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En el instante 23 de junio de 2026, 15:51:28 UTC,
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Modificado el valor del campo
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 Fine-scale determinants of vertebrate roadkills across a biodiversity hotspot in Southern Spain.
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| 82 | "notes": "An increasing number of wildlife-vehicle collisions occur | 82 | "notes": "An increasing number of wildlife-vehicle collisions occur | ||
| 83 | each year worldwide, which involves extensive economic costs and | 83 | each year worldwide, which involves extensive economic costs and | ||
| 84 | constitutes one of the main anthropogenic causes of animal mortality. | 84 | constitutes one of the main anthropogenic causes of animal mortality. | ||
| 85 | Because of this, there is an urgent need to identify the factors | 85 | Because of this, there is an urgent need to identify the factors | ||
| 86 | leading to collision hotspots and thus implementing effective | 86 | leading to collision hotspots and thus implementing effective | ||
| 87 | mitigation measures. By using a stratified random sampling survey, we | 87 | mitigation measures. By using a stratified random sampling survey, we | ||
| 88 | investigated the fine-scale determinants of roadkill probability in | 88 | investigated the fine-scale determinants of roadkill probability in | ||
| 89 | small and medium-sized birds and mammals across a country-size region | 89 | small and medium-sized birds and mammals across a country-size region | ||
| 90 | of Southern Spain, Andalusia (87,000 km2), located within a global | 90 | of Southern Spain, Andalusia (87,000 km2), located within a global | ||
| 91 | biodiversity hotspot. During two consecutive seasons, we regularly | 91 | biodiversity hotspot. During two consecutive seasons, we regularly | ||
| 92 | surveyed 45 road transects of 10 km each and characterized the | 92 | surveyed 45 road transects of 10 km each and characterized the | ||
| 93 | site-specific attributes of both roadkill and random points, including | 93 | site-specific attributes of both roadkill and random points, including | ||
| 94 | traffic density, road design (embankments, medians, fences, roadside | 94 | traffic density, road design (embankments, medians, fences, roadside | ||
| 95 | vegetation and distance to curves), and adjacent landscape matrix. | 95 | vegetation and distance to curves), and adjacent landscape matrix. | ||
| 96 | Based on this information, we investigated variation in collision risk | 96 | Based on this information, we investigated variation in collision risk | ||
| 97 | according to landscape and road features, and the life history of the | 97 | according to landscape and road features, and the life history of the | ||
| 98 | affected taxa. Mortality rates of mammals and birds increased with | 98 | affected taxa. Mortality rates of mammals and birds increased with | ||
| 99 | traffic density, and were also significantly affected by the distance | 99 | traffic density, and were also significantly affected by the distance | ||
| 100 | to the nearest curve, slope of embankments, height of roadside | 100 | to the nearest curve, slope of embankments, height of roadside | ||
| 101 | vegetation, and land use adjacent to roads. Road mortality of both | 101 | vegetation, and land use adjacent to roads. Road mortality of both | ||
| 102 | birds and mammals was related to the presence and typology of fences | 102 | birds and mammals was related to the presence and typology of fences | ||
| 103 | and center medians, so more densely vegetated medians and smaller mesh | 103 | and center medians, so more densely vegetated medians and smaller mesh | ||
| 104 | sizes reduced roadkill probability. Overall, our results indicate that | 104 | sizes reduced roadkill probability. Overall, our results indicate that | ||
| 105 | roadkill risk may vary at exceedingly small spatial scales. The | 105 | roadkill risk may vary at exceedingly small spatial scales. The | ||
| 106 | information provided by this extensive survey may be used to identify | 106 | information provided by this extensive survey may be used to identify | ||
| 107 | taxa-specific factors associated to roadkill risk and priority points | 107 | taxa-specific factors associated to roadkill risk and priority points | ||
| 108 | for action. Our findings will therefore be relevant for the design of | 108 | for action. Our findings will therefore be relevant for the design of | ||
