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En el instante 23 de junio de 2026, 16:02:21 UTC,
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Modificado el valor del campo
spatial_coverage
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en Effects of roads on small-mammal movements: opportunities and risks of vegetation management on roadsides.
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| 5 | "author": "Galantinho, A., Santos, S., Eufr\u00e1zio, S., Silva, C., | 5 | "author": "Galantinho, A., Santos, S., Eufr\u00e1zio, S., Silva, C., | ||
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| 81 | "notes": "Roads can block animal movement and reduce persistence of | 81 | "notes": "Roads can block animal movement and reduce persistence of | ||
| 82 | species living in road surroundings. Movement restrictions on local | 82 | species living in road surroundings. Movement restrictions on local | ||
| 83 | populations may even increase extinction risk of abundant small | 83 | populations may even increase extinction risk of abundant small | ||
| 84 | mammals. However, road verges (road managed area between the edge of | 84 | mammals. However, road verges (road managed area between the edge of | ||
| 85 | the road and the beginning of private land) may provide refuge and | 85 | the road and the beginning of private land) may provide refuge and | ||
| 86 | corridors for small mammals when properly managed. Information on the | 86 | corridors for small mammals when properly managed. Information on the | ||
| 87 | effects of roads and roadside management on small-mammal movement is | 87 | effects of roads and roadside management on small-mammal movement is | ||
| 88 | still scarce for low traffic roads (<20,000 vehicles per day) crossing | 88 | still scarce for low traffic roads (<20,000 vehicles per day) crossing | ||
| 89 | well-preserved habitats. We aimed to fill this gap by comparing | 89 | well-preserved habitats. We aimed to fill this gap by comparing | ||
| 90 | fine-scale movement patterns of wood mice (Apodemus sylvaticus) in a | 90 | fine-scale movement patterns of wood mice (Apodemus sylvaticus) in a | ||
| 91 | road and in a similar roadless area without management. Both areas | 91 | road and in a similar roadless area without management. Both areas | ||
| 92 | consisted of a well-preserved Mediterranean agro-silvo pastoral | 92 | consisted of a well-preserved Mediterranean agro-silvo pastoral | ||
| 93 | system. We studied several movement patterns: road crossings, verge | 93 | system. We studied several movement patterns: road crossings, verge | ||
| 94 | use, length, and direction of movement. Additionally, we assessed how | 94 | use, length, and direction of movement. Additionally, we assessed how | ||
| 95 | roadside management, animals\u2019 sex and residency status, season | 95 | roadside management, animals\u2019 sex and residency status, season | ||
| 96 | and microhabitat affect movement at the road area. At the roadless | 96 | and microhabitat affect movement at the road area. At the roadless | ||
| 97 | area, we defined a virtual road and verges at equivalent locations to | 97 | area, we defined a virtual road and verges at equivalent locations to | ||
| 98 | the road area for comparison purposes. We gathered | 98 | the road area for comparison purposes. We gathered | ||
| 99 | capture-mark-recapture data for two years to characterize movement | 99 | capture-mark-recapture data for two years to characterize movement | ||
| 100 | patterns. Wood mice tended to avoid the road by crossing it less often | 100 | patterns. Wood mice tended to avoid the road by crossing it less often | ||
| 101 | and moving away from it more frequently than from equivalent locations | 101 | and moving away from it more frequently than from equivalent locations | ||
| 102 | in the roadless area. Wood mice used road verges more frequently than | 102 | in the roadless area. Wood mice used road verges more frequently than | ||
| 103 | virtual verges and moved more often parallel to the road than to the | 103 | virtual verges and moved more often parallel to the road than to the | ||
| 104 | virtual road. Road crossings were more frequent after firebreak | 104 | virtual road. Road crossings were more frequent after firebreak | ||
| 105 | openings (strips of mowed land) in surrounding areas and near taller | 105 | openings (strips of mowed land) in surrounding areas and near taller | ||
| 106 | shrubs. Also, males used road verges more often than females. | 106 | shrubs. Also, males used road verges more often than females. | ||
| 107 | Differences on several movement patterns between areas and their | 107 | Differences on several movement patterns between areas and their | ||
| 108 | trends within the road area can be explained mainly by the presence of | 108 | trends within the road area can be explained mainly by the presence of | ||
| 109 | the road and roadside vegetation management (e.g., firebreaks | 109 | the road and roadside vegetation management (e.g., firebreaks | ||
| 110 | openings). We suggest roadside vegetation management practices (e.g., | 110 | openings). We suggest roadside vegetation management practices (e.g., | ||
