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En el instante 23 de junio de 2026, 15:58:44 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 The spatial distribution of animal casualties within a road corridor: implications for roadkill monitoring in the southern Iberian rangelands.
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| 84 | "name": "d50abbc1-54f0-5de9-89d4-dfbe5661c84e", | 84 | "name": "d50abbc1-54f0-5de9-89d4-dfbe5661c84e", | ||
| 85 | "notes": "We assessed wildlife roadkill spatial patterns focusing on | 85 | "notes": "We assessed wildlife roadkill spatial patterns focusing on | ||
| 86 | asphalt roads in southern Spanish oak rangelands | 86 | asphalt roads in southern Spanish oak rangelands | ||
| 87 | (\u201cdehesas\u201d). Four roads in the Sierra Morena range | 87 | (\u201cdehesas\u201d). Four roads in the Sierra Morena range | ||
| 88 | (Andalusia) were surveyed twice during autumn-winter 2009\u20132010 | 88 | (Andalusia) were surveyed twice during autumn-winter 2009\u20132010 | ||
| 89 | and spring-summer 2010. Roadsides were walked on both sides across the | 89 | and spring-summer 2010. Roadsides were walked on both sides across the | ||
| 90 | total road length (53 km; overall length walked per season = 106 km) | 90 | total road length (53 km; overall length walked per season = 106 km) | ||
| 91 | for each field season by 1\u20134 trained observers at \u223c1\u20132 | 91 | for each field season by 1\u20134 trained observers at \u223c1\u20132 | ||
| 92 | km/h. Asphalt surface, road verges/shoulders, runoff ditches and road | 92 | km/h. Asphalt surface, road verges/shoulders, runoff ditches and road | ||
| 93 | banks/slopes (neighboring habitat) were exhaustively inspected for all | 93 | banks/slopes (neighboring habitat) were exhaustively inspected for all | ||
| 94 | dead vertebrates, which were georeferenced and identified. Roadkills | 94 | dead vertebrates, which were georeferenced and identified. Roadkills | ||
| 95 | (N = 396) were classified into 67 species (5 amphibians, 7 reptiles, | 95 | (N = 396) were classified into 67 species (5 amphibians, 7 reptiles, | ||
| 96 | 37 birds and 18 mammals). In total, 128 (32.3%) of all roadkills were | 96 | 37 birds and 18 mammals). In total, 128 (32.3%) of all roadkills were | ||
| 97 | found within the road asphalt lanes, with the remaining two-thirds | 97 | found within the road asphalt lanes, with the remaining two-thirds | ||
| 98 | (268, 67.7%) outside the asphalt lanes. This pattern was consistent | 98 | (268, 67.7%) outside the asphalt lanes. This pattern was consistent | ||
| 99 | regardless of season and several structural attributes of roads. | 99 | regardless of season and several structural attributes of roads. | ||
| 100 | However, vertebrate class was determinant, with more poiquilotherms | 100 | However, vertebrate class was determinant, with more poiquilotherms | ||
| 101 | (amphibians and reptiles) being detected inside asphalt compared to | 101 | (amphibians and reptiles) being detected inside asphalt compared to | ||
| 102 | birds and mammals (off-asphalt casualties were significantly more | 102 | birds and mammals (off-asphalt casualties were significantly more | ||
| 103 | numerous). This is a strong argument in favor of recommending | 103 | numerous). This is a strong argument in favor of recommending | ||
| 104 | surveying roadkill on foot as a main survey method or complementarily | 104 | surveying roadkill on foot as a main survey method or complementarily | ||
| 105 | to vehicle surveys.", | 105 | to vehicle surveys.", | ||
| 106 | "notes_translated": { | 106 | "notes_translated": { | ||
| 107 | "en": "We assessed wildlife roadkill spatial patterns focusing on | 107 | "en": "We assessed wildlife roadkill spatial patterns focusing on | ||
| 108 | asphalt roads in southern Spanish oak rangelands | 108 | asphalt roads in southern Spanish oak rangelands | ||
| 109 | (\u201cdehesas\u201d). Four roads in the Sierra Morena range | 109 | (\u201cdehesas\u201d). Four roads in the Sierra Morena range | ||
| 110 | (Andalusia) were surveyed twice during autumn-winter 2009\u20132010 | 110 | (Andalusia) were surveyed twice during autumn-winter 2009\u20132010 | ||
| 111 | and spring-summer 2010. Roadsides were walked on both sides across the | 111 | and spring-summer 2010. Roadsides were walked on both sides across the | ||
| 112 | total road length (53\u202fkm; overall length walked per | 112 | total road length (53\u202fkm; overall length walked per | ||
| 113 | season\u202f=\u202f106\u202fkm) for each field season by 1\u20134 | 113 | season\u202f=\u202f106\u202fkm) for each field season by 1\u20134 | ||
| 114 | trained observers at \u223c1\u20132\u202fkm/h. Asphalt surface, road | 114 | trained observers at \u223c1\u20132\u202fkm/h. Asphalt surface, road | ||
| 115 | verges/shoulders, runoff ditches and road banks/slopes (neighboring | 115 | verges/shoulders, runoff ditches and road banks/slopes (neighboring | ||
