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En el instante 25 de junio de 2026, 12:30:28 UTC,
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Modificado el valor del campo
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a2026-06-25
en Mechanisms underlying the road effects on owls: move towards mitigation. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Mechanisms underlying the road effects on owls: move towards mitigation.
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| 79 | "notes": "The negative effects of roads on wildlife are recognized | 93 | "notes": "The negative effects of roads on wildlife are recognized | ||
| 80 | as important contributors to the global biodiversity crisis but the | 94 | as important contributors to the global biodiversity crisis but the | ||
| 81 | underlying mechanisms remain poorly understood, a fact critical for | 95 | underlying mechanisms remain poorly understood, a fact critical for | ||
| 82 | appropriate management strategies. At this stage, a way to optimize | 96 | appropriate management strategies. At this stage, a way to optimize | ||
| 83 | mitigation measures is to move from the description of mortality and | 97 | mitigation measures is to move from the description of mortality and | ||
| 84 | distribution patterns towards the study of individual behavioral | 98 | distribution patterns towards the study of individual behavioral | ||
| 85 | responses to roads and the environmental variables that control them. | 99 | responses to roads and the environmental variables that control them. | ||
| 86 | In this study, using mortality and the broadcast of territorial calls | 100 | In this study, using mortality and the broadcast of territorial calls | ||
| 87 | records, we examined the effect of road- and landscape-related factors | 101 | records, we examined the effect of road- and landscape-related factors | ||
| 88 | on distribution and mortality of barn owl Tyto alba, tawny owl Strix | 102 | on distribution and mortality of barn owl Tyto alba, tawny owl Strix | ||
| 89 | aluco and little owl Athene noctua. We also analyzed fine-scale | 103 | aluco and little owl Athene noctua. We also analyzed fine-scale | ||
| 90 | movements of radiotracked barn owls, estimated the mortality risk | 104 | movements of radiotracked barn owls, estimated the mortality risk | ||
| 91 | based on the highway crossings and compared the expected with the | 105 | based on the highway crossings and compared the expected with the | ||
| 92 | observed mortality. Our results show that owls tend to occur far away | 106 | observed mortality. Our results show that owls tend to occur far away | ||
| 93 | from the major roads. We recorded high mortality rates (59 ind./100 | 107 | from the major roads. We recorded high mortality rates (59 ind./100 | ||
| 94 | km/year) in road sections with low traffic and within suitable | 108 | km/year) in road sections with low traffic and within suitable | ||
| 95 | habitat. Barn owls, in particular, define their home-ranges nearby | 109 | habitat. Barn owls, in particular, define their home-ranges nearby | ||
| 96 | highways if there is available habitat and tend to be road-killed in | 110 | highways if there is available habitat and tend to be road-killed in | ||
| 97 | the same places where they successful cross the highways. The risk of | 111 | the same places where they successful cross the highways. The risk of | ||
| 98 | being killed per crossing event is 0.018, resulting in an expected | 112 | being killed per crossing event is 0.018, resulting in an expected | ||
| 99 | mortality of 48-96 barn owls/100 km/year. These estimates were much | 113 | mortality of 48-96 barn owls/100 km/year. These estimates were much | ||
| 100 | higher than the observed daily mortality (6.2 ind./100 km/year). The | 114 | higher than the observed daily mortality (6.2 ind./100 km/year). The | ||
| 101 | high death toll imposed by roads may decrease density regionally over | 115 | high death toll imposed by roads may decrease density regionally over | ||
| 102 | the years by acting as a demographic sink that often remains | 116 | the years by acting as a demographic sink that often remains | ||
| 103 | unoccupied and where dispersing individuals tend to settle. Thus, road | 117 | unoccupied and where dispersing individuals tend to settle. Thus, road | ||
| 104 | managers must reduce road mortality risk by discouraging owls from | 118 | managers must reduce road mortality risk by discouraging owls from | ||
| 105 | flying along the road verges (e. g. frequent mowing and ploughing) and | 119 | flying along the road verges (e. g. frequent mowing and ploughing) and | ||
