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En el instante 23 de junio de 2026, 16:12:16 UTC,
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Modificado el valor del campo
spatial_coverage
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en Do dry ledges reduce the barrier effect of roads?
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| 81 | "notes": "Wildlife crossing structures combined with fencing seek to | 81 | "notes": "Wildlife crossing structures combined with fencing seek to | ||
| 82 | improve permeability and habitat connectivity across roads and reduce | 82 | improve permeability and habitat connectivity across roads and reduce | ||
| 83 | wildlife-vehicle collisions. However, the presence of water inside | 83 | wildlife-vehicle collisions. However, the presence of water inside | ||
| 84 | culverts can seriously limit their effectiveness. The implementation | 84 | culverts can seriously limit their effectiveness. The implementation | ||
| 85 | of dry ledges can be a good measure to allow crossing when flooded. So | 85 | of dry ledges can be a good measure to allow crossing when flooded. So | ||
| 86 | far, there is a lack of knowledge on the effectiveness of dry ledges | 86 | far, there is a lack of knowledge on the effectiveness of dry ledges | ||
| 87 | combined with fencing for a wide diversity of vertebrates. The main | 87 | combined with fencing for a wide diversity of vertebrates. The main | ||
| 88 | goal of this study is to evaluate how the presence of dry ledge affect | 88 | goal of this study is to evaluate how the presence of dry ledge affect | ||
| 89 | culvert use for Mediterranean mesocarnivores (red fox Vulpes vulpes, | 89 | culvert use for Mediterranean mesocarnivores (red fox Vulpes vulpes, | ||
| 90 | stone marten Martes foina, European badger Meles meles, European otter | 90 | stone marten Martes foina, European badger Meles meles, European otter | ||
| 91 | Lutra lutra and common genet Genetta genetta). Between January and | 91 | Lutra lutra and common genet Genetta genetta). Between January and | ||
| 92 | March 2008, wooden dry ledges were placed in 15 of 32 surveyed | 92 | March 2008, wooden dry ledges were placed in 15 of 32 surveyed | ||
| 93 | culverts. Additionally 100 meters of small mesh size and buried fences | 93 | culverts. Additionally 100 meters of small mesh size and buried fences | ||
| 94 | were installed along each side of all culverts. During one year we | 94 | were installed along each side of all culverts. During one year we | ||
| 95 | used video surveillance and track-plates to detect crossing events | 95 | used video surveillance and track-plates to detect crossing events | ||
| 96 | over seven consecutive nights per season in each monitored culvert. We | 96 | over seven consecutive nights per season in each monitored culvert. We | ||
| 97 | evaluate the relative importance of dry ledges on culvert use and | 97 | evaluate the relative importance of dry ledges on culvert use and | ||
| 98 | compare the number of road-kills within a 100 m buffer radius around | 98 | compare the number of road-kills within a 100 m buffer radius around | ||
| 99 | the culverts before and after fence installation and culverts that | 99 | the culverts before and after fence installation and culverts that | ||
| 100 | were never fenced (control culverts). Although different species | 100 | were never fenced (control culverts). Although different species | ||
| 101 | responded to culvert features differently, the presence of dry ledges | 101 | responded to culvert features differently, the presence of dry ledges | ||
| 102 | was the most relevant feature explaining crossing events, in | 102 | was the most relevant feature explaining crossing events, in | ||
| 103 | particular, for stone martens and genets. The fencing used did not | 103 | particular, for stone martens and genets. The fencing used did not | ||
| 104 | reduce mammals road-kill prevalence. Our results imply that in order | 104 | reduce mammals road-kill prevalence. Our results imply that in order | ||
| 105 | to improve culvert use, road managers should take into account the | 105 | to improve culvert use, road managers should take into account the | ||
| 106 | placement of ledges on culverts that remain flooded most of the year | 106 | placement of ledges on culverts that remain flooded most of the year | ||
| 107 | (more than 3 cm of water-depth). We also suggest exploring the role of | 107 | (more than 3 cm of water-depth). We also suggest exploring the role of | ||
| 108 | ledge size and construction materials to increase the likelihood of | 108 | ledge size and construction materials to increase the likelihood of | ||
