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en Effects of roads on European badger occurrence in intensively used Mediterranean farmland. -
Modificado el valor del campo
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del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Effects of roads on European badger occurrence in intensively used Mediterranean farmland.
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| 81 | "notes": "Understanding how transportation infrastructure affects | 95 | "notes": "Understanding how transportation infrastructure affects | ||
| 82 | wildlife is a key goal in conservation biology. This goal is | 96 | wildlife is a key goal in conservation biology. This goal is | ||
| 83 | particularly relevant in intensively used landscapes, where species | 97 | particularly relevant in intensively used landscapes, where species | ||
| 84 | are potentially impacted both by roads and the scarcity of suitable | 98 | are potentially impacted both by roads and the scarcity of suitable | ||
| 85 | natural habitats. We investigated how road density and landscape | 99 | natural habitats. We investigated how road density and landscape | ||
| 86 | composition and configuration affect the occurrence of the European | 100 | composition and configuration affect the occurrence of the European | ||
| 87 | badger (Meles meles) in intensively used Mediterranean farmland. | 101 | badger (Meles meles) in intensively used Mediterranean farmland. | ||
| 88 | Although most studies documenting road impacts on carnivores species | 102 | Although most studies documenting road impacts on carnivores species | ||
| 89 | in Mediterranean areas have been largely focused on the factors | 103 | in Mediterranean areas have been largely focused on the factors | ||
| 90 | driving mortality at roads or habitat use near and far from roads, few | 104 | driving mortality at roads or habitat use near and far from roads, few | ||
| 91 | have explicitly assessed how road density impacts species occurrence, | 105 | have explicitly assessed how road density impacts species occurrence, | ||
| 92 | particularly in intensively used farmland, where their preferred | 106 | particularly in intensively used farmland, where their preferred | ||
| 93 | native woodland habitats are relatively scarce. Based on badgers\u2019 | 107 | native woodland habitats are relatively scarce. Based on badgers\u2019 | ||
| 94 | presence signs surveys conducted in three occasions (spring, summer | 108 | presence signs surveys conducted in three occasions (spring, summer | ||
| 95 | and autumn) across 60 landscape units (3.14-km2 circles) scattered | 109 | and autumn) across 60 landscape units (3.14-km2 circles) scattered | ||
| 96 | through SW Portugal, we used occupancy-detection modelling to quantify | 110 | through SW Portugal, we used occupancy-detection modelling to quantify | ||
| 97 | the effect of paved road density on the occurrence of the species in | 111 | the effect of paved road density on the occurrence of the species in | ||
| 98 | intensively used Mediterranean farmland. In addition, we tested the | 112 | intensively used Mediterranean farmland. In addition, we tested the | ||
| 99 | prediction that forestry plantations and hedgerows embedded in the | 113 | prediction that forestry plantations and hedgerows embedded in the | ||
| 100 | agricultural matrix should in turn result in increased probabilities | 114 | agricultural matrix should in turn result in increased probabilities | ||
| 101 | of badger occupancy, as these habitats should provide substitute | 115 | of badger occupancy, as these habitats should provide substitute | ||
| 102 | refuge areas for the species. According to our predictions, badger | 116 | refuge areas for the species. According to our predictions, badger | ||
| 103 | occupancy significantly decreased with increasing paved road density, | 117 | occupancy significantly decreased with increasing paved road density, | ||
| 104 | and increased with increasing amount of forestry plantations and | 118 | and increased with increasing amount of forestry plantations and | ||
| 105 | arboreal hedgerows. These results suggest that badger conservation in | 119 | arboreal hedgerows. These results suggest that badger conservation in | ||
| 106 | intensively used Mediterranean farmland requires the protection of | 120 | intensively used Mediterranean farmland requires the protection of | ||
