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En el instante 25 de junio de 2026, 12:34:40 UTC,
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a2026-06-25
en How do landscape context and fences influence roadkill locations of small and médium-size mammals? -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en How do landscape context and fences influence roadkill locations of small and médium-size mammals?
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| 78 | "notes": "Road mortality is the most easily visible effect of roads | 92 | "notes": "Road mortality is the most easily visible effect of roads | ||
| 79 | and traffic on wildlife populations. Mitigation measures such as | 93 | and traffic on wildlife populations. Mitigation measures such as | ||
| 80 | fences and wildlife passages have been applied to reduce these | 94 | fences and wildlife passages have been applied to reduce these | ||
| 81 | effects. During the widening of Quebec's Highway 175 from two to four | 95 | effects. During the widening of Quebec's Highway 175 from two to four | ||
| 82 | lanes between 2006 and 2012, 33 wildlife passages designed | 96 | lanes between 2006 and 2012, 33 wildlife passages designed | ||
| 83 | specifically for small and medium-sized mammals were installed under | 97 | specifically for small and medium-sized mammals were installed under | ||
| 84 | the road in combination with short fences. This study examined the | 98 | the road in combination with short fences. This study examined the | ||
| 85 | effectiveness of the fences at reducing the number of small and | 99 | effectiveness of the fences at reducing the number of small and | ||
| 86 | medium-sized mammals killed along a 68 km section of the road while | 100 | medium-sized mammals killed along a 68 km section of the road while | ||
| 87 | controlling for the potential confounding effects of landscape | 101 | controlling for the potential confounding effects of landscape | ||
| 88 | variables. Repeated daily mortality surveys were conducted by car | 102 | variables. Repeated daily mortality surveys were conducted by car | ||
| 89 | during the summers of 2012\u20132015 to measure roadkill occurrence | 103 | during the summers of 2012\u20132015 to measure roadkill occurrence | ||
| 90 | and detection probability. A total of 893 dead animals from 13 taxa | 104 | and detection probability. A total of 893 dead animals from 13 taxa | ||
| 91 | were detected. Roadkill occurrence was significantly greater at fence | 105 | were detected. Roadkill occurrence was significantly greater at fence | ||
| 92 | ends than in fenced sections and unfenced sections (fence-end effect), | 106 | ends than in fenced sections and unfenced sections (fence-end effect), | ||
| 93 | indicating that the fences were not long enough to discourage animals | 107 | indicating that the fences were not long enough to discourage animals | ||
| 94 | from moving along the fence to the fence ends. Greater length would be | 108 | from moving along the fence to the fence ends. Greater length would be | ||
| 95 | required to meet the target of reduced road mortality. Shrubby | 109 | required to meet the target of reduced road mortality. Shrubby | ||
| 96 | vegetation in the median strip separating the two directions of the | 110 | vegetation in the median strip separating the two directions of the | ||
| 97 | highway was associated with high roadkill occurrence for medium-sized | 111 | highway was associated with high roadkill occurrence for medium-sized | ||
| 98 | species. Roadkill detection probability for all species combined was | 112 | species. Roadkill detection probability for all species combined was | ||
| 99 | 0.72, ranging from 0.17 for small mammals (<1 kg) to 0.82 for | 113 | 0.72, ranging from 0.17 for small mammals (<1 kg) to 0.82 for | ||
| 100 | medium-sized mammals (>1 kg). To reduce road mortality, when wildlife | 114 | medium-sized mammals (>1 kg). To reduce road mortality, when wildlife | ||
| 101 | passages are constructed along with new highways or retrofitted to old | 115 | passages are constructed along with new highways or retrofitted to old | ||
| 102 | highways, fences either should be continuous or sufficiently long to | 116 | highways, fences either should be continuous or sufficiently long to | ||
| 103 | encourage passage use rather than movement around the fence ends. | 117 | encourage passage use rather than movement around the fence ends. | ||
| 104 | Future road mortality studies should be combined with data about | 118 | Future road mortality studies should be combined with data about | ||