| 109 | being used by foxes and badgers.\n Palabras clave: Barrier", | 109 | being used by foxes and badgers.\n Palabras clave: Barrier", | ||
| 110 | "notes_translated": { | 110 | "notes_translated": { | ||
| 111 | "en": "Wildlife crossing structures combined with fencing seek to | 111 | "en": "Wildlife crossing structures combined with fencing seek to | ||
| 112 | improve permeability and habitat connectivity across roads and reduce | 112 | improve permeability and habitat connectivity across roads and reduce | ||
| 113 | wildlife-vehicle collisions. However, the presence of water inside | 113 | wildlife-vehicle collisions. However, the presence of water inside | ||
| 114 | culverts can seriously limit their effectiveness. The implementation | 114 | culverts can seriously limit their effectiveness. The implementation | ||
| 115 | of dry ledges can be a good measure to allow crossing when flooded. So | 115 | of dry ledges can be a good measure to allow crossing when flooded. So | ||
| 116 | far, there is a lack of knowledge on the effectiveness of dry ledges | 116 | far, there is a lack of knowledge on the effectiveness of dry ledges | ||
| 117 | combined with fencing for a wide diversity of vertebrates. The main | 117 | combined with fencing for a wide diversity of vertebrates. The main | ||
| 118 | goal of this study is to evaluate how the presence of dry ledge affect | 118 | goal of this study is to evaluate how the presence of dry ledge affect | ||
| 119 | culvert use for Mediterranean mesocarnivores (red fox Vulpes vulpes, | 119 | culvert use for Mediterranean mesocarnivores (red fox Vulpes vulpes, | ||
| 120 | stone marten Martes foina, European badger Meles meles, European otter | 120 | stone marten Martes foina, European badger Meles meles, European otter | ||
| 121 | Lutra lutra and common genet Genetta genetta). Between January and | 121 | Lutra lutra and common genet Genetta genetta). Between January and | ||
| 122 | March 2008, wooden dry ledges were placed in 15 of 32 surveyed | 122 | March 2008, wooden dry ledges were placed in 15 of 32 surveyed | ||
| 123 | culverts. Additionally 100 meters of small mesh size and buried fences | 123 | culverts. Additionally 100 meters of small mesh size and buried fences | ||
| 124 | were installed along each side of all culverts. During one year we | 124 | were installed along each side of all culverts. During one year we | ||
| 125 | used video surveillance and track-plates to detect crossing events | 125 | used video surveillance and track-plates to detect crossing events | ||
| 126 | over seven consecutive nights per season in each monitored culvert. We | 126 | over seven consecutive nights per season in each monitored culvert. We | ||
| 127 | evaluate the relative importance of dry ledges on culvert use and | 127 | evaluate the relative importance of dry ledges on culvert use and | ||
| 128 | compare the number of road-kills within a 100 m buffer radius around | 128 | compare the number of road-kills within a 100 m buffer radius around | ||
| 129 | the culverts before and after fence installation and culverts that | 129 | the culverts before and after fence installation and culverts that | ||
| 130 | were never fenced (control culverts). Although different species | 130 | were never fenced (control culverts). Although different species | ||
| 131 | responded to culvert features differently, the presence of dry ledges | 131 | responded to culvert features differently, the presence of dry ledges | ||
| 132 | was the most relevant feature explaining crossing events, in | 132 | was the most relevant feature explaining crossing events, in | ||
| 133 | particular, for stone martens and genets. The fencing used did not | 133 | particular, for stone martens and genets. The fencing used did not | ||
| 134 | reduce mammals road-kill prevalence. Our results imply that in order | 134 | reduce mammals road-kill prevalence. Our results imply that in order | ||
| 135 | to improve culvert use, road managers should take into account the | 135 | to improve culvert use, road managers should take into account the | ||
| 136 | placement of ledges on culverts that remain flooded most of the year | 136 | placement of ledges on culverts that remain flooded most of the year | ||
| 137 | (more than 3 cm of water-depth). We also suggest exploring the role of | 137 | (more than 3 cm of water-depth). We also suggest exploring the role of | ||
| 138 | ledge size and construction materials to increase the likelihood of | 138 | ledge size and construction materials to increase the likelihood of | ||
