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en Movement re-established but not restored: inferring the effectiveness of road-crossing mitigation for a gliding mammal by monitoring use. -
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(anteriormente2026-06-23
) en Movement re-established but not restored: inferring the effectiveness of road-crossing mitigation for a gliding mammal by monitoring use.
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| 81 | "notes": "Wildlife crossing structures are commonly used to mitigate | 95 | "notes": "Wildlife crossing structures are commonly used to mitigate | ||
| 82 | the barrier and mortality impacts of roads on wildlife. For arboreal | 96 | the barrier and mortality impacts of roads on wildlife. For arboreal | ||
| 83 | mammals, canopy bridges, glider poles and vegetated medians are used | 97 | mammals, canopy bridges, glider poles and vegetated medians are used | ||
| 84 | to provide safe passage across roads. However, the effectiveness of | 98 | to provide safe passage across roads. However, the effectiveness of | ||
| 85 | these measures is unknown. We investigate the effect of canopy | 99 | these measures is unknown. We investigate the effect of canopy | ||
| 86 | bridges, glider poles and vegetated medians on squirrel glider | 100 | bridges, glider poles and vegetated medians on squirrel glider | ||
| 87 | movement across a freeway in south-east Australia. We monitored | 101 | movement across a freeway in south-east Australia. We monitored | ||
| 88 | structures directly using motion-triggered cameras and passive | 102 | structures directly using motion-triggered cameras and passive | ||
| 89 | integrated transponder (PIT) scanners. Further, post-mitigation | 103 | integrated transponder (PIT) scanners. Further, post-mitigation | ||
| 90 | radio-tracking was compared to a pre-mitigation study. Squirrel | 104 | radio-tracking was compared to a pre-mitigation study. Squirrel | ||
| 91 | gliders used all structure types to cross the freeway, while the | 105 | gliders used all structure types to cross the freeway, while the | ||
| 92 | unmitigated freeway remained a barrier to movement. However, movement | 106 | unmitigated freeway remained a barrier to movement. However, movement | ||
| 93 | was not restored to the levels observed at non-freeway sites. | 107 | was not restored to the levels observed at non-freeway sites. | ||
| 94 | Nevertheless, based on the number and frequency of individuals | 108 | Nevertheless, based on the number and frequency of individuals | ||
| 95 | crossing, mitigation is likely to provide some level of functional | 109 | crossing, mitigation is likely to provide some level of functional | ||
| 96 | connectivity. The rate of crossing increased over several years as | 110 | connectivity. The rate of crossing increased over several years as | ||
| 97 | animals habituated to the structure. We also found that crossing rate | 111 | animals habituated to the structure. We also found that crossing rate | ||
| 98 | can be a misleading indicator of effectiveness if the number of | 112 | can be a misleading indicator of effectiveness if the number of | ||
| 99 | individuals crossing is not identified. Therefore, studies should | 113 | individuals crossing is not identified. Therefore, studies should | ||
| 100 | employ long-term monitoring and identify individuals crossing if | 114 | employ long-term monitoring and identify individuals crossing if | ||
| 101 | inferences about population connectivity are to be made from movement | 115 | inferences about population connectivity are to be made from movement | ||
| 102 | data alone.", | 116 | data alone.", | ||
| 103 | "notes_translated": { | 117 | "notes_translated": { | ||
| 104 | "en": "Wildlife crossing structures are commonly used to mitigate | 118 | "en": "Wildlife crossing structures are commonly used to mitigate | ||
| 105 | the barrier and mortality impacts of roads on wildlife. For arboreal | 119 | the barrier and mortality impacts of roads on wildlife. For arboreal | ||
| 106 | mammals, canopy bridges, glider poles and vegetated medians are used | 120 | mammals, canopy bridges, glider poles and vegetated medians are used | ||
| 107 | to provide safe passage across roads. However, the effectiveness of | 121 | to provide safe passage across roads. However, the effectiveness of | ||
| 108 | these measures is unknown. We investigate the effect of canopy | 122 | these measures is unknown. We investigate the effect of canopy | ||
| 109 | bridges, glider poles and vegetated medians on squirrel glider | 123 | bridges, glider poles and vegetated medians on squirrel glider | ||
| 110 | movement across a freeway in south-east Australia. We monitored | 124 | movement across a freeway in south-east Australia. We monitored | ||
| 111 | structures directly using motion-triggered cameras and passive | 125 | structures directly using motion-triggered cameras and passive | ||
| 112 | integrated\u00a0transponder\u00a0(PIT) scanners. Further, | 126 | integrated\u00a0transponder\u00a0(PIT) scanners. Further, | ||
