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En el instante 25 de junio de 2026, 12:27:10 UTC,
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Modificado el valor del campo
modified
a2026-06-25
en Are protected areas truly protected? The impact of road traffic on vertebrate fauna. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Are protected areas truly protected? The impact of road traffic on vertebrate fauna.
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| 5 | "author": "Garriga, N., Santos, X., Montori, A., Richter-Boix, A., | 5 | "author": "Garriga, N., Santos, X., Montori, A., Richter-Boix, A., | ||
| 6 | Franch, M. y Llorente, G.A.", | 6 | Franch, M. y Llorente, G.A.", | ||
| 7 | "author_name": "Garriga, N., Santos, X., Montori, A., Richter-Boix, | 7 | "author_name": "Garriga, N., Santos, X., Montori, A., Richter-Boix, | ||
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| 36 | "name": "Garriga, N., Santos, X., Montori, A., Richter-Boix, A., | 36 | "name": "Garriga, N., Santos, X., Montori, A., Richter-Boix, A., | ||
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| 51 | h\u00e1bitat se transforma en una serie de parches m\u00e1s | ||||
| 52 | peque\u00f1os de menor superficie total aislados entre s\u00ed por una | ||||
| 53 | matriz de h\u00e1bitats distinta de la original", | ||||
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| 73 | "miteco_data_territory": { | 87 | "miteco_data_territory": { | ||
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| 81 | "notes": "The extension of road networks is considered one of the | 95 | "notes": "The extension of road networks is considered one of the | ||
| 82 | major factors affecting\n fauna survival. Roadkill has been documented | 96 | major factors affecting\n fauna survival. Roadkill has been documented | ||
| 83 | widely and affects all taxonomic groups.\n Although roadkill is | 97 | widely and affects all taxonomic groups.\n Although roadkill is | ||
| 84 | associated mainly with traffic density, some life-history traits of\n | 98 | associated mainly with traffic density, some life-history traits of\n | ||
| 85 | species and the area surrounding roads are expected to modify number | 99 | species and the area surrounding roads are expected to modify number | ||
| 86 | of roadkills both\n taxonomically and geographically. Here we studied | 100 | of roadkills both\n taxonomically and geographically. Here we studied | ||
| 87 | the number of roadkills of vertebrates\n in an extensive region in the | 101 | the number of roadkills of vertebrates\n in an extensive region in the | ||
| 88 | northeastern Iberian Peninsula. We surveyed 820 km of 41\n roads in | 102 | northeastern Iberian Peninsula. We surveyed 820 km of 41\n roads in | ||
| 89 | two different seasons (spring and autumn), that differ in traffic | 103 | two different seasons (spring and autumn), that differ in traffic | ||
| 90 | intensity. In\n addition, we covered zones with distinct climatic | 104 | intensity. In\n addition, we covered zones with distinct climatic | ||
| 91 | characteristics and levels of protection of\n the surrounding | 105 | characteristics and levels of protection of\n the surrounding | ||
| 92 | habitats. Amphibians showed the highest number of roadkills whereas\n | 106 | habitats. Amphibians showed the highest number of roadkills whereas\n | ||
| 93 | reptiles, birds and mammals had similar rates. General Linear Model | 107 | reptiles, birds and mammals had similar rates. General Linear Model | ||
| 94 | tests showed no\n differences in roadkills by climatic region; | 108 | tests showed no\n differences in roadkills by climatic region; | ||
| 95 | however, differences in number of roadkills\n were linked to | 109 | however, differences in number of roadkills\n were linked to | ||
| 96 | protection status, with the highest number of casualties in highly | 110 | protection status, with the highest number of casualties in highly | ||
| 97 | protected\n areas. Redundancy Analysis demonstrated that the number of | 111 | protected\n areas. Redundancy Analysis demonstrated that the number of | ||
| 98 | amphibians and reptiles\n killed was associated with roads in highly | 112 | amphibians and reptiles\n killed was associated with roads in highly | ||
| 99 | protected areas whereas that of mammals and\n birds was linked to | 113 | protected areas whereas that of mammals and\n birds was linked to | ||
