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En el instante 23 de junio de 2026, 16:08:06 UTC,
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spatial_coverage
a[{'bbox': '{"type": "Polygon", "coordinates": [[[-18.16, 27.64], [4.32, 27.64], [4.32, 43.79], [-18.16, 43.79], [-18.16, 27.64]]]}', 'centroid': '{"type": "Point", "coordinates": [-6.92, 35.715]}', 'text': 'España', 'uri': 'http://datos.gob.es/recurso/sector-publico/territorio/Pais/España'}]
en Behavioural responses of barn owls and stone martens to highways: do ecological or highway features explain the differences?
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| 5 | "author": "Grilo, C., Sousa, J., Matos, H., Leitao, I., Pinheiro, | 5 | "author": "Grilo, C., Sousa, J., Matos, H., Leitao, I., Pinheiro, | ||
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| 83 | "notes": "Several studies have documented that owls and carnivores | 83 | "notes": "Several studies have documented that owls and carnivores | ||
| 84 | are two taxa highly impacted by road mortality, but little is known | 84 | are two taxa highly impacted by road mortality, but little is known | ||
| 85 | whether roads attract or repulse individuals. The main goal of this | 85 | whether roads attract or repulse individuals. The main goal of this | ||
| 86 | study was to evaluate the response behavior of two model species (barn | 86 | study was to evaluate the response behavior of two model species (barn | ||
| 87 | owl and stone marten) through the (a) home-ranges shape and size; (b) | 87 | owl and stone marten) through the (a) home-ranges shape and size; (b) | ||
| 88 | effect of traffic volume on the space use patterns; and (c) highway | 88 | effect of traffic volume on the space use patterns; and (c) highway | ||
| 89 | crossings rate. We radio-tracked 10 barn owls and 10 stone martens | 89 | crossings rate. We radio-tracked 10 barn owls and 10 stone martens | ||
| 90 | captured within 2000m of A2 and A6 highway (14900 and 5700 | 90 | captured within 2000m of A2 and A6 highway (14900 and 5700 | ||
| 91 | vehicles/day, respectively) in southern Portugal. Fixes were taken | 91 | vehicles/day, respectively) in southern Portugal. Fixes were taken | ||
| 92 | every 30 minutes from dusk to dawn. Six individuals of each species | 92 | every 30 minutes from dusk to dawn. Six individuals of each species | ||
| 93 | provided data to estimate home-range and the response behaviors were | 93 | provided data to estimate home-range and the response behaviors were | ||
| 94 | not similar. All barn owls had the highway as the home-range (95% | 94 | not similar. All barn owls had the highway as the home-range (95% | ||
| 95 | Kernel estimator) boundary while stone martens randomly included or | 95 | Kernel estimator) boundary while stone martens randomly included or | ||
| 96 | excluded the highway in the home-range. Barn owls also showed a | 96 | excluded the highway in the home-range. Barn owls also showed a | ||
| 97 | positive correlation between the distance to highways and traffic | 97 | positive correlation between the distance to highways and traffic | ||
| 98 | volume, while stone martens only responded to trucks traffic. On | 98 | volume, while stone martens only responded to trucks traffic. On | ||
| 99 | average, we found 7.47 barn owls highway crossings in each 100 | 99 | average, we found 7.47 barn owls highway crossings in each 100 | ||
| 100 | radio-tracking hours while for stone martens this value was almost | 100 | radio-tracking hours while for stone martens this value was almost | ||
| 101 | three times higher (16.5 crossings). The most likely explanation for | 101 | three times higher (16.5 crossings). The most likely explanation for | ||
| 102 | the observed species-specific differences is behavioral. Owls use the | 102 | the observed species-specific differences is behavioral. Owls use the | ||
| 103 | acoustic system to communicate and locate prey, and therefore seem to | 103 | acoustic system to communicate and locate prey, and therefore seem to | ||
| 104 | be more sensitive to the presence of highways and traffic than stone | 104 | be more sensitive to the presence of highways and traffic than stone | ||
| 105 | martens. Low traffic (2000 vehicles/night) may explain the tendency of | 105 | martens. Low traffic (2000 vehicles/night) may explain the tendency of | ||
| 106 | stone martens to cross the highways instead of using the existing | 106 | stone martens to cross the highways instead of using the existing | ||
| 107 | passages (1.96passages/km). Reducing risk of mortality is therefore a | 107 | passages (1.96passages/km). Reducing risk of mortality is therefore a | ||