| 109 | safer roads for both drivers and wildlife through the application of | 109 | safer roads for both drivers and wildlife through the application of | ||
| 110 | effective mitigation measures.", | 110 | effective mitigation measures.", | ||
| 111 | "notes_translated": { | 111 | "notes_translated": { | ||
| 112 | "en": "An increasing number of wildlife-vehicle collisions occur | 112 | "en": "An increasing number of wildlife-vehicle collisions occur | ||
| 113 | each year worldwide, which involves extensive economic costs and | 113 | each year worldwide, which involves extensive economic costs and | ||
| 114 | constitutes one of the main anthropogenic causes of animal mortality. | 114 | constitutes one of the main anthropogenic causes of animal mortality. | ||
| 115 | Because of this, there is an urgent need to identify the factors | 115 | Because of this, there is an urgent need to identify the factors | ||
| 116 | leading to collision hotspots and thus implementing effective | 116 | leading to collision hotspots and thus implementing effective | ||
| 117 | mitigation measures. By using a stratified random sampling survey, we | 117 | mitigation measures. By using a stratified random sampling survey, we | ||
| 118 | investigated the fine-scale determinants of roadkill probability in | 118 | investigated the fine-scale determinants of roadkill probability in | ||
| 119 | small and medium-sized birds and mammals across a country-size region | 119 | small and medium-sized birds and mammals across a country-size region | ||
| 120 | of Southern Spain, Andalusia (87,000\u00a0km2), located within a | 120 | of Southern Spain, Andalusia (87,000\u00a0km2), located within a | ||
| 121 | global biodiversity hotspot. During two consecutive seasons, we | 121 | global biodiversity hotspot. During two consecutive seasons, we | ||
| 122 | regularly surveyed 45 road transects of 10\u00a0km each and | 122 | regularly surveyed 45 road transects of 10\u00a0km each and | ||
| 123 | characterized the site-specific attributes of both roadkill and random | 123 | characterized the site-specific attributes of both roadkill and random | ||
| 124 | points, including traffic density, road design (embankments, medians, | 124 | points, including traffic density, road design (embankments, medians, | ||
| 125 | fences, roadside vegetation and distance to curves), and adjacent | 125 | fences, roadside vegetation and distance to curves), and adjacent | ||
| 126 | landscape matrix. Based on this information, we investigated variation | 126 | landscape matrix. Based on this information, we investigated variation | ||
| 127 | in collision risk according to landscape and road features, and the | 127 | in collision risk according to landscape and road features, and the | ||
| 128 | life history of the affected taxa. Mortality rates of mammals and | 128 | life history of the affected taxa. Mortality rates of mammals and | ||
| 129 | birds increased with traffic density, and were also significantly | 129 | birds increased with traffic density, and were also significantly | ||
| 130 | affected by the distance to the nearest curve, slope of embankments, | 130 | affected by the distance to the nearest curve, slope of embankments, | ||
| 131 | height of roadside vegetation, and land use adjacent to roads. Road | 131 | height of roadside vegetation, and land use adjacent to roads. Road | ||
| 132 | mortality of both birds and mammals was related to the presence and | 132 | mortality of both birds and mammals was related to the presence and | ||
| 133 | typology of fences and center medians, so more densely vegetated | 133 | typology of fences and center medians, so more densely vegetated | ||
| 134 | medians and smaller mesh sizes reduced roadkill probability. Overall, | 134 | medians and smaller mesh sizes reduced roadkill probability. Overall, | ||
| 135 | our results indicate that roadkill risk may vary at exceedingly small | 135 | our results indicate that roadkill risk may vary at exceedingly small | ||
| 136 | spatial scales. The information provided by this extensive survey may | 136 | spatial scales. The information provided by this extensive survey may | ||
| 137 | be used to identify taxa-specific factors associated to roadkill risk | 137 | be used to identify taxa-specific factors associated to roadkill risk | ||
| 138 | and priority points for action. Our findings will therefore be | 138 | and priority points for action. Our findings will therefore be | ||
| 139 | relevant for the design of safer roads for both drivers and wildlife | 139 | relevant for the design of safer roads for both drivers and wildlife | ||
