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En el instante 23 de junio de 2026, 16:00:49 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 Overcoming the barrier effect of roads - How effective are mitigation strategies?
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| 59 | Transportation. Vol. 7", | 59 | Transportation. Vol. 7", | ||
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| 80 | "notes": "Roads, railways and other linear infrastructure are | 80 | "notes": "Roads, railways and other linear infrastructure are | ||
| 81 | pervasive components of most landscapes throughout the world. Combined | 81 | pervasive components of most landscapes throughout the world. Combined | ||
| 82 | with the effect of vehicles, they have the potential to cause | 82 | with the effect of vehicles, they have the potential to cause | ||
| 83 | mortality in wildlife, severely disrupt animal movement and increase | 83 | mortality in wildlife, severely disrupt animal movement and increase | ||
| 84 | the risk of local extinction. Management agencies and conservation | 84 | the risk of local extinction. Management agencies and conservation | ||
| 85 | organisations currently spend considerable amounts of money annually | 85 | organisations currently spend considerable amounts of money annually | ||
| 86 | on engineering solutions to increase the permeability of roads for | 86 | on engineering solutions to increase the permeability of roads for | ||
| 87 | wildlife. We evaluated the use and effectiveness of wildlife crossing | 87 | wildlife. We evaluated the use and effectiveness of wildlife crossing | ||
| 88 | structures (e.g. tunnels, culverts, overpasses) by reviewing studies | 88 | structures (e.g. tunnels, culverts, overpasses) by reviewing studies | ||
| 89 | published in the refereed scientific literature, conference | 89 | published in the refereed scientific literature, conference | ||
| 90 | proceedings and consultant reports. We evaluated the scientific rigour | 90 | proceedings and consultant reports. We evaluated the scientific rigour | ||
| 91 | and methodology of studies, the extent to which studies demonstrated | 91 | and methodology of studies, the extent to which studies demonstrated | ||
| 92 | an increase in permeability, the detail included in the reporting and | 92 | an increase in permeability, the detail included in the reporting and | ||
| 93 | the extent to which population, community and ecosystem effects were | 93 | the extent to which population, community and ecosystem effects were | ||
| 94 | shown. One hundred and twenty three studies were reviewed and all | 94 | shown. One hundred and twenty three studies were reviewed and all | ||
| 95 | except two found an effect at the level of the individual animal. Two | 95 | except two found an effect at the level of the individual animal. Two | ||
| 96 | studies demonstrated a positive effect for the population and thus | 96 | studies demonstrated a positive effect for the population and thus | ||
| 97 | overall, the effectiveness of mitigation measures at reducing the risk | 97 | overall, the effectiveness of mitigation measures at reducing the risk | ||
| 98 | of population extinction remains unclear. The level of scientific | 98 | of population extinction remains unclear. The level of scientific | ||
| 99 | rigour, amount of replication and description of adjacent habitat and | 99 | rigour, amount of replication and description of adjacent habitat and | ||
| 100 | animal populations varied considerably among studies, in many cases | 100 | animal populations varied considerably among studies, in many cases | ||
| 101 | limiting the level of inference that could be made. In the context of | 101 | limiting the level of inference that could be made. In the context of | ||
| 102 | evaluation, we propose that a clear distinction be made between | 102 | evaluation, we propose that a clear distinction be made between | ||
| 103 | \u201cuse\u201d and \u201ceffectiveness\u201d of a wildlife crossing | 103 | \u201cuse\u201d and \u201ceffectiveness\u201d of a wildlife crossing | ||
| 104 | structure. The use of a structure may be broadly defined as the rate | 104 | structure. The use of a structure may be broadly defined as the rate | ||
| 105 | of detections of individuals or species, while effectiveness relates | 105 | of detections of individuals or species, while effectiveness relates | ||
| 106 | to a specific question or the goal of mitigation. A large amount of | 106 | to a specific question or the goal of mitigation. A large amount of | ||
| 107 | effort has conclusively shown that crossing structures are used by | 107 | effort has conclusively shown that crossing structures are used by | ||
| 108 | many species of wildlife. The long-term success of mitigation will | 108 | many species of wildlife. The long-term success of mitigation will | ||
| 109 | ultimately depend on their effectiveness \u2013 i.e. to what extent | 109 | ultimately depend on their effectiveness \u2013 i.e. to what extent | ||
| 110 | have they mitigated the barrier effect of roads and has this prevented | 110 | have they mitigated the barrier effect of roads and has this prevented | ||
| 111 | the local extinction of populations due to road effects? The next | 111 | the local extinction of populations due to road effects? The next | ||
| 112 | phase of research must focus more explicitly on quantifying their | 112 | phase of research must focus more explicitly on quantifying their | ||