| 105 | wildlife abundance and detection probability to more accurately | 119 | wildlife abundance and detection probability to more accurately | ||
| 106 | estimate the effects at the population level.\n Palabras clave: Fence, | 120 | estimate the effects at the population level.\n Palabras clave: Fence, | ||
| 107 | Mammal", | 121 | Mammal", | ||
| 108 | "notes_translated": { | 122 | "notes_translated": { | ||
| 109 | "en": "Road mortality is the most easily visible effect of roads | 123 | "en": "Road mortality is the most easily visible effect of roads | ||
| 110 | and traffic on wildlife populations. Mitigation measures such as | 124 | and traffic on wildlife populations. Mitigation measures such as | ||
| 111 | fences and wildlife passages have been applied to reduce these | 125 | fences and wildlife passages have been applied to reduce these | ||
| 112 | effects. During the widening of Quebec's Highway 175 from two to four | 126 | effects. During the widening of Quebec's Highway 175 from two to four | ||
| 113 | lanes between 2006 and 2012, 33 wildlife passages designed | 127 | lanes between 2006 and 2012, 33 wildlife passages designed | ||
| 114 | specifically for small and medium-sized mammals were installed under | 128 | specifically for small and medium-sized mammals were installed under | ||
| 115 | the road in combination with short fences. This study examined the | 129 | the road in combination with short fences. This study examined the | ||
| 116 | effectiveness of the fences at reducing the number of small and | 130 | effectiveness of the fences at reducing the number of small and | ||
| 117 | medium-sized mammals killed along a 68\u202fkm section of the road | 131 | medium-sized mammals killed along a 68\u202fkm section of the road | ||
| 118 | while controlling for the potential confounding effects of landscape | 132 | while controlling for the potential confounding effects of landscape | ||
| 119 | variables. Repeated daily mortality surveys were conducted by car | 133 | variables. Repeated daily mortality surveys were conducted by car | ||
| 120 | during the summers of 2012\u20132015 to measure roadkill occurrence | 134 | during the summers of 2012\u20132015 to measure roadkill occurrence | ||
| 121 | and detection probability. A total of 893 dead animals from 13 taxa | 135 | and detection probability. A total of 893 dead animals from 13 taxa | ||
| 122 | were detected. Roadkill occurrence was significantly greater at fence | 136 | were detected. Roadkill occurrence was significantly greater at fence | ||
| 123 | ends than in fenced sections and unfenced sections (fence-end effect), | 137 | ends than in fenced sections and unfenced sections (fence-end effect), | ||
| 124 | indicating that the fences were not long enough to discourage animals | 138 | indicating that the fences were not long enough to discourage animals | ||
| 125 | from moving along the fence to the fence ends. Greater length would be | 139 | from moving along the fence to the fence ends. Greater length would be | ||
| 126 | required to meet the target of reduced road mortality. Shrubby | 140 | required to meet the target of reduced road mortality. Shrubby | ||
| 127 | vegetation in the median strip separating the two directions of the | 141 | vegetation in the median strip separating the two directions of the | ||
| 128 | highway was associated with high roadkill occurrence for medium-sized | 142 | highway was associated with high roadkill occurrence for medium-sized | ||
| 129 | species. Roadkill detection probability for all species combined was | 143 | species. Roadkill detection probability for all species combined was | ||
| 130 | 0.72, ranging from 0.17 for small mammals (<1\u202fkg) to 0.82 for | 144 | 0.72, ranging from 0.17 for small mammals (<1\u202fkg) to 0.82 for | ||
| 131 | medium-sized mammals (>1\u202fkg). To reduce road mortality, when | 145 | medium-sized mammals (>1\u202fkg). To reduce road mortality, when | ||
| 132 | wildlife passages are constructed along with new highways or | 146 | wildlife passages are constructed along with new highways or | ||
| 133 | retrofitted to old highways, fences either should be continuous or | 147 | retrofitted to old highways, fences either should be continuous or | ||
| 134 | sufficiently long to encourage passage use rather than movement around | 148 | sufficiently long to encourage passage use rather than movement around | ||
| 135 | the fence ends. Future road mortality studies should be combined with | 149 | the fence ends. Future road mortality studies should be combined with | ||
| 136 | data about wildlife abundance and detection probability to more | 150 | data about wildlife abundance and detection probability to more | ||