| 140 | through the application of effective mitigation measures.", | 140 | through the application of effective mitigation measures.", | ||
| 141 | "es": "An increasing number of wildlife-vehicle collisions occur | 141 | "es": "An increasing number of wildlife-vehicle collisions occur | ||
| 142 | each year worldwide, which involves extensive economic costs and | 142 | each year worldwide, which involves extensive economic costs and | ||
| 143 | constitutes one of the main anthropogenic causes of animal mortality. | 143 | constitutes one of the main anthropogenic causes of animal mortality. | ||
| 144 | Because of this, there is an urgent need to identify the factors | 144 | Because of this, there is an urgent need to identify the factors | ||
| 145 | leading to collision hotspots and thus implementing effective | 145 | leading to collision hotspots and thus implementing effective | ||
| 146 | mitigation measures. By using a stratified random sampling survey, we | 146 | mitigation measures. By using a stratified random sampling survey, we | ||
| 147 | investigated the fine-scale determinants of roadkill probability in | 147 | investigated the fine-scale determinants of roadkill probability in | ||
| 148 | small and medium-sized birds and mammals across a country-size region | 148 | small and medium-sized birds and mammals across a country-size region | ||
| 149 | of Southern Spain, Andalusia (87,000 km2), located within a global | 149 | of Southern Spain, Andalusia (87,000 km2), located within a global | ||
| 150 | biodiversity hotspot. During two consecutive seasons, we regularly | 150 | biodiversity hotspot. During two consecutive seasons, we regularly | ||
| 151 | surveyed 45 road transects of 10 km each and characterized the | 151 | surveyed 45 road transects of 10 km each and characterized the | ||
| 152 | site-specific attributes of both roadkill and random points, including | 152 | site-specific attributes of both roadkill and random points, including | ||
| 153 | traffic density, road design (embankments, medians, fences, roadside | 153 | traffic density, road design (embankments, medians, fences, roadside | ||
| 154 | vegetation and distance to curves), and adjacent landscape matrix. | 154 | vegetation and distance to curves), and adjacent landscape matrix. | ||
| 155 | Based on this information, we investigated variation in collision risk | 155 | Based on this information, we investigated variation in collision risk | ||
| 156 | according to landscape and road features, and the life history of the | 156 | according to landscape and road features, and the life history of the | ||
| 157 | affected taxa. Mortality rates of mammals and birds increased with | 157 | affected taxa. Mortality rates of mammals and birds increased with | ||
| 158 | traffic density, and were also significantly affected by the distance | 158 | traffic density, and were also significantly affected by the distance | ||
| 159 | to the nearest curve, slope of embankments, height of roadside | 159 | to the nearest curve, slope of embankments, height of roadside | ||
| 160 | vegetation, and land use adjacent to roads. Road mortality of both | 160 | vegetation, and land use adjacent to roads. Road mortality of both | ||
| 161 | birds and mammals was related to the presence and typology of fences | 161 | birds and mammals was related to the presence and typology of fences | ||
| 162 | and center medians, so more densely vegetated medians and smaller mesh | 162 | and center medians, so more densely vegetated medians and smaller mesh | ||
| 163 | sizes reduced roadkill probability. Overall, our results indicate that | 163 | sizes reduced roadkill probability. Overall, our results indicate that | ||
| 164 | roadkill risk may vary at exceedingly small spatial scales. The | 164 | roadkill risk may vary at exceedingly small spatial scales. The | ||
| 165 | information provided by this extensive survey may be used to identify | 165 | information provided by this extensive survey may be used to identify | ||
| 166 | taxa-specific factors associated to roadkill risk and priority points | 166 | taxa-specific factors associated to roadkill risk and priority points | ||
| 167 | for action. Our findings will therefore be relevant for the design of | 167 | for action. Our findings will therefore be relevant for the design of | ||
| 168 | safer roads for both drivers and wildlife through the application of | 168 | safer roads for both drivers and wildlife through the application of | ||
| 169 | effective mitigation measures." | 169 | effective mitigation measures." | ||
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