| 107 | areas with low road density, and the retention of wood cover, even | 121 | areas with low road density, and the retention of wood cover, even | ||
| 108 | where these are mostly forestry plantations and arboreal hedgerows.", | 122 | where these are mostly forestry plantations and arboreal hedgerows.", | ||
| 109 | "notes_translated": { | 123 | "notes_translated": { | ||
| 110 | "en": "Understanding how transportation infrastructure affects | 124 | "en": "Understanding how transportation infrastructure affects | ||
| 111 | wildlife is a key goal in conservation biology. This goal is | 125 | wildlife is a key goal in conservation biology. This goal is | ||
| 112 | particularly relevant in intensively used landscapes, where species | 126 | particularly relevant in intensively used landscapes, where species | ||
| 113 | are potentially impacted both by roads and the scarcity of suitable | 127 | are potentially impacted both by roads and the scarcity of suitable | ||
| 114 | natural habitats. We investigated how road density and landscape | 128 | natural habitats. We investigated how road density and landscape | ||
| 115 | composition and configuration affect the occurrence of the European | 129 | composition and configuration affect the occurrence of the European | ||
| 116 | badger (Meles meles) in intensively used Mediterranean farmland. | 130 | badger (Meles meles) in intensively used Mediterranean farmland. | ||
| 117 | Although most studies documenting road impacts on carnivores species | 131 | Although most studies documenting road impacts on carnivores species | ||
| 118 | in Mediterranean areas have been largely focused on the factors | 132 | in Mediterranean areas have been largely focused on the factors | ||
| 119 | driving mortality at roads or habitat use near and far from roads, few | 133 | driving mortality at roads or habitat use near and far from roads, few | ||
| 120 | have explicitly assessed how road density impacts species occurrence, | 134 | have explicitly assessed how road density impacts species occurrence, | ||
| 121 | particularly in intensively used farmland, where their preferred | 135 | particularly in intensively used farmland, where their preferred | ||
| 122 | native woodland habitats are relatively scarce. Based on badgers\u2019 | 136 | native woodland habitats are relatively scarce. Based on badgers\u2019 | ||
| 123 | presence signs surveys conducted in three occasions (spring, summer | 137 | presence signs surveys conducted in three occasions (spring, summer | ||
| 124 | and autumn) across 60 landscape units (3.14-km2 circles) scattered | 138 | and autumn) across 60 landscape units (3.14-km2 circles) scattered | ||
| 125 | through SW Portugal, we used occupancy-detection modelling to quantify | 139 | through SW Portugal, we used occupancy-detection modelling to quantify | ||
| 126 | the effect of paved road density on the occurrence of the species in | 140 | the effect of paved road density on the occurrence of the species in | ||
| 127 | intensively used Mediterranean farmland. In addition, we tested the | 141 | intensively used Mediterranean farmland. In addition, we tested the | ||
| 128 | prediction that forestry plantations and hedgerows embedded in the | 142 | prediction that forestry plantations and hedgerows embedded in the | ||
| 129 | agricultural matrix should in turn result in increased probabilities | 143 | agricultural matrix should in turn result in increased probabilities | ||
| 130 | of badger occupancy, as these habitats should provide substitute | 144 | of badger occupancy, as these habitats should provide substitute | ||
| 131 | refuge areas for the species. According to our predictions, badger | 145 | refuge areas for the species. According to our predictions, badger | ||
| 132 | occupancy significantly decreased with increasing paved road density, | 146 | occupancy significantly decreased with increasing paved road density, | ||
| 133 | and increased with increasing amount of forestry plantations and | 147 | and increased with increasing amount of forestry plantations and | ||
| 134 | arboreal hedgerows. These results suggest that badger conservation in | 148 | arboreal hedgerows. These results suggest that badger conservation in | ||
| 135 | intensively used Mediterranean farmland requires the protection of | 149 | intensively used Mediterranean farmland requires the protection of | ||
| 136 | areas with low road density, and the retention of wood cover, even | 150 | areas with low road density, and the retention of wood cover, even | ||