| 108 | management need. Natural obstacles would force owls to fly higher | 108 | management need. Natural obstacles would force owls to fly higher | ||
| 109 | whilst crossing the highway and will also reduce the disturbance in | 109 | whilst crossing the highway and will also reduce the disturbance in | ||
| 110 | the vicinity, while passages adaptation may improve its use by stone | 110 | the vicinity, while passages adaptation may improve its use by stone | ||
| 111 | martens.", | 111 | martens.", | ||
| 112 | "notes_translated": { | 112 | "notes_translated": { | ||
| 113 | "en": "Several studies have documented that owls and carnivores | 113 | "en": "Several studies have documented that owls and carnivores | ||
| 114 | are two taxa highly impacted by road mortality, but little is known | 114 | are two taxa highly impacted by road mortality, but little is known | ||
| 115 | whether roads attract or repulse individuals. The main goal of this | 115 | whether roads attract or repulse individuals. The main goal of this | ||
| 116 | study was to evaluate the response behavior of two model species (barn | 116 | study was to evaluate the response behavior of two model species (barn | ||
| 117 | owl and stone marten) through the (a) home-ranges shape and size; (b) | 117 | owl and stone marten) through the (a) home-ranges shape and size; (b) | ||
| 118 | effect of traffic volume on the space use patterns; and (c) highway | 118 | effect of traffic volume on the space use patterns; and (c) highway | ||
| 119 | crossings rate. We radio-tracked 10 barn owls and 10 stone martens | 119 | crossings rate. We radio-tracked 10 barn owls and 10 stone martens | ||
| 120 | captured within 2000m of A2 and A6 highway (14900 and 5700 | 120 | captured within 2000m of A2 and A6 highway (14900 and 5700 | ||
| 121 | vehicles/day, respectively) in southern Portugal. Fixes were taken | 121 | vehicles/day, respectively) in southern Portugal. Fixes were taken | ||
| 122 | every 30 minutes from dusk to dawn. Six individuals of each species | 122 | every 30 minutes from dusk to dawn. Six individuals of each species | ||
| 123 | provided data to estimate home-range and the response behaviors were | 123 | provided data to estimate home-range and the response behaviors were | ||
| 124 | not similar. All barn owls had the highway as the home-range (95% | 124 | not similar. All barn owls had the highway as the home-range (95% | ||
| 125 | Kernel estimator) boundary while stone martens randomly included or | 125 | Kernel estimator) boundary while stone martens randomly included or | ||
| 126 | excluded the highway in the home-range. Barn owls also showed a | 126 | excluded the highway in the home-range. Barn owls also showed a | ||
| 127 | positive correlation between the distance to highways and traffic | 127 | positive correlation between the distance to highways and traffic | ||
| 128 | volume, while stone martens only responded to trucks traffic. On | 128 | volume, while stone martens only responded to trucks traffic. On | ||
| 129 | average, we found 7.47 barn owls highway crossings in each 100 | 129 | average, we found 7.47 barn owls highway crossings in each 100 | ||
| 130 | radio-tracking hours while for stone martens this value was almost | 130 | radio-tracking hours while for stone martens this value was almost | ||
| 131 | three times higher (16.5 crossings). The most likely explanation for | 131 | three times higher (16.5 crossings). The most likely explanation for | ||
| 132 | the observed species-specific differences is behavioral. Owls use the | 132 | the observed species-specific differences is behavioral. Owls use the | ||
| 133 | acoustic system to communicate and locate prey, and therefore seem to | 133 | acoustic system to communicate and locate prey, and therefore seem to | ||
| 134 | be more sensitive to the presence of highways and traffic than stone | 134 | be more sensitive to the presence of highways and traffic than stone | ||
| 135 | martens. Low traffic (2000 vehicles/night) may explain the tendency of | 135 | martens. Low traffic (2000 vehicles/night) may explain the tendency of | ||
| 136 | stone martens to cross the highways instead of using the existing | 136 | stone martens to cross the highways instead of using the existing | ||
| 137 | passages (1.96passages/km). Reducing risk of mortality is therefore a | 137 | passages (1.96passages/km). Reducing risk of mortality is therefore a | ||
| 138 | management need. Natural obstacles would force owls to fly higher | 138 | management need. Natural obstacles would force owls to fly higher | ||
| 139 | whilst crossing the highway and will also reduce the disturbance in | 139 | whilst crossing the highway and will also reduce the disturbance in | ||