| 113 | effectiveness, relative to location- and species-specific goals.", | 113 | effectiveness, relative to location- and species-specific goals.", | ||
| 114 | "notes_translated": { | 114 | "notes_translated": { | ||
| 115 | "en": "Roads, railways and other linear infrastructure are | 115 | "en": "Roads, railways and other linear infrastructure are | ||
| 116 | pervasive components of most landscapes throughout the world. Combined | 116 | pervasive components of most landscapes throughout the world. Combined | ||
| 117 | with the effect of vehicles, they have the potential to cause | 117 | with the effect of vehicles, they have the potential to cause | ||
| 118 | mortality in wildlife, severely disrupt animal movement and increase | 118 | mortality in wildlife, severely disrupt animal movement and increase | ||
| 119 | the risk of local extinction. Management agencies and conservation | 119 | the risk of local extinction. Management agencies and conservation | ||
| 120 | organisations currently spend considerable amounts of money annually | 120 | organisations currently spend considerable amounts of money annually | ||
| 121 | on engineering solutions to increase the permeability of roads for | 121 | on engineering solutions to increase the permeability of roads for | ||
| 122 | wildlife. We evaluated the use and effectiveness of wildlife crossing | 122 | wildlife. We evaluated the use and effectiveness of wildlife crossing | ||
| 123 | structures (e.g. tunnels, culverts, overpasses) by reviewing studies | 123 | structures (e.g. tunnels, culverts, overpasses) by reviewing studies | ||
| 124 | published in the refereed scientific literature, conference | 124 | published in the refereed scientific literature, conference | ||
| 125 | proceedings and consultant reports. We evaluated the scientific rigour | 125 | proceedings and consultant reports. We evaluated the scientific rigour | ||
| 126 | and methodology of studies, the extent to which studies demonstrated | 126 | and methodology of studies, the extent to which studies demonstrated | ||
| 127 | an increase in permeability, the detail included in the reporting and | 127 | an increase in permeability, the detail included in the reporting and | ||
| 128 | the extent to which population, community and ecosystem effects were | 128 | the extent to which population, community and ecosystem effects were | ||
| 129 | shown. One hundred and twenty three studies were reviewed and all | 129 | shown. One hundred and twenty three studies were reviewed and all | ||
| 130 | except two found an effect at the level of the individual animal. Two | 130 | except two found an effect at the level of the individual animal. Two | ||
| 131 | studies demonstrated a positive effect for the population and thus | 131 | studies demonstrated a positive effect for the population and thus | ||
| 132 | overall, the effectiveness of mitigation measures at reducing the risk | 132 | overall, the effectiveness of mitigation measures at reducing the risk | ||
| 133 | of population extinction remains unclear. The level of scientific | 133 | of population extinction remains unclear. The level of scientific | ||
| 134 | rigour, amount of replication and description of adjacent habitat and | 134 | rigour, amount of replication and description of adjacent habitat and | ||
| 135 | animal populations varied considerably among studies, in many cases | 135 | animal populations varied considerably among studies, in many cases | ||
| 136 | limiting the level of inference that could be made. In the context of | 136 | limiting the level of inference that could be made. In the context of | ||
| 137 | evaluation, we propose that a clear distinction be made between | 137 | evaluation, we propose that a clear distinction be made between | ||
| 138 | \u201cuse\u201d and \u201ceffectiveness\u201d of a wildlife crossing | 138 | \u201cuse\u201d and \u201ceffectiveness\u201d of a wildlife crossing | ||
| 139 | structure. The use of a structure may be broadly defined as the rate | 139 | structure. The use of a structure may be broadly defined as the rate | ||
| 140 | of detections of individuals or species, while effectiveness relates | 140 | of detections of individuals or species, while effectiveness relates | ||
| 141 | to a specific question or the goal of mitigation. A large amount of | 141 | to a specific question or the goal of mitigation. A large amount of | ||
| 142 | effort has conclusively shown that crossing structures are used by | 142 | effort has conclusively shown that crossing structures are used by | ||
| 143 | many species of wildlife. The long-term success of mitigation will | 143 | many species of wildlife. The long-term success of mitigation will | ||
| 144 | ultimately depend on their effectiveness \u2013 i.e. to what extent | 144 | ultimately depend on their effectiveness \u2013 i.e. to what extent | ||
| 145 | have they mitigated the barrier effect of roads and has this prevented | 145 | have they mitigated the barrier effect of roads and has this prevented | ||
| 146 | the local extinction of populations due to road effects? The next | 146 | the local extinction of populations due to road effects? The next | ||
| 147 | phase of research must focus more explicitly on quantifying their | 147 | phase of research must focus more explicitly on quantifying their | ||
| 148 | effectiveness, relative to location- and species-specific goals.", | 148 | effectiveness, relative to location- and species-specific goals.", | ||