| 137 | where these are mostly forestry plantations and arboreal hedgerows.", | 151 | where these are mostly forestry plantations and arboreal hedgerows.", | ||
| 138 | "es": "Understanding how transportation infrastructure affects | 152 | "es": "Understanding how transportation infrastructure affects | ||
| 139 | wildlife is a key goal in conservation biology. This goal is | 153 | wildlife is a key goal in conservation biology. This goal is | ||
| 140 | particularly relevant in intensively used landscapes, where species | 154 | particularly relevant in intensively used landscapes, where species | ||
| 141 | are potentially impacted both by roads and the scarcity of suitable | 155 | are potentially impacted both by roads and the scarcity of suitable | ||
| 142 | natural habitats. We investigated how road density and landscape | 156 | natural habitats. We investigated how road density and landscape | ||
| 143 | composition and configuration affect the occurrence of the European | 157 | composition and configuration affect the occurrence of the European | ||
| 144 | badger (Meles meles) in intensively used Mediterranean farmland. | 158 | badger (Meles meles) in intensively used Mediterranean farmland. | ||
| 145 | Although most studies documenting road impacts on carnivores species | 159 | Although most studies documenting road impacts on carnivores species | ||
| 146 | in Mediterranean areas have been largely focused on the factors | 160 | in Mediterranean areas have been largely focused on the factors | ||
| 147 | driving mortality at roads or habitat use near and far from roads, few | 161 | driving mortality at roads or habitat use near and far from roads, few | ||
| 148 | have explicitly assessed how road density impacts species occurrence, | 162 | have explicitly assessed how road density impacts species occurrence, | ||
| 149 | particularly in intensively used farmland, where their preferred | 163 | particularly in intensively used farmland, where their preferred | ||
| 150 | native woodland habitats are relatively scarce. Based on badgers\u2019 | 164 | native woodland habitats are relatively scarce. Based on badgers\u2019 | ||
| 151 | presence signs surveys conducted in three occasions (spring, summer | 165 | presence signs surveys conducted in three occasions (spring, summer | ||
| 152 | and autumn) across 60 landscape units (3.14-km2 circles) scattered | 166 | and autumn) across 60 landscape units (3.14-km2 circles) scattered | ||
| 153 | through SW Portugal, we used occupancy-detection modelling to quantify | 167 | through SW Portugal, we used occupancy-detection modelling to quantify | ||
| 154 | the effect of paved road density on the occurrence of the species in | 168 | the effect of paved road density on the occurrence of the species in | ||
| 155 | intensively used Mediterranean farmland. In addition, we tested the | 169 | intensively used Mediterranean farmland. In addition, we tested the | ||
| 156 | prediction that forestry plantations and hedgerows embedded in the | 170 | prediction that forestry plantations and hedgerows embedded in the | ||
| 157 | agricultural matrix should in turn result in increased probabilities | 171 | agricultural matrix should in turn result in increased probabilities | ||
| 158 | of badger occupancy, as these habitats should provide substitute | 172 | of badger occupancy, as these habitats should provide substitute | ||
| 159 | refuge areas for the species. According to our predictions, badger | 173 | refuge areas for the species. According to our predictions, badger | ||
| 160 | occupancy significantly decreased with increasing paved road density, | 174 | occupancy significantly decreased with increasing paved road density, | ||
| 161 | and increased with increasing amount of forestry plantations and | 175 | and increased with increasing amount of forestry plantations and | ||
| 162 | arboreal hedgerows. These results suggest that badger conservation in | 176 | arboreal hedgerows. These results suggest that badger conservation in | ||
| 163 | intensively used Mediterranean farmland requires the protection of | 177 | intensively used Mediterranean farmland requires the protection of | ||
| 164 | areas with low road density, and the retention of wood cover, even | 178 | areas with low road density, and the retention of wood cover, even | ||
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