| 106 | raising the height of the roadside verges to encourage owls to fly | 120 | raising the height of the roadside verges to encourage owls to fly | ||
| 107 | above the traffic in high incidence of road mortality.", | 121 | above the traffic in high incidence of road mortality.", | ||
| 108 | "notes_translated": { | 122 | "notes_translated": { | ||
| 109 | "en": "The negative effects of roads on wildlife are recognized as | 123 | "en": "The negative effects of roads on wildlife are recognized as | ||
| 110 | important contributors to the global biodiversity crisis but the | 124 | important contributors to the global biodiversity crisis but the | ||
| 111 | underlying mechanisms remain poorly understood, a fact critical for | 125 | underlying mechanisms remain poorly understood, a fact critical for | ||
| 112 | appropriate management strategies. At this stage, a way to optimize | 126 | appropriate management strategies. At this stage, a way to optimize | ||
| 113 | mitigation\nmeasures is to move from the description of mortality and | 127 | mitigation\nmeasures is to move from the description of mortality and | ||
| 114 | distribution patterns towards the study of individual behavioral | 128 | distribution patterns towards the study of individual behavioral | ||
| 115 | responses to roads and the environmental variables that control them. | 129 | responses to roads and the environmental variables that control them. | ||
| 116 | In this study, using mortality and the broadcast of territorial calls | 130 | In this study, using mortality and the broadcast of territorial calls | ||
| 117 | records,\nwe examined the effect of road- and landscape-related | 131 | records,\nwe examined the effect of road- and landscape-related | ||
| 118 | factors on distribution and mortality of barn owl Tyto alba, tawny owl | 132 | factors on distribution and mortality of barn owl Tyto alba, tawny owl | ||
| 119 | Strix aluco and little owl Athene noctua. We also analyzed fine-scale | 133 | Strix aluco and little owl Athene noctua. We also analyzed fine-scale | ||
| 120 | movements of radiotracked barn owls, estimated the mortality risk | 134 | movements of radiotracked barn owls, estimated the mortality risk | ||
| 121 | based\non the highway crossings and compared the expected with the | 135 | based\non the highway crossings and compared the expected with the | ||
| 122 | observed mortality. Our results show that owls tend to occur far away | 136 | observed mortality. Our results show that owls tend to occur far away | ||
| 123 | from the major roads. We recorded high mortality rates (59 ind./100 | 137 | from the major roads. We recorded high mortality rates (59 ind./100 | ||
| 124 | km/year) in road sections with low traffic and within suitable | 138 | km/year) in road sections with low traffic and within suitable | ||
| 125 | habitat.\nBarn owls, in particular, define their home-ranges nearby | 139 | habitat.\nBarn owls, in particular, define their home-ranges nearby | ||
| 126 | highways if there is available habitat and tend to be road-killed in | 140 | highways if there is available habitat and tend to be road-killed in | ||
| 127 | the same places where they successful cross the highways. The risk of | 141 | the same places where they successful cross the highways. The risk of | ||
| 128 | being killed per crossing event is 0.018, resulting in an expected | 142 | being killed per crossing event is 0.018, resulting in an expected | ||
| 129 | mortality of 48-96 barn owls/100 km/year. These estimates were much | 143 | mortality of 48-96 barn owls/100 km/year. These estimates were much | ||
| 130 | higher than the observed daily mortality (6.2 ind./100 km/year). The | 144 | higher than the observed daily mortality (6.2 ind./100 km/year). The | ||
| 131 | high death toll imposed by roads may decrease density regionally over | 145 | high death toll imposed by roads may decrease density regionally over | ||
| 132 | the years by acting as a demographic sink that often remains | 146 | the years by acting as a demographic sink that often remains | ||
| 133 | unoccupied\nand where dispersing individuals tend to settle. Thus, | 147 | unoccupied\nand where dispersing individuals tend to settle. Thus, | ||
| 134 | road managers must reduce road mortality risk by discouraging owls | 148 | road managers must reduce road mortality risk by discouraging owls | ||
| 135 | from flying along the road verges (e. g. frequent mowing and | 149 | from flying along the road verges (e. g. frequent mowing and | ||
| 136 | ploughing) and raising the height of the roadside verges to encourage | 150 | ploughing) and raising the height of the roadside verges to encourage | ||