| 140 | the vicinity, while passages adaptation may improve its use by stone | 140 | the vicinity, while passages adaptation may improve its use by stone | ||
| 141 | martens.", | 141 | martens.", | ||
| 142 | "es": "Several studies have documented that owls and carnivores | 142 | "es": "Several studies have documented that owls and carnivores | ||
| 143 | are two taxa highly impacted by road mortality, but little is known | 143 | are two taxa highly impacted by road mortality, but little is known | ||
| 144 | whether roads attract or repulse individuals. The main goal of this | 144 | whether roads attract or repulse individuals. The main goal of this | ||
| 145 | study was to evaluate the response behavior of two model species (barn | 145 | study was to evaluate the response behavior of two model species (barn | ||
| 146 | owl and stone marten) through the (a) home-ranges shape and size; (b) | 146 | owl and stone marten) through the (a) home-ranges shape and size; (b) | ||
| 147 | effect of traffic volume on the space use patterns; and (c) highway | 147 | effect of traffic volume on the space use patterns; and (c) highway | ||
| 148 | crossings rate. We radio-tracked 10 barn owls and 10 stone martens | 148 | crossings rate. We radio-tracked 10 barn owls and 10 stone martens | ||
| 149 | captured within 2000m of A2 and A6 highway (14900 and 5700 | 149 | captured within 2000m of A2 and A6 highway (14900 and 5700 | ||
| 150 | vehicles/day, respectively) in southern Portugal. Fixes were taken | 150 | vehicles/day, respectively) in southern Portugal. Fixes were taken | ||
| 151 | every 30 minutes from dusk to dawn. Six individuals of each species | 151 | every 30 minutes from dusk to dawn. Six individuals of each species | ||
| 152 | provided data to estimate home-range and the response behaviors were | 152 | provided data to estimate home-range and the response behaviors were | ||
| 153 | not similar. All barn owls had the highway as the home-range (95% | 153 | not similar. All barn owls had the highway as the home-range (95% | ||
| 154 | Kernel estimator) boundary while stone martens randomly included or | 154 | Kernel estimator) boundary while stone martens randomly included or | ||
| 155 | excluded the highway in the home-range. Barn owls also showed a | 155 | excluded the highway in the home-range. Barn owls also showed a | ||
| 156 | positive correlation between the distance to highways and traffic | 156 | positive correlation between the distance to highways and traffic | ||
| 157 | volume, while stone martens only responded to trucks traffic. On | 157 | volume, while stone martens only responded to trucks traffic. On | ||
| 158 | average, we found 7.47 barn owls highway crossings in each 100 | 158 | average, we found 7.47 barn owls highway crossings in each 100 | ||
| 159 | radio-tracking hours while for stone martens this value was almost | 159 | radio-tracking hours while for stone martens this value was almost | ||
| 160 | three times higher (16.5 crossings). The most likely explanation for | 160 | three times higher (16.5 crossings). The most likely explanation for | ||
| 161 | the observed species-specific differences is behavioral. Owls use the | 161 | the observed species-specific differences is behavioral. Owls use the | ||
| 162 | acoustic system to communicate and locate prey, and therefore seem to | 162 | acoustic system to communicate and locate prey, and therefore seem to | ||
| 163 | be more sensitive to the presence of highways and traffic than stone | 163 | be more sensitive to the presence of highways and traffic than stone | ||
| 164 | martens. Low traffic (2000 vehicles/night) may explain the tendency of | 164 | martens. Low traffic (2000 vehicles/night) may explain the tendency of | ||
| 165 | stone martens to cross the highways instead of using the existing | 165 | stone martens to cross the highways instead of using the existing | ||
| 166 | passages (1.96passages/km). Reducing risk of mortality is therefore a | 166 | passages (1.96passages/km). Reducing risk of mortality is therefore a | ||
| 167 | management need. Natural obstacles would force owls to fly higher | 167 | management need. Natural obstacles would force owls to fly higher | ||
| 168 | whilst crossing the highway and will also reduce the disturbance in | 168 | whilst crossing the highway and will also reduce the disturbance in | ||
| 169 | the vicinity, while passages adaptation may improve its use by stone | 169 | the vicinity, while passages adaptation may improve its use by stone | ||
| 170 | martens." | 170 | martens." | ||
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