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En el instante 25 de junio de 2026, 12:31:08 UTC,
-
Modificado el valor del campo
modified
a2026-06-25
en Roads, forestry plantations and hedgerows affect badger occupancy in intensive Mediterranean farmland. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Roads, forestry plantations and hedgerows affect badger occupancy in intensive Mediterranean farmland.
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| 81 | "name": "b0a696c0-c72f-506b-87c6-a1c6ba651ffe", | 95 | "name": "b0a696c0-c72f-506b-87c6-a1c6ba651ffe", | ||
| 82 | "notes": "There is increasing interest in understanding how to | 96 | "notes": "There is increasing interest in understanding how to | ||
| 83 | retain wildlife in agricultural landscapes, thereby contributing to | 97 | retain wildlife in agricultural landscapes, thereby contributing to | ||
| 84 | global biodiversity conservation efforts. Here we investigate the | 98 | global biodiversity conservation efforts. Here we investigate the | ||
| 85 | drivers of European badger (Meles meles) occurrence in Mediterranean | 99 | drivers of European badger (Meles meles) occurrence in Mediterranean | ||
| 86 | farmland. The badger is a generalist mammalian carnivore usually | 100 | farmland. The badger is a generalist mammalian carnivore usually | ||
| 87 | associated to native woodland and shrubland, so we hypothesised that | 101 | associated to native woodland and shrubland, so we hypothesised that | ||
| 88 | its occurrence in Mediterranean farmland should be favoured by | 102 | its occurrence in Mediterranean farmland should be favoured by | ||
| 89 | substitute habitats such as forestry plantations, and negatively | 103 | substitute habitats such as forestry plantations, and negatively | ||
| 90 | affected by areas more heavily used by humans such as paved roads. The | 104 | affected by areas more heavily used by humans such as paved roads. The | ||
| 91 | study was conducted in SW Portugal, where we surveyed for badgers | 105 | study was conducted in SW Portugal, where we surveyed for badgers | ||
| 92 | presence signs (latrines, footprints, setts) along transects located | 106 | presence signs (latrines, footprints, setts) along transects located | ||
| 93 | at 60 3.14-km2 circles scattered through the landscape, each of which | 107 | at 60 3.14-km2 circles scattered through the landscape, each of which | ||
| 94 | surveyed in spring (March-May), summer (July-August) and autumn | 108 | surveyed in spring (March-May), summer (July-August) and autumn | ||
| 95 | (September-October). Occupancy-detection models were used to quantify | 109 | (September-October). Occupancy-detection models were used to quantify | ||
| 96 | the effect of environmental variables on badger occupancy probability, | 110 | the effect of environmental variables on badger occupancy probability, | ||
| 97 | while controlling for imperfect detection. Badger detection | 111 | while controlling for imperfect detection. Badger detection | ||
| 98 | probability was positively affected by the density of dirt roads, | 112 | probability was positively affected by the density of dirt roads, | ||
| 99 | possibly reflecting a preference of badgers to mark along those | 113 | possibly reflecting a preference of badgers to mark along those | ||
| 100 | structures. According to predictions, badger occupancy significantly | 114 | structures. According to predictions, badger occupancy significantly | ||
| 101 | increased with the amount of forestry plantations and arboreal | 115 | increased with the amount of forestry plantations and arboreal | ||
| 102 | hedgerows, while decreasing with increasing paved road density. Taken | 116 | hedgerows, while decreasing with increasing paved road density. Taken | ||
| 103 | together, our results indicate that badger conservation in | 117 | together, our results indicate that badger conservation in | ||
| 104 | Mediterranean farmland under agricultural intensification should | 118 | Mediterranean farmland under agricultural intensification should | ||
| 105 | require the protection of areas with low paved road density, and the | 119 | require the protection of areas with low paved road density, and the | ||
| 106 | retention of wood cover, even where these are highly-modified habitats | 120 | retention of wood cover, even where these are highly-modified habitats | ||
| 107 | such as forest plantations and arboreal hedgerows.", | 121 | such as forest plantations and arboreal hedgerows.", | ||
| 108 | "notes_translated": { | 122 | "notes_translated": { | ||
| 109 | "en": "There is increasing interest in understanding how to retain | 123 | "en": "There is increasing interest in understanding how to retain | ||
| 110 | wildlife in\u00a0agricultural landscapes, thereby contributing to | 124 | wildlife in\u00a0agricultural landscapes, thereby contributing to | ||
| 111 | global biodiversity conservation efforts. Here we investigate the | 125 | global biodiversity conservation efforts. Here we investigate the | ||
| 112 | drivers of European badger (Meles meles) occurrence in Mediterranean | 126 | drivers of European badger (Meles meles) occurrence in Mediterranean | ||
| 113 | farmland. The badger is a generalist mammalian carnivore usually | 127 | farmland. The badger is a generalist mammalian carnivore usually | ||
| 114 | associated to native woodland and shrubland, so we hypothesised that | 128 | associated to native woodland and shrubland, so we hypothesised that | ||
| 115 | its occurrence in Mediterranean farmland should be favoured by | 129 | its occurrence in Mediterranean farmland should be favoured by | ||
| 116 | substitute habitats such as forestry plantations, and negatively | 130 | substitute habitats such as forestry plantations, and negatively | ||
| 117 | affected by areas more heavily used by humans such as paved roads. The | 131 | affected by areas more heavily used by humans such as paved roads. The | ||
| 118 | study was conducted in SW Portugal, where we surveyed for badgers | 132 | study was conducted in SW Portugal, where we surveyed for badgers | ||
| 119 | presence signs (latrines, footprints, setts) along transects located | 133 | presence signs (latrines, footprints, setts) along transects located | ||
