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En el instante 25 de junio de 2026, 12:28:32 UTC,
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a2026-06-25
en Are motorway wildlife passages worth building? Vertebrate use of road-crossing structures on a Spanish motorway. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Are motorway wildlife passages worth building? Vertebrate use of road-crossing structures on a Spanish motorway.
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| 83 | costly mitigation measures to offset the barrier effect produced on | 97 | costly mitigation measures to offset the barrier effect produced on | ||
| 84 | local fauna, despite the scarcity of data on the effectiveness of such | 98 | local fauna, despite the scarcity of data on the effectiveness of such | ||
| 85 | mitigation measures. In this study, we evaluate the utility of | 99 | mitigation measures. In this study, we evaluate the utility of | ||
| 86 | different types of crossing structures. Vertebrate use of 43 | 100 | different types of crossing structures. Vertebrate use of 43 | ||
| 87 | transverse crossing structures along the A-52 motorway (north-western | 101 | transverse crossing structures along the A-52 motorway (north-western | ||
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| 89 | passages (9), wildlife-adapted box culverts (7), functional passages | 103 | passages (9), wildlife-adapted box culverts (7), functional passages | ||
| 90 | (6 overpasses, 7 underpasses) and culverts (14), with marble dust | 104 | (6 overpasses, 7 underpasses) and culverts (14), with marble dust | ||
| 91 | being used to record animal tracks. A total of 424 track-days were | 105 | being used to record animal tracks. A total of 424 track-days were | ||
| 92 | recorded, with most of the larger vertebrate groups present in the | 106 | recorded, with most of the larger vertebrate groups present in the | ||
| 93 | area being detected. All crossing structure types were used by | 107 | area being detected. All crossing structure types were used by | ||
| 94 | animals, although the intensity of use varied significantly among them | 108 | animals, although the intensity of use varied significantly among them | ||
| 95 | (Kruskal\u2013Wallis test, p<0.05); culverts were used less frequently | 109 | (Kruskal\u2013Wallis test, p<0.05); culverts were used less frequently | ||
| 96 | than other structures. Crossing structure type and width were | 110 | than other structures. Crossing structure type and width were | ||
| 97 | identified as the most important factors in their selection for use. | 111 | identified as the most important factors in their selection for use. | ||
| 98 | Wildlife passages and adapted culverts allowed crossing by certain | 112 | Wildlife passages and adapted culverts allowed crossing by certain | ||
| 99 | species (wild boar, roe deer, Eurasian badger), which do not tend to | 113 | species (wild boar, roe deer, Eurasian badger), which do not tend to | ||
| 100 | cross elsewhere. These results highlight the importance of using both | 114 | cross elsewhere. These results highlight the importance of using both | ||
| 101 | mixed-type structures and wildlife passages in reducing the barrier | 115 | mixed-type structures and wildlife passages in reducing the barrier | ||
| 102 | effect of roads.\n Palabras clave: Motorway", | 116 | effect of roads.\n Palabras clave: Motorway", | ||
| 103 | "notes_translated": { | 117 | "notes_translated": { | ||
| 104 | "en": "Numerous road and railway construction projects include | 118 | "en": "Numerous road and railway construction projects include | ||
| 105 | costly mitigation measures to offset the barrier effect produced on | 119 | costly mitigation measures to offset the barrier effect produced on | ||
| 106 | local fauna, despite the scarcity of data on the effectiveness of such | 120 | local fauna, despite the scarcity of data on the effectiveness of such | ||
| 107 | mitigation measures. In this study, we evaluate the utility of | 121 | mitigation measures. In this study, we evaluate the utility of | ||
| 108 | different types of crossing structures. Vertebrate use of 43 | 122 | different types of crossing structures. Vertebrate use of 43 | ||
| 109 | transverse crossing structures along the A-52 motorway (north-western | 123 | transverse crossing structures along the A-52 motorway (north-western | ||
| 110 | Spain) was studied during spring 2001. Research centered on wildlife | 124 | Spain) was studied during spring 2001. Research centered on wildlife | ||
| 111 | passages (9), wildlife-adapted box culverts (7), functional passages | 125 | passages (9), wildlife-adapted box culverts (7), functional passages | ||