| 100 | unprotected areas. Protected areas often receive many visitors, which | 114 | unprotected areas. Protected areas often receive many visitors, which | ||
| 101 | in\n turn may increase wildlife casualties as a result of greater | 115 | in\n turn may increase wildlife casualties as a result of greater | ||
| 102 | traffic density. We recommend\n that correction measures be taken to | 116 | traffic density. We recommend\n that correction measures be taken to | ||
| 103 | reduce the high number of vertebrate fauna killed\n along roads that | 117 | reduce the high number of vertebrate fauna killed\n along roads that | ||
| 104 | cross protected areas.\n Palabras clave: Fauna casualty, Habitat | 118 | cross protected areas.\n Palabras clave: Fauna casualty, Habitat | ||
| 105 | fragmentation, Mortality, Vertebrate", | 119 | fragmentation, Mortality, Vertebrate", | ||
| 106 | "notes_translated": { | 120 | "notes_translated": { | ||
| 107 | "en": "The extension of road networks is considered one of the | 121 | "en": "The extension of road networks is considered one of the | ||
| 108 | major factors affecting\n fauna survival. Roadkill has been documented | 122 | major factors affecting\n fauna survival. Roadkill has been documented | ||
| 109 | widely and affects all taxonomic groups.\n Although roadkill is | 123 | widely and affects all taxonomic groups.\n Although roadkill is | ||
| 110 | associated mainly with traffic density, some life-history traits of\n | 124 | associated mainly with traffic density, some life-history traits of\n | ||
| 111 | species and the area surrounding roads are expected to modify number | 125 | species and the area surrounding roads are expected to modify number | ||
| 112 | of roadkills both\n taxonomically and geographically. Here we studied | 126 | of roadkills both\n taxonomically and geographically. Here we studied | ||
| 113 | the number of roadkills of vertebrates\n in an extensive region in the | 127 | the number of roadkills of vertebrates\n in an extensive region in the | ||
| 114 | northeastern Iberian Peninsula. We surveyed 820 km of 41\n roads in | 128 | northeastern Iberian Peninsula. We surveyed 820 km of 41\n roads in | ||
| 115 | two different seasons (spring and autumn), that differ in traffic | 129 | two different seasons (spring and autumn), that differ in traffic | ||
| 116 | intensity. In\n addition, we covered zones with distinct climatic | 130 | intensity. In\n addition, we covered zones with distinct climatic | ||
| 117 | characteristics and levels of protection of\n the surrounding | 131 | characteristics and levels of protection of\n the surrounding | ||
| 118 | habitats. Amphibians showed the highest number of roadkills whereas\n | 132 | habitats. Amphibians showed the highest number of roadkills whereas\n | ||
| 119 | reptiles, birds and mammals had similar rates. General Linear Model | 133 | reptiles, birds and mammals had similar rates. General Linear Model | ||
| 120 | tests showed no\n differences in roadkills by climatic region; | 134 | tests showed no\n differences in roadkills by climatic region; | ||
| 121 | however, differences in number of roadkills\n were linked to | 135 | however, differences in number of roadkills\n were linked to | ||
| 122 | protection status, with the highest number of casualties in highly | 136 | protection status, with the highest number of casualties in highly | ||
| 123 | protected\n areas. Redundancy Analysis demonstrated that the number of | 137 | protected\n areas. Redundancy Analysis demonstrated that the number of | ||
| 124 | amphibians and reptiles\n killed was associated with roads in highly | 138 | amphibians and reptiles\n killed was associated with roads in highly | ||
| 125 | protected areas whereas that of mammals and\n birds was linked to | 139 | protected areas whereas that of mammals and\n birds was linked to | ||
| 126 | unprotected areas. Protected areas often receive many visitors, which | 140 | unprotected areas. Protected areas often receive many visitors, which | ||
| 127 | in\n turn may increase wildlife casualties as a result of greater | 141 | in\n turn may increase wildlife casualties as a result of greater | ||
| 128 | traffic density. We recommend\n that correction measures be taken to | 142 | traffic density. We recommend\n that correction measures be taken to | ||
| 129 | reduce the high number of vertebrate fauna killed\n along roads that | 143 | reduce the high number of vertebrate fauna killed\n along roads that | ||
