Cambios
En el instante 23 de junio de 2026, 16:09:45 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 How long do the dead survive on the road? Carcass persistence probability and implications for road-kill monitoring surveys.
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| 77 | "notes": "Road mortality is probably the best-known and visible | 77 | "notes": "Road mortality is probably the best-known and visible | ||
| 78 | impact of roads upon wildlife. Although several factors influence | 78 | impact of roads upon wildlife. Although several factors influence | ||
| 79 | road-kill counts, carcass persistence time is considered the most | 79 | road-kill counts, carcass persistence time is considered the most | ||
| 80 | important determinant underlying underestimates of road mortality. The | 80 | important determinant underlying underestimates of road mortality. The | ||
| 81 | present study aims to describe and model carcass persistence | 81 | present study aims to describe and model carcass persistence | ||
| 82 | variability on the road for different taxonomic groups under different | 82 | variability on the road for different taxonomic groups under different | ||
| 83 | environmental conditions throughout the year; and also to assess the | 83 | environmental conditions throughout the year; and also to assess the | ||
| 84 | effect of sampling frequency on the relative variation in road-kill | 84 | effect of sampling frequency on the relative variation in road-kill | ||
| 85 | estimates registered within a survey.\n Daily surveys of road-killed | 85 | estimates registered within a survey.\n Daily surveys of road-killed | ||
| 86 | vertebrates were conducted over one year along four road sections with | 86 | vertebrates were conducted over one year along four road sections with | ||
| 87 | different traffic volumes. Survival analysis was then used to i) | 87 | different traffic volumes. Survival analysis was then used to i) | ||
| 88 | describe carcass persistence timings for overall and for specific | 88 | describe carcass persistence timings for overall and for specific | ||
| 89 | animal groups; ii) assess optimal sampling designs according to | 89 | animal groups; ii) assess optimal sampling designs according to | ||
| 90 | research objectives; and iii) model the influence of road, animal and | 90 | research objectives; and iii) model the influence of road, animal and | ||
| 91 | weather factors on carcass persistence probabilities. Most animal | 91 | weather factors on carcass persistence probabilities. Most animal | ||
| 92 | carcasses persisted on the road for the first day only, with some | 92 | carcasses persisted on the road for the first day only, with some | ||
| 93 | groups disappearing at very high rates. The advisable periodicity of | 93 | groups disappearing at very high rates. The advisable periodicity of | ||
| 94 | road monitoring that minimizes bias in road mortality estimates is | 94 | road monitoring that minimizes bias in road mortality estimates is | ||
| 95 | daily monitoring for bats (in the morning) and lizards (in the | 95 | daily monitoring for bats (in the morning) and lizards (in the | ||
| 96 | afternoon), daily monitoring for toads, small birds, small mammals, | 96 | afternoon), daily monitoring for toads, small birds, small mammals, | ||
| 97 | snakes, salamanders, and lagomorphs; 1 day-interval (alternate days) | 97 | snakes, salamanders, and lagomorphs; 1 day-interval (alternate days) | ||
| 98 | for large birds, birds of prey, hedgehogs, and freshwater turtles; and | 98 | for large birds, birds of prey, hedgehogs, and freshwater turtles; and | ||
| 99 | 2 day-interval for carnivores. Multiple factors influenced the | 99 | 2 day-interval for carnivores. Multiple factors influenced the | ||
| 100 | persistence probabilities of vertebrate carcasses on the road. | 100 | persistence probabilities of vertebrate carcasses on the road. | ||
| 101 | Overall, the persistence was much lower for small animals, on roads | 101 | Overall, the persistence was much lower for small animals, on roads | ||
| 102 | with lower traffic volumes, for carcasses located on road lanes, and | 102 | with lower traffic volumes, for carcasses located on road lanes, and | ||
| 103 | during humid conditions and high temperatures during the wet season | 103 | during humid conditions and high temperatures during the wet season | ||
| 104 | and dry seasons, respectively.\n The guidance given here on monitoring | 104 | and dry seasons, respectively.\n The guidance given here on monitoring | ||
