that verges contributed significantly more to | 162 | metrics we demonstrated that verges contributed significantly more to | ||
| 163 | the overall landscape connectivity than surrounding areas. This shows | 163 | the overall landscape connectivity than surrounding areas. This shows | ||
| 164 | the high importance of verges as small mammal corridors, even in well | 164 | the high importance of verges as small mammal corridors, even in well | ||
| 165 | preserved landscapes. We also show a strong positive association | 165 | preserved landscapes. We also show a strong positive association | ||
| 166 | between locations of snakes, owls and mammal carnivores road | 166 | between locations of snakes, owls and mammal carnivores road | ||
| 167 | casualties and the abundance on verges of wood mice and rabbits, the | 167 | casualties and the abundance on verges of wood mice and rabbits, the | ||
| 168 | two main prey in the studied area. These results support the | 168 | two main prey in the studied area. These results support the | ||
| 169 | hypothesis that prey abundance on road verges may be a major driver | 169 | hypothesis that prey abundance on road verges may be a major driver | ||
| 170 | explaining\npredator roadkills. In Portugal, road verges and other | 170 | explaining\npredator roadkills. In Portugal, road verges and other | ||
| 171 | road remnants of natural habitats are estimated to cover more than 140 | 171 | road remnants of natural habitats are estimated to cover more than 140 | ||
| 172 | thousand hectares, an area larger than any terrestrial protected area | 172 | thousand hectares, an area larger than any terrestrial protected area | ||
| 173 | in the country. Similar or larger areas of remnant habitats along | 173 | in the country. Similar or larger areas of remnant habitats along | ||
| 174 | roads occur in many other countries. Thus, gathering further knowledge | 174 | roads occur in many other countries. Thus, gathering further knowledge | ||
| 175 | aiming to quantify and identify their role in biodiversity | 175 | aiming to quantify and identify their role in biodiversity | ||
| 176 | conservation is key to properly offset road impacts on wildlife.", | 176 | conservation is key to properly offset road impacts on wildlife.", | ||
| 177 | "es": "A living on the roadside involves serious risks including | 177 | "es": "A living on the roadside involves serious risks including | ||
| 178 | restrictions to movements, disturbance of resting and feeding places, | 178 | restrictions to movements, disturbance of resting and feeding places, | ||
| 179 | and roadkill menace. However, when crossing highly human modified | 179 | and roadkill menace. However, when crossing highly human modified | ||
| 180 | areas such as simplified intensive agricultural landscapes or highly | 180 | areas such as simplified intensive agricultural landscapes or highly | ||
| 181 | grazed areas, remnant natural habitats associated to roads (verges, | 181 | grazed areas, remnant natural habitats associated to roads (verges, | ||
| 182 | roundabouts, bypasses, etc.) may be the only leftover natural areas | 182 | roundabouts, bypasses, etc.) may be the only leftover natural areas | ||
| 183 | acting as a last refuge for rare plants and small fauna. In these | 183 | acting as a last refuge for rare plants and small fauna. In these | ||
| 184 | circumstances, there may be a positive contribution of roads and | 184 | circumstances, there may be a positive contribution of roads and | ||
| 185 | associated vegetated areas for biodiversity conservation may be | 185 | associated vegetated areas for biodiversity conservation may be | ||
| 186 | considered. In Europe, remnants of natural habits on roadsidesmay be | 186 | considered. In Europe, remnants of natural habits on roadsidesmay be | ||
| 187 | particularly relevant for the implementation of the \u201cEuropean | 187 | particularly relevant for the implementation of the \u201cEuropean | ||
| 188 | Green Infrastructure\u201d (EGI) , defined as \u201c\u2026 an | 188 | Green Infrastructure\u201d (EGI) , defined as \u201c\u2026 an | ||
| 189 | interconnected network of green spaces in urban and infrastructure | 189 | interconnected network of green spaces in urban and infrastructure | ||
| 190 | dominated environments that preserves the natural value and functions | 190 | dominated environments that preserves the natural value and functions | ||
| 191 | of the ecosystems and provide humans with the benefits associated with | 191 | of the ecosystems and provide humans with the benefits associated with | ||
| 192 | them\u201d.However, to enhancethe role of road vegetated marginal | 192 | them\u201d.However, to enhancethe role of road vegetated marginal | ||
| 193 | areas in the EGI there is still a long way to go and many fundamental | 193 | areas in the EGI there is still a long way to go and many fundamental | ||