| 137 | accurately estimate the effects at the population level.", | 151 | accurately estimate the effects at the population level.", | ||
| 138 | "es": "Road mortality is the most easily visible effect of roads | 152 | "es": "Road mortality is the most easily visible effect of roads | ||
| 139 | and traffic on wildlife populations. Mitigation measures such as | 153 | and traffic on wildlife populations. Mitigation measures such as | ||
| 140 | fences and wildlife passages have been applied to reduce these | 154 | fences and wildlife passages have been applied to reduce these | ||
| 141 | effects. During the widening of Quebec's Highway 175 from two to four | 155 | effects. During the widening of Quebec's Highway 175 from two to four | ||
| 142 | lanes between 2006 and 2012, 33 wildlife passages designed | 156 | lanes between 2006 and 2012, 33 wildlife passages designed | ||
| 143 | specifically for small and medium-sized mammals were installed under | 157 | specifically for small and medium-sized mammals were installed under | ||
| 144 | the road in combination with short fences. This study examined the | 158 | the road in combination with short fences. This study examined the | ||
| 145 | effectiveness of the fences at reducing the number of small and | 159 | effectiveness of the fences at reducing the number of small and | ||
| 146 | medium-sized mammals killed along a 68 km section of the road while | 160 | medium-sized mammals killed along a 68 km section of the road while | ||
| 147 | controlling for the potential confounding effects of landscape | 161 | controlling for the potential confounding effects of landscape | ||
| 148 | variables. Repeated daily mortality surveys were conducted by car | 162 | variables. Repeated daily mortality surveys were conducted by car | ||
| 149 | during the summers of 2012\u20132015 to measure roadkill occurrence | 163 | during the summers of 2012\u20132015 to measure roadkill occurrence | ||
| 150 | and detection probability. A total of 893 dead animals from 13 taxa | 164 | and detection probability. A total of 893 dead animals from 13 taxa | ||
| 151 | were detected. Roadkill occurrence was significantly greater at fence | 165 | were detected. Roadkill occurrence was significantly greater at fence | ||
| 152 | ends than in fenced sections and unfenced sections (fence-end effect), | 166 | ends than in fenced sections and unfenced sections (fence-end effect), | ||
| 153 | indicating that the fences were not long enough to discourage animals | 167 | indicating that the fences were not long enough to discourage animals | ||
| 154 | from moving along the fence to the fence ends. Greater length would be | 168 | from moving along the fence to the fence ends. Greater length would be | ||
| 155 | required to meet the target of reduced road mortality. Shrubby | 169 | required to meet the target of reduced road mortality. Shrubby | ||
| 156 | vegetation in the median strip separating the two directions of the | 170 | vegetation in the median strip separating the two directions of the | ||
| 157 | highway was associated with high roadkill occurrence for medium-sized | 171 | highway was associated with high roadkill occurrence for medium-sized | ||
| 158 | species. Roadkill detection probability for all species combined was | 172 | species. Roadkill detection probability for all species combined was | ||
| 159 | 0.72, ranging from 0.17 for small mammals (<1 kg) to 0.82 for | 173 | 0.72, ranging from 0.17 for small mammals (<1 kg) to 0.82 for | ||
| 160 | medium-sized mammals (>1 kg). To reduce road mortality, when wildlife | 174 | medium-sized mammals (>1 kg). To reduce road mortality, when wildlife | ||
| 161 | passages are constructed along with new highways or retrofitted to old | 175 | passages are constructed along with new highways or retrofitted to old | ||
| 162 | highways, fences either should be continuous or sufficiently long to | 176 | highways, fences either should be continuous or sufficiently long to | ||
| 163 | encourage passage use rather than movement around the fence ends. | 177 | encourage passage use rather than movement around the fence ends. | ||
| 164 | Future road mortality studies should be combined with data about | 178 | Future road mortality studies should be combined with data about | ||
| 165 | wildlife abundance and detection probability to more accurately | 179 | wildlife abundance and detection probability to more accurately | ||
| 166 | estimate the effects at the population level.\n Palabras clave: Fence, | 180 | estimate the effects at the population level.\n Palabras clave: Fence, | ||
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