| 139 | being used by foxes and badgers.\n Palabras clave: Barrier", | 139 | being used by foxes and badgers.\n Palabras clave: Barrier", | ||
| 140 | "es": "Wildlife crossing structures combined with fencing seek to | 140 | "es": "Wildlife crossing structures combined with fencing seek to | ||
| 141 | improve permeability and habitat connectivity across roads and reduce | 141 | improve permeability and habitat connectivity across roads and reduce | ||
| 142 | wildlife-vehicle collisions. However, the presence of water inside | 142 | wildlife-vehicle collisions. However, the presence of water inside | ||
| 143 | culverts can seriously limit their effectiveness. The implementation | 143 | culverts can seriously limit their effectiveness. The implementation | ||
| 144 | of dry ledges can be a good measure to allow crossing when flooded. So | 144 | of dry ledges can be a good measure to allow crossing when flooded. So | ||
| 145 | far, there is a lack of knowledge on the effectiveness of dry ledges | 145 | far, there is a lack of knowledge on the effectiveness of dry ledges | ||
| 146 | combined with fencing for a wide diversity of vertebrates. The main | 146 | combined with fencing for a wide diversity of vertebrates. The main | ||
| 147 | goal of this study is to evaluate how the presence of dry ledge affect | 147 | goal of this study is to evaluate how the presence of dry ledge affect | ||
| 148 | culvert use for Mediterranean mesocarnivores (red fox Vulpes vulpes, | 148 | culvert use for Mediterranean mesocarnivores (red fox Vulpes vulpes, | ||
| 149 | stone marten Martes foina, European badger Meles meles, European otter | 149 | stone marten Martes foina, European badger Meles meles, European otter | ||
| 150 | Lutra lutra and common genet Genetta genetta). Between January and | 150 | Lutra lutra and common genet Genetta genetta). Between January and | ||
| 151 | March 2008, wooden dry ledges were placed in 15 of 32 surveyed | 151 | March 2008, wooden dry ledges were placed in 15 of 32 surveyed | ||
| 152 | culverts. Additionally 100 meters of small mesh size and buried fences | 152 | culverts. Additionally 100 meters of small mesh size and buried fences | ||
| 153 | were installed along each side of all culverts. During one year we | 153 | were installed along each side of all culverts. During one year we | ||
| 154 | used video surveillance and track-plates to detect crossing events | 154 | used video surveillance and track-plates to detect crossing events | ||
| 155 | over seven consecutive nights per season in each monitored culvert. We | 155 | over seven consecutive nights per season in each monitored culvert. We | ||
| 156 | evaluate the relative importance of dry ledges on culvert use and | 156 | evaluate the relative importance of dry ledges on culvert use and | ||
| 157 | compare the number of road-kills within a 100 m buffer radius around | 157 | compare the number of road-kills within a 100 m buffer radius around | ||
| 158 | the culverts before and after fence installation and culverts that | 158 | the culverts before and after fence installation and culverts that | ||
| 159 | were never fenced (control culverts). Although different species | 159 | were never fenced (control culverts). Although different species | ||
| 160 | responded to culvert features differently, the presence of dry ledges | 160 | responded to culvert features differently, the presence of dry ledges | ||
| 161 | was the most relevant feature explaining crossing events, in | 161 | was the most relevant feature explaining crossing events, in | ||
| 162 | particular, for stone martens and genets. The fencing used did not | 162 | particular, for stone martens and genets. The fencing used did not | ||
| 163 | reduce mammals road-kill prevalence. Our results imply that in order | 163 | reduce mammals road-kill prevalence. Our results imply that in order | ||
| 164 | to improve culvert use, road managers should take into account the | 164 | to improve culvert use, road managers should take into account the | ||
| 165 | placement of ledges on culverts that remain flooded most of the year | 165 | placement of ledges on culverts that remain flooded most of the year | ||
| 166 | (more than 3 cm of water-depth). We also suggest exploring the role of | 166 | (more than 3 cm of water-depth). We also suggest exploring the role of | ||
| 167 | ledge size and construction materials to increase the likelihood of | 167 | ledge size and construction materials to increase the likelihood of | ||
| 168 | being used by foxes and badgers.\n Palabras clave: Barrier" | 168 | being used by foxes and badgers.\n Palabras clave: Barrier" | ||
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