| 137 | owls to fly above the traffic in high incidence of road mortality.", | 151 | owls to fly above the traffic in high incidence of road mortality.", | ||
| 138 | "es": "The negative effects of roads on wildlife are recognized as | 152 | "es": "The negative effects of roads on wildlife are recognized as | ||
| 139 | important contributors to the global biodiversity crisis but the | 153 | important contributors to the global biodiversity crisis but the | ||
| 140 | underlying mechanisms remain poorly understood, a fact critical for | 154 | underlying mechanisms remain poorly understood, a fact critical for | ||
| 141 | appropriate management strategies. At this stage, a way to optimize | 155 | appropriate management strategies. At this stage, a way to optimize | ||
| 142 | mitigation measures is to move from the description of mortality and | 156 | mitigation measures is to move from the description of mortality and | ||
| 143 | distribution patterns towards the study of individual behavioral | 157 | distribution patterns towards the study of individual behavioral | ||
| 144 | responses to roads and the environmental variables that control them. | 158 | responses to roads and the environmental variables that control them. | ||
| 145 | In this study, using mortality and the broadcast of territorial calls | 159 | In this study, using mortality and the broadcast of territorial calls | ||
| 146 | records, we examined the effect of road- and landscape-related factors | 160 | records, we examined the effect of road- and landscape-related factors | ||
| 147 | on distribution and mortality of barn owl Tyto alba, tawny owl Strix | 161 | on distribution and mortality of barn owl Tyto alba, tawny owl Strix | ||
| 148 | aluco and little owl Athene noctua. We also analyzed fine-scale | 162 | aluco and little owl Athene noctua. We also analyzed fine-scale | ||
| 149 | movements of radiotracked barn owls, estimated the mortality risk | 163 | movements of radiotracked barn owls, estimated the mortality risk | ||
| 150 | based on the highway crossings and compared the expected with the | 164 | based on the highway crossings and compared the expected with the | ||
| 151 | observed mortality. Our results show that owls tend to occur far away | 165 | observed mortality. Our results show that owls tend to occur far away | ||
| 152 | from the major roads. We recorded high mortality rates (59 ind./100 | 166 | from the major roads. We recorded high mortality rates (59 ind./100 | ||
| 153 | km/year) in road sections with low traffic and within suitable | 167 | km/year) in road sections with low traffic and within suitable | ||
| 154 | habitat. Barn owls, in particular, define their home-ranges nearby | 168 | habitat. Barn owls, in particular, define their home-ranges nearby | ||
| 155 | highways if there is available habitat and tend to be road-killed in | 169 | highways if there is available habitat and tend to be road-killed in | ||
| 156 | the same places where they successful cross the highways. The risk of | 170 | the same places where they successful cross the highways. The risk of | ||
| 157 | being killed per crossing event is 0.018, resulting in an expected | 171 | being killed per crossing event is 0.018, resulting in an expected | ||
| 158 | mortality of 48-96 barn owls/100 km/year. These estimates were much | 172 | mortality of 48-96 barn owls/100 km/year. These estimates were much | ||
| 159 | higher than the observed daily mortality (6.2 ind./100 km/year). The | 173 | higher than the observed daily mortality (6.2 ind./100 km/year). The | ||
| 160 | high death toll imposed by roads may decrease density regionally over | 174 | high death toll imposed by roads may decrease density regionally over | ||
| 161 | the years by acting as a demographic sink that often remains | 175 | the years by acting as a demographic sink that often remains | ||
| 162 | unoccupied and where dispersing individuals tend to settle. Thus, road | 176 | unoccupied and where dispersing individuals tend to settle. Thus, road | ||
| 163 | managers must reduce road mortality risk by discouraging owls from | 177 | managers must reduce road mortality risk by discouraging owls from | ||
| 164 | flying along the road verges (e. g. frequent mowing and ploughing) and | 178 | flying along the road verges (e. g. frequent mowing and ploughing) and | ||
| 165 | raising the height of the roadside verges to encourage owls to fly | 179 | raising the height of the roadside verges to encourage owls to fly | ||
| 166 | above the traffic in high incidence of road mortality." | 180 | above the traffic in high incidence of road mortality." | ||
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