| 105 | frequencies is particularly relevant to provide conservation and | 105 | frequencies is particularly relevant to provide conservation and | ||
| 106 | transportation agencies with accurate numbers of road-kills, realistic | 106 | transportation agencies with accurate numbers of road-kills, realistic | ||
| 107 | mitigation measures, and detailed designs for road monitoring | 107 | mitigation measures, and detailed designs for road monitoring | ||
| 108 | programs.", | 108 | programs.", | ||
| 109 | "notes_translated": { | 109 | "notes_translated": { | ||
| 110 | "en": "Background Road mortality is probably the best-known and | 110 | "en": "Background Road mortality is probably the best-known and | ||
| 111 | visible impact of roads upon wildlife. Although several factors | 111 | visible impact of roads upon wildlife. Although several factors | ||
| 112 | influence road-kill counts, carcass persistence time is considered the | 112 | influence road-kill counts, carcass persistence time is considered the | ||
| 113 | most important determinant underlying underestimates of road | 113 | most important determinant underlying underestimates of road | ||
| 114 | mortality. The present study aims to describe and model carcass | 114 | mortality. The present study aims to describe and model carcass | ||
| 115 | persistence variability on the road for different taxonomic groups | 115 | persistence variability on the road for different taxonomic groups | ||
| 116 | under different environmental conditions throughout the year; and also | 116 | under different environmental conditions throughout the year; and also | ||
| 117 | to assess the effect of sampling frequency on the relative variation | 117 | to assess the effect of sampling frequency on the relative variation | ||
| 118 | in road-kill estimates registered within a survey. | 118 | in road-kill estimates registered within a survey. | ||
| 119 | Methodology/Principal Findings Daily surveys of road-killed | 119 | Methodology/Principal Findings Daily surveys of road-killed | ||
| 120 | vertebrates were conducted over one year along four road sections with | 120 | vertebrates were conducted over one year along four road sections with | ||
| 121 | different traffic volumes. Survival analysis was then used to i) | 121 | different traffic volumes. Survival analysis was then used to i) | ||
| 122 | describe carcass persistence timings for overall and for specific | 122 | describe carcass persistence timings for overall and for specific | ||
| 123 | animal groups; ii) assess optimal sampling designs according to | 123 | animal groups; ii) assess optimal sampling designs according to | ||
| 124 | research objectives; and iii) model the influence of road, animal and | 124 | research objectives; and iii) model the influence of road, animal and | ||
| 125 | weather factors on carcass persistence probabilities. Most animal | 125 | weather factors on carcass persistence probabilities. Most animal | ||
| 126 | carcasses persisted on the road for the first day only, with some | 126 | carcasses persisted on the road for the first day only, with some | ||
| 127 | groups disappearing at very high rates. The advisable periodicity of | 127 | groups disappearing at very high rates. The advisable periodicity of | ||
| 128 | road monitoring that minimizes bias in road mortality estimates is | 128 | road monitoring that minimizes bias in road mortality estimates is | ||
| 129 | daily monitoring for bats (in the morning) and lizards (in the | 129 | daily monitoring for bats (in the morning) and lizards (in the | ||
| 130 | afternoon), daily monitoring for toads, small birds, small mammals, | 130 | afternoon), daily monitoring for toads, small birds, small mammals, | ||
| 131 | snakes, salamanders, and lagomorphs; 1 day-interval (alternate days) | 131 | snakes, salamanders, and lagomorphs; 1 day-interval (alternate days) | ||
| 132 | for large birds, birds of prey, hedgehogs, and freshwater turtles; and | 132 | for large birds, birds of prey, hedgehogs, and freshwater turtles; and | ||
| 133 | 2 day-interval for carnivores. Multiple factors influenced the | 133 | 2 day-interval for carnivores. Multiple factors influenced the | ||
| 134 | persistence probabilities of vertebrate carcasses on the road. | 134 | persistence probabilities of vertebrate carcasses on the road. | ||
| 135 | Overall, the persistence was much lower for small", | 135 | Overall, the persistence was much lower for small", | ||
| 136 | "es": "Road mortality is probably the best-known and visible | 136 | "es": "Road mortality is probably the best-known and visible | ||
| 137 | impact of roads upon wildlife. Although several factors influence | 137 | impact of roads upon wildlife. Although several factors influence | ||
