Cambios
En el instante 23 de junio de 2026, 15:59:50 UTC,
-
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 Road effects on species abundance and population trend: a case study on tawny owl.
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| 82 | "notes": "Urbanization and its inherent road network are one of the | 82 | "notes": "Urbanization and its inherent road network are one of the | ||
| 83 | major movements that impulse landscape and biodiversity change, and | 83 | major movements that impulse landscape and biodiversity change, and | ||
| 84 | its effects have yet to be fully understood. Few works focus on the | 84 | its effects have yet to be fully understood. Few works focus on the | ||
| 85 | effect of this urbanization on abundance and population trend of a | 85 | effect of this urbanization on abundance and population trend of a | ||
| 86 | certain species, as this study does, using the tawny owl (Strix aluco) | 86 | certain species, as this study does, using the tawny owl (Strix aluco) | ||
| 87 | as our case study. Although the tawny owl is not threatened at | 87 | as our case study. Although the tawny owl is not threatened at | ||
| 88 | European or global scale, it is often found roadkilled. We studied the | 88 | European or global scale, it is often found roadkilled. We studied the | ||
| 89 | effects of different road types on tawny owl abundance in southern | 89 | effects of different road types on tawny owl abundance in southern | ||
| 90 | Portugal, from 2005 to 2016. In woodlands far from roads, we found | 90 | Portugal, from 2005 to 2016. In woodlands far from roads, we found | ||
| 91 | high tawny owl abundance, a stable population trend, and low variation | 91 | high tawny owl abundance, a stable population trend, and low variation | ||
| 92 | in site occupancy. On the contrary, main roads disrupted habitat | 92 | in site occupancy. On the contrary, main roads disrupted habitat | ||
| 93 | quality for tawny owls\u2014limiting their abundance and site | 93 | quality for tawny owls\u2014limiting their abundance and site | ||
| 94 | occupancy and leading to a negative population trend due to | 94 | occupancy and leading to a negative population trend due to | ||
| 95 | disturbance and/or mortality. Secondary roads did not severely disrupt | 95 | disturbance and/or mortality. Secondary roads did not severely disrupt | ||
| 96 | habitat quality, allowing initial occupation and relatively high | 96 | habitat quality, allowing initial occupation and relatively high | ||
| 97 | densities, yet they may act as ecological traps, revealing instability | 97 | densities, yet they may act as ecological traps, revealing instability | ||
| 98 | in occupation along the breeding season and a negative population | 98 | in occupation along the breeding season and a negative population | ||
| 99 | trend. Tawny owl individuals may settle near secondary roads while | 99 | trend. Tawny owl individuals may settle near secondary roads while | ||
| 100 | waiting for a vacant space in woodlands far from roads (the prime | 100 | waiting for a vacant space in woodlands far from roads (the prime | ||
| 101 | high-quality habitats). To avoid the negative effects of roads on | 101 | high-quality habitats). To avoid the negative effects of roads on | ||
| 102 | tawny owl populations, mitigation efforts should be applied to both | 102 | tawny owl populations, mitigation efforts should be applied to both | ||
| 103 | main and secondary roads.", | 103 | main and secondary roads.", | ||
| 104 | "notes_translated": { | 104 | "notes_translated": { | ||
| 105 | "en": "Urbanization and its inherent road network are one of the | 105 | "en": "Urbanization and its inherent road network are one of the | ||
| 106 | major movements that impulse landscape and biodiversity change, and | 106 | major movements that impulse landscape and biodiversity change, and | ||
| 107 | its effects have yet to be fully understood. Few works focus on the | 107 | its effects have yet to be fully understood. Few works focus on the | ||
| 108 | effect of this urbanization on abundance and population trend of a | 108 | effect of this urbanization on abundance and population trend of a | ||
| 109 | certain species, as this study does, using the tawny owl (Strix aluco) | 109 | certain species, as this study does, using the tawny owl (Strix aluco) | ||
| 110 | as our case study. Although the tawny owl is not threatened at | 110 | as our case study. Although the tawny owl is not threatened at | ||
| 111 | European or global scale, it is often found roadkilled. We studied the | 111 | European or global scale, it is often found roadkilled. We studied the | ||
| 112 | effects of different road types on tawny owl abundance in southern | 112 | effects of different road types on tawny owl abundance in southern | ||
| 113 | Portugal, from 2005 to 2016. In woodlands far from roads, we found | 113 | Portugal, from 2005 to 2016. In woodlands far from roads, we found | ||
| 114 | high tawny owl abundance, a stable population trend, and low variation | 114 | high tawny owl abundance, a stable population trend, and low variation | ||