| 116 | habitat) were exhaustively inspected for all dead vertebrates, which | 116 | habitat) were exhaustively inspected for all dead vertebrates, which | ||
| 117 | were georeferenced and identified. Roadkills (N\u202f=\u202f396) were | 117 | were georeferenced and identified. Roadkills (N\u202f=\u202f396) were | ||
| 118 | classified into 67 species (5 amphibians, 7 reptiles, 37 birds and 18 | 118 | classified into 67 species (5 amphibians, 7 reptiles, 37 birds and 18 | ||
| 119 | mammals). In total, 128 (32.3%) of all roadkills were found within the | 119 | mammals). In total, 128 (32.3%) of all roadkills were found within the | ||
| 120 | road asphalt lanes, with the remaining two-thirds (268, 67.7%) outside | 120 | road asphalt lanes, with the remaining two-thirds (268, 67.7%) outside | ||
| 121 | the asphalt lanes. This pattern was consistent regardless of season | 121 | the asphalt lanes. This pattern was consistent regardless of season | ||
| 122 | and several structural attributes of roads. However, vertebrate class | 122 | and several structural attributes of roads. However, vertebrate class | ||
| 123 | was determinant, with more poiquilotherms (amphibians and reptiles) | 123 | was determinant, with more poiquilotherms (amphibians and reptiles) | ||
| 124 | being detected inside asphalt compared to birds and mammals | 124 | being detected inside asphalt compared to birds and mammals | ||
| 125 | (off-asphalt casualties were significantly more numerous). This is a | 125 | (off-asphalt casualties were significantly more numerous). This is a | ||
| 126 | strong argument in favor of recommending surveying roadkill on foot as | 126 | strong argument in favor of recommending surveying roadkill on foot as | ||
| 127 | a main survey method or complementarily to vehicle surveys.", | 127 | a main survey method or complementarily to vehicle surveys.", | ||
| 128 | "es": "We assessed wildlife roadkill spatial patterns focusing on | 128 | "es": "We assessed wildlife roadkill spatial patterns focusing on | ||
| 129 | asphalt roads in southern Spanish oak rangelands | 129 | asphalt roads in southern Spanish oak rangelands | ||
| 130 | (\u201cdehesas\u201d). Four roads in the Sierra Morena range | 130 | (\u201cdehesas\u201d). Four roads in the Sierra Morena range | ||
| 131 | (Andalusia) were surveyed twice during autumn-winter 2009\u20132010 | 131 | (Andalusia) were surveyed twice during autumn-winter 2009\u20132010 | ||
| 132 | and spring-summer 2010. Roadsides were walked on both sides across the | 132 | and spring-summer 2010. Roadsides were walked on both sides across the | ||
| 133 | total road length (53 km; overall length walked per season = 106 km) | 133 | total road length (53 km; overall length walked per season = 106 km) | ||
| 134 | for each field season by 1\u20134 trained observers at \u223c1\u20132 | 134 | for each field season by 1\u20134 trained observers at \u223c1\u20132 | ||
| 135 | km/h. Asphalt surface, road verges/shoulders, runoff ditches and road | 135 | km/h. Asphalt surface, road verges/shoulders, runoff ditches and road | ||
| 136 | banks/slopes (neighboring habitat) were exhaustively inspected for all | 136 | banks/slopes (neighboring habitat) were exhaustively inspected for all | ||
| 137 | dead vertebrates, which were georeferenced and identified. Roadkills | 137 | dead vertebrates, which were georeferenced and identified. Roadkills | ||
| 138 | (N = 396) were classified into 67 species (5 amphibians, 7 reptiles, | 138 | (N = 396) were classified into 67 species (5 amphibians, 7 reptiles, | ||
| 139 | 37 birds and 18 mammals). In total, 128 (32.3%) of all roadkills were | 139 | 37 birds and 18 mammals). In total, 128 (32.3%) of all roadkills were | ||
| 140 | found within the road asphalt lanes, with the remaining two-thirds | 140 | found within the road asphalt lanes, with the remaining two-thirds | ||
| 141 | (268, 67.7%) outside the asphalt lanes. This pattern was consistent | 141 | (268, 67.7%) outside the asphalt lanes. This pattern was consistent | ||
| 142 | regardless of season and several structural attributes of roads. | 142 | regardless of season and several structural attributes of roads. | ||
| 143 | However, vertebrate class was determinant, with more poiquilotherms | 143 | However, vertebrate class was determinant, with more poiquilotherms | ||
| 144 | (amphibians and reptiles) being detected inside asphalt compared to | 144 | (amphibians and reptiles) being detected inside asphalt compared to | ||
| 145 | birds and mammals (off-asphalt casualties were significantly more | 145 | birds and mammals (off-asphalt casualties were significantly more | ||
| 146 | numerous). This is a strong argument in favor of recommending | 146 | numerous). This is a strong argument in favor of recommending | ||
| 147 | surveying roadkill on foot as a main survey method or complementarily | 147 | surveying roadkill on foot as a main survey method or complementarily | ||
| 148 | to vehicle surveys." | 148 | to vehicle surveys." | ||
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