| 130 | cross protected areas.\n Palabras clave: Fauna casualty, Habitat | 144 | cross protected areas.\n Palabras clave: Fauna casualty, Habitat | ||
| 131 | fragmentation, Mortality, Vertebrate", | 145 | fragmentation, Mortality, Vertebrate", | ||
| 132 | "es": "The extension of road networks is considered one of the | 146 | "es": "The extension of road networks is considered one of the | ||
| 133 | major factors affecting\n fauna survival. Roadkill has been documented | 147 | major factors affecting\n fauna survival. Roadkill has been documented | ||
| 134 | widely and affects all taxonomic groups.\n Although roadkill is | 148 | widely and affects all taxonomic groups.\n Although roadkill is | ||
| 135 | associated mainly with traffic density, some life-history traits of\n | 149 | associated mainly with traffic density, some life-history traits of\n | ||
| 136 | species and the area surrounding roads are expected to modify number | 150 | species and the area surrounding roads are expected to modify number | ||
| 137 | of roadkills both\n taxonomically and geographically. Here we studied | 151 | of roadkills both\n taxonomically and geographically. Here we studied | ||
| 138 | the number of roadkills of vertebrates\n in an extensive region in the | 152 | the number of roadkills of vertebrates\n in an extensive region in the | ||
| 139 | northeastern Iberian Peninsula. We surveyed 820 km of 41\n roads in | 153 | northeastern Iberian Peninsula. We surveyed 820 km of 41\n roads in | ||
| 140 | two different seasons (spring and autumn), that differ in traffic | 154 | two different seasons (spring and autumn), that differ in traffic | ||
| 141 | intensity. In\n addition, we covered zones with distinct climatic | 155 | intensity. In\n addition, we covered zones with distinct climatic | ||
| 142 | characteristics and levels of protection of\n the surrounding | 156 | characteristics and levels of protection of\n the surrounding | ||
| 143 | habitats. Amphibians showed the highest number of roadkills whereas\n | 157 | habitats. Amphibians showed the highest number of roadkills whereas\n | ||
| 144 | reptiles, birds and mammals had similar rates. General Linear Model | 158 | reptiles, birds and mammals had similar rates. General Linear Model | ||
| 145 | tests showed no\n differences in roadkills by climatic region; | 159 | tests showed no\n differences in roadkills by climatic region; | ||
| 146 | however, differences in number of roadkills\n were linked to | 160 | however, differences in number of roadkills\n were linked to | ||
| 147 | protection status, with the highest number of casualties in highly | 161 | protection status, with the highest number of casualties in highly | ||
| 148 | protected\n areas. Redundancy Analysis demonstrated that the number of | 162 | protected\n areas. Redundancy Analysis demonstrated that the number of | ||
| 149 | amphibians and reptiles\n killed was associated with roads in highly | 163 | amphibians and reptiles\n killed was associated with roads in highly | ||
| 150 | protected areas whereas that of mammals and\n birds was linked to | 164 | protected areas whereas that of mammals and\n birds was linked to | ||
| 151 | unprotected areas. Protected areas often receive many visitors, which | 165 | unprotected areas. Protected areas often receive many visitors, which | ||
| 152 | in\n turn may increase wildlife casualties as a result of greater | 166 | in\n turn may increase wildlife casualties as a result of greater | ||
| 153 | traffic density. We recommend\n that correction measures be taken to | 167 | traffic density. We recommend\n that correction measures be taken to | ||
| 154 | reduce the high number of vertebrate fauna killed\n along roads that | 168 | reduce the high number of vertebrate fauna killed\n along roads that | ||
| 155 | cross protected areas.\n Palabras clave: Fauna casualty, Habitat | 169 | cross protected areas.\n Palabras clave: Fauna casualty, Habitat | ||
| 156 | fragmentation, Mortality, Vertebrate" | 170 | fragmentation, Mortality, Vertebrate" | ||
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| 329 | "title": "Are protected areas truly protected? The impact of road | 343 | "title": "Are protected areas truly protected? The impact of road | ||
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| 331 | "title_translated": { | 345 | "title_translated": { | ||
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