| 115 | in site occupancy. On the contrary, main roads disrupted habitat | 115 | in site occupancy. On the contrary, main roads disrupted habitat | ||
| 116 | quality for tawny owls\u2014limiting their abundance and site | 116 | quality for tawny owls\u2014limiting their abundance and site | ||
| 117 | occupancy and leading to a negative population trend due to | 117 | occupancy and leading to a negative population trend due to | ||
| 118 | disturbance and/or mortality. Secondary roads did not severely disrupt | 118 | disturbance and/or mortality. Secondary roads did not severely disrupt | ||
| 119 | habitat quality, allowing initial occupation and relatively high | 119 | habitat quality, allowing initial occupation and relatively high | ||
| 120 | densities, yet they may act as ecological traps, revealing instability | 120 | densities, yet they may act as ecological traps, revealing instability | ||
| 121 | in occupation along the breeding season and a negative population | 121 | in occupation along the breeding season and a negative population | ||
| 122 | trend. Tawny owl individuals may settle near secondary roads while | 122 | trend. Tawny owl individuals may settle near secondary roads while | ||
| 123 | waiting for a vacant space in woodlands far from roads (the prime | 123 | waiting for a vacant space in woodlands far from roads (the prime | ||
| 124 | high-quality habitats). To avoid the negative effects of roads on | 124 | high-quality habitats). To avoid the negative effects of roads on | ||
| 125 | tawny owl populations, mitigation efforts should be applied to both | 125 | tawny owl populations, mitigation efforts should be applied to both | ||
| 126 | main and secondary roads.", | 126 | main and secondary roads.", | ||
| 127 | "es": "Urbanization and its inherent road network are one of the | 127 | "es": "Urbanization and its inherent road network are one of the | ||
| 128 | major movements that impulse landscape and biodiversity change, and | 128 | major movements that impulse landscape and biodiversity change, and | ||
| 129 | its effects have yet to be fully understood. Few works focus on the | 129 | its effects have yet to be fully understood. Few works focus on the | ||
| 130 | effect of this urbanization on abundance and population trend of a | 130 | effect of this urbanization on abundance and population trend of a | ||
| 131 | certain species, as this study does, using the tawny owl (Strix aluco) | 131 | certain species, as this study does, using the tawny owl (Strix aluco) | ||
| 132 | as our case study. Although the tawny owl is not threatened at | 132 | as our case study. Although the tawny owl is not threatened at | ||
| 133 | European or global scale, it is often found roadkilled. We studied the | 133 | European or global scale, it is often found roadkilled. We studied the | ||
| 134 | effects of different road types on tawny owl abundance in southern | 134 | effects of different road types on tawny owl abundance in southern | ||
| 135 | Portugal, from 2005 to 2016. In woodlands far from roads, we found | 135 | Portugal, from 2005 to 2016. In woodlands far from roads, we found | ||
| 136 | high tawny owl abundance, a stable population trend, and low variation | 136 | high tawny owl abundance, a stable population trend, and low variation | ||
| 137 | in site occupancy. On the contrary, main roads disrupted habitat | 137 | in site occupancy. On the contrary, main roads disrupted habitat | ||
| 138 | quality for tawny owls\u2014limiting their abundance and site | 138 | quality for tawny owls\u2014limiting their abundance and site | ||
| 139 | occupancy and leading to a negative population trend due to | 139 | occupancy and leading to a negative population trend due to | ||
| 140 | disturbance and/or mortality. Secondary roads did not severely disrupt | 140 | disturbance and/or mortality. Secondary roads did not severely disrupt | ||
| 141 | habitat quality, allowing initial occupation and relatively high | 141 | habitat quality, allowing initial occupation and relatively high | ||
| 142 | densities, yet they may act as ecological traps, revealing instability | 142 | densities, yet they may act as ecological traps, revealing instability | ||
| 143 | in occupation along the breeding season and a negative population | 143 | in occupation along the breeding season and a negative population | ||
| 144 | trend. Tawny owl individuals may settle near secondary roads while | 144 | trend. Tawny owl individuals may settle near secondary roads while | ||
| 145 | waiting for a vacant space in woodlands far from roads (the prime | 145 | waiting for a vacant space in woodlands far from roads (the prime | ||
| 146 | high-quality habitats). To avoid the negative effects of roads on | 146 | high-quality habitats). To avoid the negative effects of roads on | ||
| 147 | tawny owl populations, mitigation efforts should be applied to both | 147 | tawny owl populations, mitigation efforts should be applied to both | ||
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