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En el instante 25 de junio de 2026, 12:33:39 UTC,
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Modificado el valor del campo
modified
a2026-06-25
en Herpetofauna and roads: a review. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Herpetofauna and roads: a review.
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| 78 | "notes": "Roads and traffic are tightly related to some of the mains | 92 | "notes": "Roads and traffic are tightly related to some of the mains | ||
| 79 | threats for biodiversity. Road network affects wildlife populations | 93 | threats for biodiversity. Road network affects wildlife populations | ||
| 80 | due to, among other effects, partial occupation and transformation of | 94 | due to, among other effects, partial occupation and transformation of | ||
| 81 | landscape, alteration of surrounding habitat, dispersal of | 95 | landscape, alteration of surrounding habitat, dispersal of | ||
| 82 | physicochemical pollutants, fragmentation and loss of connectivity, or | 96 | physicochemical pollutants, fragmentation and loss of connectivity, or | ||
| 83 | direct road-kills. Because of their ecological characteristics, | 97 | direct road-kills. Because of their ecological characteristics, | ||
| 84 | amphibians and reptiles are very exposed to road effects. In this | 98 | amphibians and reptiles are very exposed to road effects. In this | ||
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| 86 | road network. Amphibians exhibit high road-kill rates that can | 100 | road network. Amphibians exhibit high road-kill rates that can | ||
| 87 | condition viability of some populations, and are vulnerable to | 101 | condition viability of some populations, and are vulnerable to | ||
| 88 | pollution of road margins. Reptiles also suffer casualties because of | 102 | pollution of road margins. Reptiles also suffer casualties because of | ||
| 89 | road-kills when they move to paved roads for thermoregulation. Roads, | 103 | road-kills when they move to paved roads for thermoregulation. Roads, | ||
| 90 | especially those with high traffic load, act as barriers that | 104 | especially those with high traffic load, act as barriers that | ||
| 91 | difficult movements and contribute to population isolation in both | 105 | difficult movements and contribute to population isolation in both | ||
| 92 | groups. However, road impacts do not have equal intensity over space | 106 | groups. However, road impacts do not have equal intensity over space | ||
| 93 | and time, and consequently some spatio-temporal patterns can be | 107 | and time, and consequently some spatio-temporal patterns can be | ||
| 94 | defined. Not all species show the same degree of exposure to road | 108 | defined. Not all species show the same degree of exposure to road | ||
| 95 | impacts, which depend on specific ecological requirements in each | 109 | impacts, which depend on specific ecological requirements in each | ||
| 96 | case. Mobile species are generally more vulnerable than sedentary | 110 | case. Mobile species are generally more vulnerable than sedentary | ||
| 97 | ones. There are also intra-specific differences as a function of | 111 | ones. There are also intra-specific differences as a function of | ||
| 98 | gender and age. All these considerations must be taken into account | 112 | gender and age. All these considerations must be taken into account | ||
| 99 | when designing and implementing the corresponding mitigation measures | 113 | when designing and implementing the corresponding mitigation measures | ||
| 100 | necessary to reduce the negative effects of roads on herpetofauna | 114 | necessary to reduce the negative effects of roads on herpetofauna | ||
| 101 | populations.", | 115 | populations.", | ||
| 102 | "notes_translated": { | 116 | "notes_translated": { | ||
| 103 | "en": "Roads and traffic are tightly related to some of the mains | 117 | "en": "Roads and traffic are tightly related to some of the mains | ||
| 104 | threats for biodiversity. Road network affects wildlife populations | 118 | threats for biodiversity. Road network affects wildlife populations | ||
| 105 | due to, among other effects, partial occupation and transformation of | 119 | due to, among other effects, partial occupation and transformation of | ||
| 106 | landscape, alteration of surrounding habitat, dispersal of | 120 | landscape, alteration of surrounding habitat, dispersal of | ||
| 107 | physicochemical pollutants, fragmentation and loss of connectivity, or | 121 | physicochemical pollutants, fragmentation and loss of connectivity, or | ||
| 108 | direct road-kills. Because of their ecological characteristics, | 122 | direct road-kills. Because of their ecological characteristics, | ||
| 109 | amphibians and reptiles are very exposed to road effects. In this | 123 | amphibians and reptiles are very exposed to road effects. In this | ||
| 110 | article we review the relationship between these faunal groups and the | 124 | article we review the relationship between these faunal groups and the | ||