| 120 | at 60 3.14-km2\u00a0circles scattered through the landscape, each of | 134 | at 60 3.14-km2\u00a0circles scattered through the landscape, each of | ||
| 121 | which surveyed in spring (March-May), summer (July-August) and autumn | 135 | which surveyed in spring (March-May), summer (July-August) and autumn | ||
| 122 | (September-October). Occupancy-detection models were used to quantify | 136 | (September-October). Occupancy-detection models were used to quantify | ||
| 123 | the effect of environmental variables on badger occupancy probability, | 137 | the effect of environmental variables on badger occupancy probability, | ||
| 124 | while controlling for imperfect detection. Badger detection | 138 | while controlling for imperfect detection. Badger detection | ||
| 125 | probability was positively affected by the density of dirt roads, | 139 | probability was positively affected by the density of dirt roads, | ||
| 126 | possibly reflecting a preference of badgers to mark along those | 140 | possibly reflecting a preference of badgers to mark along those | ||
| 127 | structures. According to predictions, badger occupancy significantly | 141 | structures. According to predictions, badger occupancy significantly | ||
| 128 | increased with the amount of forestry plantations and | 142 | increased with the amount of forestry plantations and | ||
| 129 | arboreal\u00a0hedgerows, while decreasing with increasing paved road | 143 | arboreal\u00a0hedgerows, while decreasing with increasing paved road | ||
| 130 | density. Taken together, our results indicate that badger conservation | 144 | density. Taken together, our results indicate that badger conservation | ||
| 131 | in Mediterranean farmland under agricultural intensification should | 145 | in Mediterranean farmland under agricultural intensification should | ||
| 132 | require the protection of areas with low paved road density, and the | 146 | require the protection of areas with low paved road density, and the | ||
| 133 | retention of wood cover, even where these are highly-modified habitats | 147 | retention of wood cover, even where these are highly-modified habitats | ||
| 134 | such as forest plantations and arboreal hedgerows.", | 148 | such as forest plantations and arboreal hedgerows.", | ||
| 135 | "es": "There is increasing interest in understanding how to retain | 149 | "es": "There is increasing interest in understanding how to retain | ||
| 136 | wildlife in agricultural landscapes, thereby contributing to global | 150 | wildlife in agricultural landscapes, thereby contributing to global | ||
| 137 | biodiversity conservation efforts. Here we investigate the drivers of | 151 | biodiversity conservation efforts. Here we investigate the drivers of | ||
| 138 | European badger (Meles meles) occurrence in Mediterranean farmland. | 152 | European badger (Meles meles) occurrence in Mediterranean farmland. | ||
| 139 | The badger is a generalist mammalian carnivore usually associated to | 153 | The badger is a generalist mammalian carnivore usually associated to | ||
| 140 | native woodland and shrubland, so we hypothesised that its occurrence | 154 | native woodland and shrubland, so we hypothesised that its occurrence | ||
| 141 | in Mediterranean farmland should be favoured by substitute habitats | 155 | in Mediterranean farmland should be favoured by substitute habitats | ||
| 142 | such as forestry plantations, and negatively affected by areas more | 156 | such as forestry plantations, and negatively affected by areas more | ||
| 143 | heavily used by humans such as paved roads. The study was conducted in | 157 | heavily used by humans such as paved roads. The study was conducted in | ||
| 144 | SW Portugal, where we surveyed for badgers presence signs (latrines, | 158 | SW Portugal, where we surveyed for badgers presence signs (latrines, | ||
| 145 | footprints, setts) along transects located at 60 3.14-km2 circles | 159 | footprints, setts) along transects located at 60 3.14-km2 circles | ||
| 146 | scattered through the landscape, each of which surveyed in spring | 160 | scattered through the landscape, each of which surveyed in spring | ||
| 147 | (March-May), summer (July-August) and autumn (September-October). | 161 | (March-May), summer (July-August) and autumn (September-October). | ||
| 148 | Occupancy-detection models were used to quantify the effect of | 162 | Occupancy-detection models were used to quantify the effect of | ||
| 149 | environmental variables on badger occupancy probability, while | 163 | environmental variables on badger occupancy probability, while | ||
| 150 | controlling for imperfect detection. Badger detection probability was | 164 | controlling for imperfect detection. Badger detection probability was | ||
| 151 | positively affected by the density of dirt roads, possibly reflecting | 165 | positively affected by the density of dirt roads, possibly reflecting | ||
| 152 | a preference of badgers to mark along those structures. According to | 166 | a preference of badgers to mark along those structures. According to | ||
| 153 | predictions, badger occupancy significantly increased with the amount | 167 | predictions, badger occupancy significantly increased with the amount | ||
| 154 | of forestry plantations and arboreal hedgerows, while decreasing with | 168 | of forestry plantations and arboreal hedgerows, while decreasing with | ||
| 155 | increasing paved road density. Taken together, our results indicate | 169 | increasing paved road density. Taken together, our results indicate | ||
| 156 | that badger conservation in Mediterranean farmland under agricultural | 170 | that badger conservation in Mediterranean farmland under agricultural | ||
| 157 | intensification should require the protection of areas with low paved | 171 | intensification should require the protection of areas with low paved | ||
| 158 | road density, and the retention of wood cover, even where these are | 172 | road density, and the retention of wood cover, even where these are | ||
| 159 | highly-modified habitats such as forest plantations and arboreal | 173 | highly-modified habitats such as forest plantations and arboreal | ||
| 160 | hedgerows." | 174 | hedgerows." | ||
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