| 111 | avoid land mowing; maintain vegetation strips) to promote the role of | 111 | avoid land mowing; maintain vegetation strips) to promote the role of | ||
| 112 | verges as refuges and/or corridors for small mammals.", | 112 | verges as refuges and/or corridors for small mammals.", | ||
| 113 | "notes_translated": { | 113 | "notes_translated": { | ||
| 114 | "en": "Roads can block animal movement and reduce persistence of | 114 | "en": "Roads can block animal movement and reduce persistence of | ||
| 115 | species living in road surroundings. Movement restrictions on local | 115 | species living in road surroundings. Movement restrictions on local | ||
| 116 | populations may even increase extinction risk of abundant small | 116 | populations may even increase extinction risk of abundant small | ||
| 117 | mammals. However, road verges (road managed area between the edge of | 117 | mammals. However, road verges (road managed area between the edge of | ||
| 118 | the road and the beginning of private land) may provide refuge and | 118 | the road and the beginning of private land) may provide refuge and | ||
| 119 | corridors for small mammals when properly managed. Information on the | 119 | corridors for small mammals when properly managed. Information on the | ||
| 120 | effects of roads and\u00a0roadside\u00a0management on small-mammal | 120 | effects of roads and\u00a0roadside\u00a0management on small-mammal | ||
| 121 | movement is still scarce for low traffic roads (<20,000 vehicles per | 121 | movement is still scarce for low traffic roads (<20,000 vehicles per | ||
| 122 | day) crossing well-preserved habitats. We aimed to fill this gap by | 122 | day) crossing well-preserved habitats. We aimed to fill this gap by | ||
| 123 | comparing fine-scale movement patterns of wood mice (Apodemus | 123 | comparing fine-scale movement patterns of wood mice (Apodemus | ||
| 124 | sylvaticus) in a road and in a similar roadless area without | 124 | sylvaticus) in a road and in a similar roadless area without | ||
| 125 | management. Both areas consisted of a well-preserved Mediterranean | 125 | management. Both areas consisted of a well-preserved Mediterranean | ||
| 126 | agro-silvo pastoral system. We studied several movement patterns: road | 126 | agro-silvo pastoral system. We studied several movement patterns: road | ||
| 127 | crossings, verge use, length, and direction of movement. Additionally, | 127 | crossings, verge use, length, and direction of movement. Additionally, | ||
| 128 | we assessed how\u00a0roadside\u00a0management, animals\u2019 sex and | 128 | we assessed how\u00a0roadside\u00a0management, animals\u2019 sex and | ||
| 129 | residency status,\u00a0season\u00a0and\u00a0microhabitat\u00a0affect | 129 | residency status,\u00a0season\u00a0and\u00a0microhabitat\u00a0affect | ||
| 130 | movement at the road area. At the roadless area, we defined a virtual | 130 | movement at the road area. At the roadless area, we defined a virtual | ||
| 131 | road and verges at equivalent locations to the road area for | 131 | road and verges at equivalent locations to the road area for | ||
| 132 | comparison purposes. We gathered capture-mark-recapture data for two | 132 | comparison purposes. We gathered capture-mark-recapture data for two | ||
| 133 | years to characterize movement patterns. Wood mice tended to avoid the | 133 | years to characterize movement patterns. Wood mice tended to avoid the | ||
| 134 | road by crossing it less often and moving away from it more frequently | 134 | road by crossing it less often and moving away from it more frequently | ||
| 135 | than from equivalent locations in the roadless area. Wood mice used | 135 | than from equivalent locations in the roadless area. Wood mice used | ||
| 136 | road verges more frequently than virtual verges and moved more often | 136 | road verges more frequently than virtual verges and moved more often | ||
| 137 | parallel to the road than to the virtual road. Road crossings were | 137 | parallel to the road than to the virtual road. Road crossings were | ||
| 138 | more frequent after\u00a0firebreak\u00a0openings (strips of mowed | 138 | more frequent after\u00a0firebreak\u00a0openings (strips of mowed | ||
| 139 | land) in surrounding areas and near taller shrubs. Also, males used | 139 | land) in surrounding areas and near taller shrubs. Also, males used | ||
| 140 | road verges more often than females. Differences on several movement | 140 | road verges more often than females. Differences on several movement | ||
| 141 | patterns between areas and their trends within the road area can be | 141 | patterns between areas and their trends within the road area can be | ||
| 142 | explained mainly by the presence of the road and roadside vegetation | 142 | explained mainly by the presence of the road and roadside vegetation | ||
| 143 | management (e.g., firebreaks openings). We suggest roadside vegetation | 143 | management (e.g., firebreaks openings). We suggest roadside vegetation | ||
| 144 | management practices (e.g., avoid land mowing; maintain vegetation | 144 | management practices (e.g., avoid land mowing; maintain vegetation | ||