| 112 | (6 overpasses, 7 underpasses) and culverts (14), with marble dust | 126 | (6 overpasses, 7 underpasses) and culverts (14), with marble dust | ||
| 113 | being used to record animal tracks. A total of 424 track-days were | 127 | being used to record animal tracks. A total of 424 track-days were | ||
| 114 | recorded, with most of the larger vertebrate groups present in the | 128 | recorded, with most of the larger vertebrate groups present in the | ||
| 115 | area being detected. All crossing structure types were used by | 129 | area being detected. All crossing structure types were used by | ||
| 116 | animals, although the intensity of use varied significantly among them | 130 | animals, although the intensity of use varied significantly among them | ||
| 117 | (Kruskal\u2013Wallis test, p<0.05); culverts were used less frequently | 131 | (Kruskal\u2013Wallis test, p<0.05); culverts were used less frequently | ||
| 118 | than", | 132 | than", | ||
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| 120 | costly mitigation measures to offset the barrier effect produced on | 134 | costly mitigation measures to offset the barrier effect produced on | ||
| 121 | local fauna, despite the scarcity of data on the effectiveness of such | 135 | local fauna, despite the scarcity of data on the effectiveness of such | ||
| 122 | mitigation measures. In this study, we evaluate the utility of | 136 | mitigation measures. In this study, we evaluate the utility of | ||
| 123 | different types of crossing structures. Vertebrate use of 43 | 137 | different types of crossing structures. Vertebrate use of 43 | ||
| 124 | transverse crossing structures along the A-52 motorway (north-western | 138 | transverse crossing structures along the A-52 motorway (north-western | ||
| 125 | Spain) was studied during spring 2001. Research centered on wildlife | 139 | Spain) was studied during spring 2001. Research centered on wildlife | ||
| 126 | passages (9), wildlife-adapted box culverts (7), functional passages | 140 | passages (9), wildlife-adapted box culverts (7), functional passages | ||
| 127 | (6 overpasses, 7 underpasses) and culverts (14), with marble dust | 141 | (6 overpasses, 7 underpasses) and culverts (14), with marble dust | ||
| 128 | being used to record animal tracks. A total of 424 track-days were | 142 | being used to record animal tracks. A total of 424 track-days were | ||
| 129 | recorded, with most of the larger vertebrate groups present in the | 143 | recorded, with most of the larger vertebrate groups present in the | ||
| 130 | area being detected. All crossing structure types were used by | 144 | area being detected. All crossing structure types were used by | ||
| 131 | animals, although the intensity of use varied significantly among them | 145 | animals, although the intensity of use varied significantly among them | ||
| 132 | (Kruskal\u2013Wallis test, p<0.05); culverts were used less frequently | 146 | (Kruskal\u2013Wallis test, p<0.05); culverts were used less frequently | ||
| 133 | than other structures. Crossing structure type and width were | 147 | than other structures. Crossing structure type and width were | ||
| 134 | identified as the most important factors in their selection for use. | 148 | identified as the most important factors in their selection for use. | ||
| 135 | Wildlife passages and adapted culverts allowed crossing by certain | 149 | Wildlife passages and adapted culverts allowed crossing by certain | ||
| 136 | species (wild boar, roe deer, Eurasian badger), which do not tend to | 150 | species (wild boar, roe deer, Eurasian badger), which do not tend to | ||
| 137 | cross elsewhere. These results highlight the importance of using both | 151 | cross elsewhere. These results highlight the importance of using both | ||
| 138 | mixed-type structures and wildlife passages in reducing the barrier | 152 | mixed-type structures and wildlife passages in reducing the barrier | ||
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| 291 | "title": "Are motorway wildlife passages worth building? Vertebrate | 305 | "title": "Are motorway wildlife passages worth building? Vertebrate | ||
| 292 | use of road-crossing structures on a Spanish motorway.", | 306 | use of road-crossing structures on a Spanish motorway.", | ||
| 293 | "title_translated": { | 307 | "title_translated": { | ||
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| 295 | "es": "Are motorway wildlife passages worth building? Vertebrate | 309 | "es": "Are motorway wildlife passages worth building? Vertebrate | ||
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