| 111 | road network. Amphibians exhibit high road-kill rates that can | 125 | road network. Amphibians exhibit high road-kill rates that can | ||
| 112 | condition viability of some populations, and are vulnerable to | 126 | condition viability of some populations, and are vulnerable to | ||
| 113 | pollution of road margins. Reptiles also suffer casualties because of | 127 | pollution of road margins. Reptiles also suffer casualties because of | ||
| 114 | road-kills when they move to paved roads for thermoregulation. Roads, | 128 | road-kills when they move to paved roads for thermoregulation. Roads, | ||
| 115 | especially those with high traffic load, act as barriers that | 129 | especially those with high traffic load, act as barriers that | ||
| 116 | difficult movements and contribute to population isolation in both | 130 | difficult movements and contribute to population isolation in both | ||
| 117 | groups. However, road impacts do not have equal intensity over space | 131 | groups. However, road impacts do not have equal intensity over space | ||
| 118 | and time, and consequently some spatio-temporal patterns can be | 132 | and time, and consequently some spatio-temporal patterns can be | ||
| 119 | defined. Not all species show the same degree of exposure to road | 133 | defined. Not all species show the same degree of exposure to road | ||
| 120 | impacts, which depend on specific ecological requirements in each | 134 | impacts, which depend on specific ecological requirements in each | ||
| 121 | case. Mobile species are generally more vulnerable than sedentary | 135 | case. Mobile species are generally more vulnerable than sedentary | ||
| 122 | ones. There are also intra-specific differences as a function of | 136 | ones. There are also intra-specific differences as a function of | ||
| 123 | gender and age. All these considerations must be taken into account | 137 | gender and age. All these considerations must be taken into account | ||
| 124 | when designing and implementing the corresponding mitigation measures | 138 | when designing and implementing the corresponding mitigation measures | ||
| 125 | necessary to reduce the negative effects of roads on herpetofauna | 139 | necessary to reduce the negative effects of roads on herpetofauna | ||
| 126 | populations.", | 140 | populations.", | ||
| 127 | "es": "Roads and traffic are tightly related to some of the mains | 141 | "es": "Roads and traffic are tightly related to some of the mains | ||
| 128 | threats for biodiversity. Road network affects wildlife populations | 142 | threats for biodiversity. Road network affects wildlife populations | ||
| 129 | due to, among other effects, partial occupation and transformation of | 143 | due to, among other effects, partial occupation and transformation of | ||
| 130 | landscape, alteration of surrounding habitat, dispersal of | 144 | landscape, alteration of surrounding habitat, dispersal of | ||
| 131 | physicochemical pollutants, fragmentation and loss of connectivity, or | 145 | physicochemical pollutants, fragmentation and loss of connectivity, or | ||
| 132 | direct road-kills. Because of their ecological characteristics, | 146 | direct road-kills. Because of their ecological characteristics, | ||
| 133 | amphibians and reptiles are very exposed to road effects. In this | 147 | amphibians and reptiles are very exposed to road effects. In this | ||
| 134 | article we review the relationship between these faunal groups and the | 148 | article we review the relationship between these faunal groups and the | ||
| 135 | road network. Amphibians exhibit high road-kill rates that can | 149 | road network. Amphibians exhibit high road-kill rates that can | ||
| 136 | condition viability of some populations, and are vulnerable to | 150 | condition viability of some populations, and are vulnerable to | ||
| 137 | pollution of road margins. Reptiles also suffer casualties because of | 151 | pollution of road margins. Reptiles also suffer casualties because of | ||
| 138 | road-kills when they move to paved roads for thermoregulation. Roads, | 152 | road-kills when they move to paved roads for thermoregulation. Roads, | ||
| 139 | especially those with high traffic load, act as barriers that | 153 | especially those with high traffic load, act as barriers that | ||
| 140 | difficult movements and contribute to population isolation in both | 154 | difficult movements and contribute to population isolation in both | ||
| 141 | groups. However, road impacts do not have equal intensity over space | 155 | groups. However, road impacts do not have equal intensity over space | ||
| 142 | and time, and consequently some spatio-temporal patterns can be | 156 | and time, and consequently some spatio-temporal patterns can be | ||
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| 144 | impacts, which depend on specific ecological requirements in each | 158 | impacts, which depend on specific ecological requirements in each | ||
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