| 113 | post-mitigation radio-tracking was compared to a pre-mitigation study. | 127 | post-mitigation radio-tracking was compared to a pre-mitigation study. | ||
| 114 | Squirrel gliders used all structure types to cross the freeway, while | 128 | Squirrel gliders used all structure types to cross the freeway, while | ||
| 115 | the unmitigated freeway remained a barrier to movement. However, | 129 | the unmitigated freeway remained a barrier to movement. However, | ||
| 116 | movement was not restored to the levels observed at non-freeway sites. | 130 | movement was not restored to the levels observed at non-freeway sites. | ||
| 117 | Nevertheless, based on the number and frequency of individuals | 131 | Nevertheless, based on the number and frequency of individuals | ||
| 118 | crossing, mitigation is likely to provide some level of functional | 132 | crossing, mitigation is likely to provide some level of functional | ||
| 119 | connectivity. The rate of crossing increased over several years as | 133 | connectivity. The rate of crossing increased over several years as | ||
| 120 | animals habituated to the structure. We also found that crossing rate | 134 | animals habituated to the structure. We also found that crossing rate | ||
| 121 | can be a misleading indicator of effectiveness if the number of | 135 | can be a misleading indicator of effectiveness if the number of | ||
| 122 | individuals crossing is not identified. Therefore, studies should | 136 | individuals crossing is not identified. Therefore, studies should | ||
| 123 | employ long-term monitoring and identify individuals crossing if | 137 | employ long-term monitoring and identify individuals crossing if | ||
| 124 | inferences about population connectivity are to be made from movement | 138 | inferences about population connectivity are to be made from movement | ||
| 125 | data alone.", | 139 | data alone.", | ||
| 126 | "es": "Wildlife crossing structures are commonly used to mitigate | 140 | "es": "Wildlife crossing structures are commonly used to mitigate | ||
| 127 | the barrier and mortality impacts of roads on wildlife. For arboreal | 141 | the barrier and mortality impacts of roads on wildlife. For arboreal | ||
| 128 | mammals, canopy bridges, glider poles and vegetated medians are used | 142 | mammals, canopy bridges, glider poles and vegetated medians are used | ||
| 129 | to provide safe passage across roads. However, the effectiveness of | 143 | to provide safe passage across roads. However, the effectiveness of | ||
| 130 | these measures is unknown. We investigate the effect of canopy | 144 | these measures is unknown. We investigate the effect of canopy | ||
| 131 | bridges, glider poles and vegetated medians on squirrel glider | 145 | bridges, glider poles and vegetated medians on squirrel glider | ||
| 132 | movement across a freeway in south-east Australia. We monitored | 146 | movement across a freeway in south-east Australia. We monitored | ||
| 133 | structures directly using motion-triggered cameras and passive | 147 | structures directly using motion-triggered cameras and passive | ||
| 134 | integrated transponder (PIT) scanners. Further, post-mitigation | 148 | integrated transponder (PIT) scanners. Further, post-mitigation | ||
| 135 | radio-tracking was compared to a pre-mitigation study. Squirrel | 149 | radio-tracking was compared to a pre-mitigation study. Squirrel | ||
| 136 | gliders used all structure types to cross the freeway, while the | 150 | gliders used all structure types to cross the freeway, while the | ||
| 137 | unmitigated freeway remained a barrier to movement. However, movement | 151 | unmitigated freeway remained a barrier to movement. However, movement | ||
| 138 | was not restored to the levels observed at non-freeway sites. | 152 | was not restored to the levels observed at non-freeway sites. | ||
| 139 | Nevertheless, based on the number and frequency of individuals | 153 | Nevertheless, based on the number and frequency of individuals | ||
| 140 | crossing, mitigation is likely to provide some level of functional | 154 | crossing, mitigation is likely to provide some level of functional | ||
| 141 | connectivity. The rate of crossing increased over several years as | 155 | connectivity. The rate of crossing increased over several years as | ||
| 142 | animals habituated to the structure. We also found that crossing rate | 156 | animals habituated to the structure. We also found that crossing rate | ||
| 143 | can be a misleading indicator of effectiveness if the number of | 157 | can be a misleading indicator of effectiveness if the number of | ||
| 144 | individuals crossing is not identified. Therefore, studies should | 158 | individuals crossing is not identified. Therefore, studies should | ||
| 145 | employ long-term monitoring and identify individuals crossing if | 159 | employ long-term monitoring and identify individuals crossing if | ||
| 146 | inferences about population connectivity are to be made from movement | 160 | inferences about population connectivity are to be made from movement | ||
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