| 149 | "es": "Roads, railways and other linear infrastructure are | 149 | "es": "Roads, railways and other linear infrastructure are | ||
| 150 | pervasive components of most landscapes throughout the world. Combined | 150 | pervasive components of most landscapes throughout the world. Combined | ||
| 151 | with the effect of vehicles, they have the potential to cause | 151 | with the effect of vehicles, they have the potential to cause | ||
| 152 | mortality in wildlife, severely disrupt animal movement and increase | 152 | mortality in wildlife, severely disrupt animal movement and increase | ||
| 153 | the risk of local extinction. Management agencies and conservation | 153 | the risk of local extinction. Management agencies and conservation | ||
| 154 | organisations currently spend considerable amounts of money annually | 154 | organisations currently spend considerable amounts of money annually | ||
| 155 | on engineering solutions to increase the permeability of roads for | 155 | on engineering solutions to increase the permeability of roads for | ||
| 156 | wildlife. We evaluated the use and effectiveness of wildlife crossing | 156 | wildlife. We evaluated the use and effectiveness of wildlife crossing | ||
| 157 | structures (e.g. tunnels, culverts, overpasses) by reviewing studies | 157 | structures (e.g. tunnels, culverts, overpasses) by reviewing studies | ||
| 158 | published in the refereed scientific literature, conference | 158 | published in the refereed scientific literature, conference | ||
| 159 | proceedings and consultant reports. We evaluated the scientific rigour | 159 | proceedings and consultant reports. We evaluated the scientific rigour | ||
| 160 | and methodology of studies, the extent to which studies demonstrated | 160 | and methodology of studies, the extent to which studies demonstrated | ||
| 161 | an increase in permeability, the detail included in the reporting and | 161 | an increase in permeability, the detail included in the reporting and | ||
| 162 | the extent to which population, community and ecosystem effects were | 162 | the extent to which population, community and ecosystem effects were | ||
| 163 | shown. One hundred and twenty three studies were reviewed and all | 163 | shown. One hundred and twenty three studies were reviewed and all | ||
| 164 | except two found an effect at the level of the individual animal. Two | 164 | except two found an effect at the level of the individual animal. Two | ||
| 165 | studies demonstrated a positive effect for the population and thus | 165 | studies demonstrated a positive effect for the population and thus | ||
| 166 | overall, the effectiveness of mitigation measures at reducing the risk | 166 | overall, the effectiveness of mitigation measures at reducing the risk | ||
| 167 | of population extinction remains unclear. The level of scientific | 167 | of population extinction remains unclear. The level of scientific | ||
| 168 | rigour, amount of replication and description of adjacent habitat and | 168 | rigour, amount of replication and description of adjacent habitat and | ||
| 169 | animal populations varied considerably among studies, in many cases | 169 | animal populations varied considerably among studies, in many cases | ||
| 170 | limiting the level of inference that could be made. In the context of | 170 | limiting the level of inference that could be made. In the context of | ||
| 171 | evaluation, we propose that a clear distinction be made between | 171 | evaluation, we propose that a clear distinction be made between | ||
| 172 | \u201cuse\u201d and \u201ceffectiveness\u201d of a wildlife crossing | 172 | \u201cuse\u201d and \u201ceffectiveness\u201d of a wildlife crossing | ||
| 173 | structure. The use of a structure may be broadly defined as the rate | 173 | structure. The use of a structure may be broadly defined as the rate | ||
| 174 | of detections of individuals or species, while effectiveness relates | 174 | of detections of individuals or species, while effectiveness relates | ||
| 175 | to a specific question or the goal of mitigation. A large amount of | 175 | to a specific question or the goal of mitigation. A large amount of | ||
| 176 | effort has conclusively shown that crossing structures are used by | 176 | effort has conclusively shown that crossing structures are used by | ||
| 177 | many species of wildlife. The long-term success of mitigation will | 177 | many species of wildlife. The long-term success of mitigation will | ||
| 178 | ultimately depend on their effectiveness \u2013 i.e. to what extent | 178 | ultimately depend on their effectiveness \u2013 i.e. to what extent | ||
| 179 | have they mitigated the barrier effect of roads and has this prevented | 179 | have they mitigated the barrier effect of roads and has this prevented | ||
| 180 | the local extinction of populations due to road effects? The next | 180 | the local extinction of populations due to road effects? The next | ||
| 181 | phase of research must focus more explicitly on quantifying their | 181 | phase of research must focus more explicitly on quantifying their | ||
| 182 | effectiveness, relative to location- and species-specific goals." | 182 | effectiveness, relative to location- and species-specific goals." | ||
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| 219 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | 219 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | ||
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