| 145 | strips) to promote the role of verges as refuges and/or corridors for | 145 | strips) to promote the role of verges as refuges and/or corridors for | ||
| 146 | small mammals.", | 146 | small mammals.", | ||
| 147 | "es": "Roads can block animal movement and reduce persistence of | 147 | "es": "Roads can block animal movement and reduce persistence of | ||
| 148 | species living in road surroundings. Movement restrictions on local | 148 | species living in road surroundings. Movement restrictions on local | ||
| 149 | populations may even increase extinction risk of abundant small | 149 | populations may even increase extinction risk of abundant small | ||
| 150 | mammals. However, road verges (road managed area between the edge of | 150 | mammals. However, road verges (road managed area between the edge of | ||
| 151 | the road and the beginning of private land) may provide refuge and | 151 | the road and the beginning of private land) may provide refuge and | ||
| 152 | corridors for small mammals when properly managed. Information on the | 152 | corridors for small mammals when properly managed. Information on the | ||
| 153 | effects of roads and roadside management on small-mammal movement is | 153 | effects of roads and roadside management on small-mammal movement is | ||
| 154 | still scarce for low traffic roads (<20,000 vehicles per day) crossing | 154 | still scarce for low traffic roads (<20,000 vehicles per day) crossing | ||
| 155 | well-preserved habitats. We aimed to fill this gap by comparing | 155 | well-preserved habitats. We aimed to fill this gap by comparing | ||
| 156 | fine-scale movement patterns of wood mice (Apodemus sylvaticus) in a | 156 | fine-scale movement patterns of wood mice (Apodemus sylvaticus) in a | ||
| 157 | road and in a similar roadless area without management. Both areas | 157 | road and in a similar roadless area without management. Both areas | ||
| 158 | consisted of a well-preserved Mediterranean agro-silvo pastoral | 158 | consisted of a well-preserved Mediterranean agro-silvo pastoral | ||
| 159 | system. We studied several movement patterns: road crossings, verge | 159 | system. We studied several movement patterns: road crossings, verge | ||
| 160 | use, length, and direction of movement. Additionally, we assessed how | 160 | use, length, and direction of movement. Additionally, we assessed how | ||
| 161 | roadside management, animals\u2019 sex and residency status, season | 161 | roadside management, animals\u2019 sex and residency status, season | ||
| 162 | and microhabitat affect movement at the road area. At the roadless | 162 | and microhabitat affect movement at the road area. At the roadless | ||
| 163 | area, we defined a virtual road and verges at equivalent locations to | 163 | area, we defined a virtual road and verges at equivalent locations to | ||
| 164 | the road area for comparison purposes. We gathered | 164 | the road area for comparison purposes. We gathered | ||
| 165 | capture-mark-recapture data for two years to characterize movement | 165 | capture-mark-recapture data for two years to characterize movement | ||
| 166 | patterns. Wood mice tended to avoid the road by crossing it less often | 166 | patterns. Wood mice tended to avoid the road by crossing it less often | ||
| 167 | and moving away from it more frequently than from equivalent locations | 167 | and moving away from it more frequently than from equivalent locations | ||
| 168 | in the roadless area. Wood mice used road verges more frequently than | 168 | in the roadless area. Wood mice used road verges more frequently than | ||
| 169 | virtual verges and moved more often parallel to the road than to the | 169 | virtual verges and moved more often parallel to the road than to the | ||
| 170 | virtual road. Road crossings were more frequent after firebreak | 170 | virtual road. Road crossings were more frequent after firebreak | ||
| 171 | openings (strips of mowed land) in surrounding areas and near taller | 171 | openings (strips of mowed land) in surrounding areas and near taller | ||
| 172 | shrubs. Also, males used road verges more often than females. | 172 | shrubs. Also, males used road verges more often than females. | ||
| 173 | Differences on several movement patterns between areas and their | 173 | Differences on several movement patterns between areas and their | ||
| 174 | trends within the road area can be explained mainly by the presence of | 174 | trends within the road area can be explained mainly by the presence of | ||
| 175 | the road and roadside vegetation management (e.g., firebreaks | 175 | the road and roadside vegetation management (e.g., firebreaks | ||
| 176 | openings). We suggest roadside vegetation management practices (e.g., | 176 | openings). We suggest roadside vegetation management practices (e.g., | ||
| 177 | avoid land mowing; maintain vegetation strips) to promote the role of | 177 | avoid land mowing; maintain vegetation strips) to promote the role of | ||
| 178 | verges as refuges and/or corridors for small mammals." | 178 | verges as refuges and/or corridors for small mammals." | ||
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