| 194 | questions need to be more deeply addressed:i) are road verges refuges | 194 | questions need to be more deeply addressed:i) are road verges refuges | ||
| 195 | or ecological traps for fauna?; (ii) what species traits makes them | 195 | or ecological traps for fauna?; (ii) what species traits makes them | ||
| 196 | more suited to persist in road natural habitats remnants?; (iii) what | 196 | more suited to persist in road natural habitats remnants?; (iii) what | ||
| 197 | is the relevance of verges as corridors?; (v) what surrounding | 197 | is the relevance of verges as corridors?; (v) what surrounding | ||
| 198 | landscape features are key to define the ecological role of road | 198 | landscape features are key to define the ecological role of road | ||
| 199 | natural habitats remnants? What are the effects of roads on | 199 | natural habitats remnants? What are the effects of roads on | ||
| 200 | demographicparameters of populations living on the roadside? We have | 200 | demographicparameters of populations living on the roadside? We have | ||
| 201 | accessed the role of verges as providing foraging opportunities for | 201 | accessed the role of verges as providing foraging opportunities for | ||
| 202 | bats, refuges and corridors for small mammals, and ecological traps | 202 | bats, refuges and corridors for small mammals, and ecological traps | ||
| 203 | for small mammal predators. We found that when roads cross lower | 203 | for small mammal predators. We found that when roads cross lower | ||
| 204 | suitable habitat, roads verges canbe an important last remnant feeding | 204 | suitable habitat, roads verges canbe an important last remnant feeding | ||
| 205 | habitat for bats.In highly grazed areas we have shown that verges are | 205 | habitat for bats.In highly grazed areas we have shown that verges are | ||
| 206 | a critical refuge for small mammals, as important as riparian | 206 | a critical refuge for small mammals, as important as riparian | ||
| 207 | galleries, considered one of the most relevant habitats for fauna in | 207 | galleries, considered one of the most relevant habitats for fauna in | ||
| 208 | the Mediterranean landscape. Using graph-theory-based connectivity | 208 | the Mediterranean landscape. Using graph-theory-based connectivity | ||
| 209 | metrics we demonstrated that verges contributed significantly more to | 209 | metrics we demonstrated that verges contributed significantly more to | ||
| 210 | the overall landscape connectivity than surrounding areas. This shows | 210 | the overall landscape connectivity than surrounding areas. This shows | ||
| 211 | the high importance of verges as small mammal corridors, even in well | 211 | the high importance of verges as small mammal corridors, even in well | ||
| 212 | preserved landscapes. We also show a strong positive association | 212 | preserved landscapes. We also show a strong positive association | ||
| 213 | between locations of snakes, owls and mammal carnivores road | 213 | between locations of snakes, owls and mammal carnivores road | ||
| 214 | casualties and the abundance on verges of wood mice and rabbits, the | 214 | casualties and the abundance on verges of wood mice and rabbits, the | ||
| 215 | two main prey in the studied area. These results support the | 215 | two main prey in the studied area. These results support the | ||
| 216 | hypothesis that prey abundance on road verges may be a major driver | 216 | hypothesis that prey abundance on road verges may be a major driver | ||
| 217 | explaining predator roadkills. In Portugal, road verges and other road | 217 | explaining predator roadkills. In Portugal, road verges and other road | ||
| 218 | remnants of natural habitats are estimated to cover more than 140 | 218 | remnants of natural habitats are estimated to cover more than 140 | ||
| 219 | thousand hectares, an area larger than any terrestrial protected area | 219 | thousand hectares, an area larger than any terrestrial protected area | ||
| 220 | in the country. Similar or larger areas of remnant habitats along | 220 | in the country. Similar or larger areas of remnant habitats along | ||
| 221 | roads occur in many other countries. Thus, gathering further knowledge | 221 | roads occur in many other countries. Thus, gathering further knowledge | ||
| 222 | aiming to quantify and identify their role in biodiversity | 222 | aiming to quantify and identify their role in biodiversity | ||
| 223 | conservation is key to properly offset road impacts on wildlife." | 223 | conservation is key to properly offset road impacts on wildlife." | ||
| 224 | }, | 224 | }, | ||
| 225 | "num_resources": 1, | 225 | "num_resources": 1, | ||
| 226 | "num_tags": 2, | 226 | "num_tags": 2, | ||
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