| 138 | road-kill counts, carcass persistence time is considered the most | 138 | road-kill counts, carcass persistence time is considered the most | ||
| 139 | important determinant underlying underestimates of road mortality. The | 139 | important determinant underlying underestimates of road mortality. The | ||
| 140 | present study aims to describe and model carcass persistence | 140 | present study aims to describe and model carcass persistence | ||
| 141 | variability on the road for different taxonomic groups under different | 141 | variability on the road for different taxonomic groups under different | ||
| 142 | environmental conditions throughout the year; and also to assess the | 142 | environmental conditions throughout the year; and also to assess the | ||
| 143 | effect of sampling frequency on the relative variation in road-kill | 143 | effect of sampling frequency on the relative variation in road-kill | ||
| 144 | estimates registered within a survey.\n Daily surveys of road-killed | 144 | estimates registered within a survey.\n Daily surveys of road-killed | ||
| 145 | vertebrates were conducted over one year along four road sections with | 145 | vertebrates were conducted over one year along four road sections with | ||
| 146 | different traffic volumes. Survival analysis was then used to i) | 146 | different traffic volumes. Survival analysis was then used to i) | ||
| 147 | describe carcass persistence timings for overall and for specific | 147 | describe carcass persistence timings for overall and for specific | ||
| 148 | animal groups; ii) assess optimal sampling designs according to | 148 | animal groups; ii) assess optimal sampling designs according to | ||
| 149 | research objectives; and iii) model the influence of road, animal and | 149 | research objectives; and iii) model the influence of road, animal and | ||
| 150 | weather factors on carcass persistence probabilities. Most animal | 150 | weather factors on carcass persistence probabilities. Most animal | ||
| 151 | carcasses persisted on the road for the first day only, with some | 151 | carcasses persisted on the road for the first day only, with some | ||
| 152 | groups disappearing at very high rates. The advisable periodicity of | 152 | groups disappearing at very high rates. The advisable periodicity of | ||
| 153 | road monitoring that minimizes bias in road mortality estimates is | 153 | road monitoring that minimizes bias in road mortality estimates is | ||
| 154 | daily monitoring for bats (in the morning) and lizards (in the | 154 | daily monitoring for bats (in the morning) and lizards (in the | ||
| 155 | afternoon), daily monitoring for toads, small birds, small mammals, | 155 | afternoon), daily monitoring for toads, small birds, small mammals, | ||
| 156 | snakes, salamanders, and lagomorphs; 1 day-interval (alternate days) | 156 | snakes, salamanders, and lagomorphs; 1 day-interval (alternate days) | ||
| 157 | for large birds, birds of prey, hedgehogs, and freshwater turtles; and | 157 | for large birds, birds of prey, hedgehogs, and freshwater turtles; and | ||
| 158 | 2 day-interval for carnivores. Multiple factors influenced the | 158 | 2 day-interval for carnivores. Multiple factors influenced the | ||
| 159 | persistence probabilities of vertebrate carcasses on the road. | 159 | persistence probabilities of vertebrate carcasses on the road. | ||
| 160 | Overall, the persistence was much lower for small animals, on roads | 160 | Overall, the persistence was much lower for small animals, on roads | ||
| 161 | with lower traffic volumes, for carcasses located on road lanes, and | 161 | with lower traffic volumes, for carcasses located on road lanes, and | ||
| 162 | during humid conditions and high temperatures during the wet season | 162 | during humid conditions and high temperatures during the wet season | ||
| 163 | and dry seasons, respectively.\n The guidance given here on monitoring | 163 | and dry seasons, respectively.\n The guidance given here on monitoring | ||
| 164 | frequencies is particularly relevant to provide conservation and | 164 | frequencies is particularly relevant to provide conservation and | ||
| 165 | transportation agencies with accurate numbers of road-kills, realistic | 165 | transportation agencies with accurate numbers of road-kills, realistic | ||
| 166 | mitigation measures, and detailed designs for road monitoring | 166 | mitigation measures, and detailed designs for road monitoring | ||
| 167 | programs." | 167 | programs." | ||
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